Volume 4. Appendixes L, Section L.7, and M Resource ...

1 

I 

Resource Conservation and Recovery Act 

Facility Investigation/Remedid Investigation 

Report for'>Waste Area Groupings 1 and 7 

at Paduchh Gaseous Diffwion Plant 

Paducah, Kentucky 

Volume 4. Appendixes L, Section L.7, and M 

CLEARED FOR PUBLIC RELEASE

DOE/OR/07- 1404&D 1 

KY/EM-lOl&Dl 

Energy Systems Environmental Restoration Program 

PGDP Environmental Restoration Program 

Resource Conservation and Recovery Act 

Facility Investigation/Remedial Investigation 

Report for Waste Area Groupings 1 and 7 

at Paducah Gaseous Diffusion Plant 

Paduca h , Kentucky 

Volume 4. Appendixes L, Sections L.7, and M 

Date Issued-November 1995 

Prepared by 

Environmental Restoration Division 

Lockheed Martin Energy Systems, Inc. 

Paducah, Kentucky 

and 

Risk Analysis Section 

Health Sciences Research Division 

Oak Ridge National Laboratory 

Lockheed Martin Energy Systems, Inc. 

Oak Ridge, Tennessee 

and 

CDM Federal Programs Corporation 


Prepared for 

U.S. Department of Energy 

Office of Environmental Restoration and Waste Management 

PADUCAH GASEOUS DIFFUSION PLANT 

Paducah, Kentucky 42002 

by 

LOCKHEED MARTIN ENERGY SYSTEMS, INC. 

for the 

U.S. DEPARTMENT OF ENERGY 

under contract DE-AC05-760R00001

Appendix L.7 

Chronic Hazard Index Estimates and Cancer Risk Estimates for Adults 

and Children

THIS PAGE LEFT BLANK

Hazard Index Estimates 

IUlAL 

PATHWAY EXPOSURE 

REFERENCE RFD HAZARD HAZARD HAZARD 

ANALYSIS CDI DOSE SOURCE QUOTIENT INDEX INDEX 

WAG 1, SWMU lOOc, RGW-Residential Dermal Contact with Water 

Aluminum 

4s 

Barium 5.52E-05 4.90E-03 9 1.13E-02 

Manganese 5.09E-04 2.00E-04 38 2.54E+00 

Methylene Chloride 1.80E-06 5.70E-02 41 3.15E-05 

bis(2-Ethylhexy1)phthalate 3.75E-06 3.8OE-03 15 9.86E-04 

Gross Alpha 

Gross Beta 

Pathway Total 

2.56E+00 

WAG 1. SWMU 1OOc. RGW-Residential Ingestion of Water 

Alummum 

3.64E-01 

Barium 1.88E-02 7.00E-02 a 2.68E-01 

Manganese 1.73E-01 5.00E-03 a 3.46E+01 

Methylene Chloride 

1.37E-04 6.00E-02 a 2.28E-03 

bis(2-Ethylhexy1)phthalate 5.48E-05 2.00E-02 a 2.74E-03 

Gross Alpha 

Gross Beta 

Pathway Total 

3.49E+01 

WAG 1, SWMU lOOc, RGW-Residential Inhalation of Water 

Aluminum 

Barium 1.43E-04 b,c 

Manganese 1.43E-05 a 

Methylene Chloride 7.13E-06 8.57E-01 b 8.32E-06 

bis(2-Ethylhexy1)phthalate 

Gross Alpha 

Gross Beta 

Pathway Total 

8.32E-06 

WAG 1, SWMU lOOc, RSO-Residential Dermal Contact with Soil 

Aluminum 3.55E-02 4s 

Arsenic 2.12E-05 1.23E-04 8 1.73E-01 

Beryllium 1.90E-06 5.00E-05 13, 1 3.79E-02 

Cobalt 3.00E-05 26 

Lead 4.39E-05 26 

Sodium 

1.42E-03 

Thallium 2.42E-07 52 

2-Methylnaphthalene 2.23E-06 43 

3-Nitroaniline 

5.47E-07 

Endosulfan Sulfate 

7.45E-09 

Endrin Ketone 

7.69E-09 

Naphthalene 1.35E-06 43 

Phenanthrene 3.71E-06 2 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-238 

Pathway Total 

2.10E-01 

WAG 1. S WMU 1 OOc, RSO-Residential Ingestion of Soil for Adult 

Aluminum 

6.34E-03 

Arsenic 

3.79E-06 3.00E-04 a 1.26E-02 

Beryllium 3.39E-07 5.00E-03 a 6.77E-05 

Cobalt 

5.35E-06 

Lead 

7.84E-06 

Sodium 

2.53E-04 

Thallium 

4.32E-08 

2-Methylnaphthalene 

2.00E-07 




6.66E-10 

Endrin Ketone 6.87E- 10 

Naphthalene 1.21E-07 e 

Phenanthrene 

3.31E-07 

Gross Alpha 

Gross Beta 

Page 1 of 53

Hazard Index Estimates (continued) 



ANALYSIS 

Neptunium-237 

CDI DOSE SOURCE QUOTIENT INDEX INDEX 

Thorium-228 

Uranium-238 

Pathway Total 

1.27E-02 

WAG 1, SWMU lOOc, RSO-Residential Ingestion of Soil for Child 

Aluminum 

5.92E-02 

Arsenic 

3.54E-05 3.00E-04 a 1.18E-01 

Beryllium 

3.16E-06 5.00E-03 a 6.32E-04 

Cobalt 

Lead 

Sodium 

Thallium 




Endrin Ketone 

Naphthalene 

5.00E-05 

7.31E-05 

2.36E-03 


1.86E-06 


6.21E-09 

6.41E-09 

1.13E-06 

e 

Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-23 8 

3.09E-06 

Pathway Total 1.19E-0 1 

WAG 1, SWMU lOOc, RSO-Residential Ingestion of Vegetables 

Aluminum 

Arsenic 4.55E-06 3.OOE-04 a 1.52E-02 

Barium 1.05E-01 7.00E-02 a 1.49E+00 

Beryllium 1.27E-07 5.OOE-03 a 2.55E-05 

Cobalt 

Lead 

5.02E-06 

Manganese 1.04E+00 5.00E-03 a 2.07E4-02 

Sodium 

Thallium 

3.47E-09 




Endrin Ketone 


1.01E-03 6.00E-02 a 1.69E-02 

Naphthalene 

1.27E-05 

e 

Phenanthrene 


Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-238 

6.79E-06 

5.56E-04 2.00E-02 a 2.78E-02 

Pathway Total 

2.09E4-02 

WAG 1, SWMU lOOc, RSO-Residential Inhalation of Soil 

Aluminum 

2.96E-07 

Arsenic 

1.77E-10 

Beryllium 

1.58E-11 

Cobalt 

2.50E-10 

Lead 3.66E- 10 

Sodium 

1.18E-08 

Thallium 

2.01E-12 

2-Methylnaphthalene 9.31E-12 


2.28E-12 


3.11E-14 

Endrin Ketone 

3.21E-14 

Naphthalene 

5.63E-12 

Phenanthrene 

1.55E-11 

Gross Alpha 

Page 2 of 53





Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-238 

Pathway Total 

SWMU Total 

2.46E+02 

WAG 1, SWMU 136, RGW-Residential Dermal Contact with Water 


Manganese 4.50E-04 2.00E-04 38 2.25E+00 

Trichloroethene 1.39E-04 57 

bis(2-Ethylhexy1)phthalate 1.87E-06 3.80E-03 15 4.93E-04 

Gross Alpha 

Gross Beta 

Pathway Total 

2.26E+00 

WAG 1, SWMU 136. RGW-Residential Ingestion of Water 

Barium 9.04E-03 7.00E-02 a 1.29E-01 


Trichloroethene 3.01E-03 


Gross Alpha 

Gross Beta 

Pathway Total 3.08E+O 1 

WAG 1, SWMU 136, RGW-Residential Inhalation of Water 



Trichloroethene 

1.57E-04 


Gross Alpha 

Gross Beta 

Pathway Total 

WAG 1, SWMU 136, RSO-Residential Dermal Contact with Soil 

Aluminum 1.49E-03 435 

Arsenic 5.36E-07 1.23E-04 8 4.36E-03 

Beryllium 6.70E-08 5.OOE-05 13, 1 1.34E-03 

Cobalt 1.54E-06 26 

Lead l.lSE-06 26 

Sodium 


Sulfate 

1.31E-04 


1.1,l -Trichloroethane 1.25E-08 55 

1.1 -Dichloroethene 8.1 1E-09 9.00E-03 31 9.0 IE-07 

Benzo(a)anthracene 5.87E-08 2 

Benzo(a)pyrene 6.26E-08 2 

Benzo(b)fluoranthene 6.56E-08 2 

Benzo(g,h,i)perylene 5.53E-08 2 

Dibenzo(qh)anthracene 2.19E-08 2 

Indeno( 1,2,3-cd)pyrene 5.66E-08 2 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathwav Total 

5.70E-03 

WAG 1. SWMU 136, RSO-Residential Ingestion of Soil for Adult 

Aluminum 

2.66E-04 

Arsenic 9.58E-08 3.00E-04 a 3.19E-04 


Cobalt 

2.74E-07 

Lead 

2.05E-07 

Sodium 

7.48E-06 

Sulfate 

2.34E-05 

Thallium 1.61 E-09 

1.1,l -Trichloroethane 4.46E-10 e 

1,l-Dichloroethene 2.90E-10 9.00E-03 a 3.22E-08 

Page 3 of 53





Benz0la)anthracene ., 

5.24E-09 

Benzo(a)pyrene 

5.59E-09 

Benzo(b)fluoranthene 

5.86E-09 

Benzo(g,h,i)perylene 


Dibenzo(a,h)anthracene 1.95E-09 

Indeno( 1,2,3-cd)pyrene 5.05E-09 

Phenanthrene 

1.90E-09 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

3.22E-04 

WAG 1, SWMU 136, RSO-Residential Ingestion of Soil for Child 

Aluminum 

2.49E-03 

Arsenic 

8.94E-07 3.00E-04 a 2.98E-03 

Beryllium 

1.12E-07 5.00E-03 a 2.23E-05 

Cobalt 

Lead 

Sodium 

Sulfate 

Thallium 

1,1, I-Trichloroethane 

1, I-Dichloroethene 

2.56E-06 

1.91E-06 

6.98E-05 

2.19E-04 

1.50E-08 


2.70E-09 9.00E-03 

e 

a 3.00E-07 

Benzo(a)anthracene 




Dibenzo(a,h)anthracene 

Indeno( 1,2,3-cd)pyrene 

Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 


5.22E-08 

5.47E-08 


1.82508 


1.78E-08 

Pathway Total 

3.00E-03 

WAG 1, SWMU 136, RSO-Residential Ingestion of Vegetables 

Aluminum 

Arsenic 

Barium 

Beryllium 

Cobalt 

Lead 

Manganese 

Sodium 

Sulfate 

Thallium 

l,l,l-Trichloroethane 

1,l -Dichloroethene 

Benzo(a)anbene 






Phenanthrene 



Gross Alpha 

Gross Beta 

Uranium-238 

Pathwav Total 

1.15E-07 

5.03E-02 


1.3 1E-07 

9.16E-0 1 

1.30E- 10 

1.24507 

1.94E-07 

2.36E-08 

1.36E-08 

1.42E-08 

8.66E-09 

6.85E-09 

3.90E-08 

2.78E-04 

3.00E-04 a 3.83E-04 

7.00E-02 a 7.18E-0 1 

5.OOE-03 a 9.00E-07 

5.00E-03 a 1.83E+02 

9.00E-03 

2.OOE-02 

WAG 1, SWMU 136, RSO-Residential Inhalation of Soil 

Aluminum 

1.24E-08 

Arsenic 


Beyllium 

5.58E-13 

Page 4 of 53 

e 

a 

a 

2.15E-05 

1.39E-02 

1.84EM2





Cobalt 

1.28E-11 

Lead 

Sodium 

Sulfate 

Thallium 


9.55E-12 

3.49E- 10 

1.09E-09 

7.53E-14 

5.32E-09 

e 








Phenanthrene 

9.18E-09 

2.45E-13 

2.61E-13 

2.73E-13 

2.31E-13 

9.12E- 14 

2.36E-13 

8.89E- 14 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

SWMU Total 

2.17E+02 

WAG 1, SWMU 38c, RGW-Residential Dermal Contact with Water 

Barium 2.34E-05 4.90E-03 9 4.78E-03 

Manganese 2.27E-04 2.00E-04 38 1.13E+00 

Methylene Chloride 4.67E-05 5.70E-02 41 8.19E-04 

Gross Beta 

Pathway Total 

1.14E+00 

WAG 1, SWMU 38c, RGW-Residential Ingestion of Water 

Barium 7.97E-03 7.00E-02 a 1.14E-01 

Manganese 7.73E-02 5.OOE-03 a 1.55E+01 

Methylene Chloride 3.56E-03 6.00E-02 a 5.94E-02 

Gross Beta 



Gross Beta 

Pathway Total 

2.16E-04 

WAG 1, SWMU 38c, RSO-Residential Dermal Contact with Soil 


Arsenic 

4.49E-05 1.23E-04 8 3.65E-01 

Beryllium 

4.18E-06 5.00E-05 13, 1 8.36E-02 

Cobalt 

Lead 

Sodium 

'Ihallium 

2-Hexanone 

Aroclor- 1260 


Benzo( a)pyrene 


Phenanthrene 

7.22E-05 

1.06E-04 

1.52E-03 

9.10507 

3.84E-07 

6.11E-07 

2.30E-06 

1.99E-06 

2.92E-06 

3.88E-06 

26 

26 

52 

36 

46 

2 

2 

2 

2 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thonum-228 

Uranium-235 

Uranium-238 

Pathwav Total 4 .. 49E-0 ..- . 1 . 

WAG 1, SWMU 38c, RSO-Residential Ingestion of Soil for Adult 

Aluminum 

1.25E-02 

Arsenic 8.02E-06 3.00E-04 a 2.67E-02 

Bervllium 7.46E-07 5.00E-03 a 1.49E-04 

Cobalt 

1.29E-05 

Page 5 of 53




I 


Lead 

1.89E-05 

Sodium 

Thallium 

2-Hexanone 

Aroclor-1260 




Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

2.72E-04 

1.62E-07 

1.37E-08 

5.46E-08 

2.05E-07 

1.78E-07 

2.60E-07 

3.46E-07 

Arsenic 

Beryllium 

Cobah 

Lead 

Sodium 

Thallium 

2-Hexanone 

Aroclor-1260 




Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

7.49E-05 3.00E-04 a 2.50E-01 

6.96E-06 5.00E-03 a 1.39E-03 

1.20E-04 

1.76E-04 

2.54E-03 

1.52E-06 

1.28E-07 

5.09E-07 

1.92E-06 

1.66E-06 

2.43E-06 

3.23E-06 

Pathway Total 2.5 1 E-0 1 

WAG 1, SWMU 38c, RSO-Residential Ingestion of Vegetables 

Aluminum 

Arsenic 

Barium 

Beryllium 

Cobalt 

Lead 

Manganese 

Sodium 

Thallium 

2-Hexanone 

Aroclor-1260 




Methvlene Chloride 

Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

Pathwav Total 

9.63E-06 

4.43502 

2.81E-07 

1.2 1E-05 

4.62E-0 1 

1.31E-08 

3.12E-08 

9.23E-07 


6.33E-07 

2.63E-02 

7.10E-06 

WAG 1, SWMU 38c, RSO-Residentlal Inhahon of Soil 

Aluminum 5 82E-07 

3.00E-04 a 3.21E-02 

7.00E-02 a 6.33E-01 

5.00E-03 a 5.62E-05 

5.00E-03 a 9.24E+01 

6.00E-02 a 4.39E-01 

9.35E+01 

Page 6 of 53 

!

~ 


' 




Arsenic 

3.74E-10 

Beryllium 

3.48E-11 

Cobalt 6.OZE- 10 

Lead 8.82E- 10 

Sodium 

1.27E-08 

Thallium 

7.58E-12 

2-Hexanone 

6.39E-13 

Aroclor- I260 

2.55E-12 


9.59E-12 


8.31E-12 

Benzo(b)fluoranthene 1.21E-11 

Phenanthrene 1.62E- 11 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

Pathway Total 

S WMU Total 1.11E+02 


Lead 5.76E-07 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

1.03E-07 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

9.59E-07 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

6.58E-08 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

SWMU Total 

WAG 7. SWMU 131, RSO-Residential Dermal Contact with Soil 

Lead 1.1 OE-07 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathwav . ~-. Total 

WAG 7, SWMU 131, RSO-Residential Ingeshon of Soil for Adult 

Lead 

1.96E-08 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

- 

Page 7 of 53


~~ 





Lead 

1.83E-07 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

1.26E-08 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 7. SWMU 131. RSO-Residential Inhalation of Soil 

Lead 9.16513 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

SWMU Total 


Lead 9.00E-06 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 7, SWMU 132, RSO-Residential Ingestion of Soil for Adult 

Lead 1.61E-06 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

1.50E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

1.03E-06 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

7.50E-11 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

SWMU Total 


Lead 1.04E-05 26 

Acenaphthylene 



Benzo@)fluoranthene 


Benzo(k)fluoranthene 



Phenanthrene 

Gross Alpha 

7.5SE-08 

5.66E-07 



2.53E-07 

3.82E-07 

3.12E-08 

2.09E-07 

5.12E-07 

Page 8 of 53


IUlAL 

EXPOSURE 

PATHWAY 



Uranrum-238 

Pathway Total 


Lead 









Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

1.86E-06 

6.74E-09 

5.05E-08 

3.80E-08 


2.26E-08 

3.41E-08 

2.79E-09 

1.87E-08 


Pathway Total 


Lead 1.746-05 









Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

6.29E-08 


3.55E-07 

3.82E-07 

2.11E-07 

3.19E-07 

2.60E-08 

1.75E-07 



Lead 

1.19E-06 



2.27E-07 


9.24E-08 


9.94E-08 



8.30E-08 



Phenanthrene 

9.37E-07 

Gross Alpha 

Gross Beta 

Uranium-23 8 

Pathwav Total 


Lead 







Dibenzo(ah)anthracene 


Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

S WMU Total 

8.70E-11 

3.15E-13 

2.36E-12 

1.77E- 12 

1.91E-12 

1.05E-12 

1.59E- 12 

1.30E-13 

8.73E-13 

2.13E-12 

Page 9 of 53


IUlAL 





Lead 1.68E-06 26 

Benzo( a)anthracene 

1.93E-08 


1.80E-08 


2.69E-08 


9.54E-09 

Phenanthrene 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

2.99E-07 


1.73E-09 

Benzo(a)pyrene 1.61E-09 


2.40E-09 


8.52E-10 

Phenanthrene 

3.87E-09 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

2.79E-06 


1.61E-08 


1.50E-08 


2.24E-08 


7.95E-09 

Phenanthrene 3.61E-08 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

1.92E-07 


7.75E-09 


3.92E-09 


5.84E-09 


Phenanthrene 

7.93E-08 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 1.40E- 11 


8.06E-14 


7.52E-14 

Benzo@)fluoranthene 1.12E- 13 

Benzo(g,h,i)perylene 3.97E- 14 

Phenanthrene 1.81 E- 13 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

S WMU Total 

WAG 7, SWMU 8b, RGW-Residential Dermal Contact with Water 

Aluminum 43 

Beryllium 4.25E-06 5.00E-05 13, 1 8.51E-02 

Cobalt 26 

Iron 26 

Manganese 2.01E-03 2.00E-04 38 1 .O 1E+O 1 

Nickel 5.26E-05 5.40E-03 44 9.75E-03 

Page 10 of 53





Silica 

Silicon 

Sulfate 

Sulfide 

1,l -Dichloroethene 7.12E-06 9.00E-03 31 7.9 IE-04 

1,2-Dichloroethene 1.31E-05 9.00E-03 1.46E-03 



Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-234 

Uranium-235 

Uranium-238 

Pathwav Total 

1.02E+01 

WAG 7, SWMU 8b, RGW-Residential Ingestion of Water 

Aluminum 

1.32E+00 

Beryllium 

1.45E-03 5.00E-03 a 2.90E-01 

Cobalt 

Iron 

Manganese 

2.34E-02 

3.37E+01 

6.85E-01 5.OOE-03 a 1.37E+02 

Nickel 

1.79E-02 2.00E-02 a 8.96E-01 

Silica 

Silicon 

Sulfate 

Sulfide 


1.38E+01 

3.29E-01 

2.18E+01 

6.58E-02 

2.66E-04 9.00E-03 a 2.95E-02 

1,2-Dichloroethene 

4.18E-03 9.00E-03 b 4.65E-01 

Phenanthrene 


Gross Alpha 

Gross Beta 

Neptunium-237 

Thonum-228 

Uranium-234 

Uranium-235 

Uranium-238 

2.74E-05 

1.46E-04 

Pathway Total 

1.39E+02 

WAG 7, SWMU 8b, RGW-Residential Inhalation of Water 

Aluminum 

Beryllium 

Cobalt 

Iron 

Manganese 

1.43E-05 a 

Nickel 

Silica 

Silicon 

Sulfate 

Sulfide 


1.38E-05 

1.2-Dichloroethene 

Phenanthrene 


7.60E-06 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-234 

Uranium-235 

Uranium-238 

Pathwav Total 

WAG 7. SWMU 8b. RSO-Residential Dermal Contact with Soil 

Page 11 of 53


IUlAL 




Aluminum 8.33E-02 4.5 

Arsenic 

3.11E-05 1.23E-04 8 2.52E-0 1 

Beryllium 

5.34E-06 5.00E-05 13, 1 1.07E-01 

Cobalt 

Lead 

Phosphate (ortho) 

Sodium 

Thallium 


Aroclor-1260 




Dibenzofuran 


Naphthalene 

Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Thorium-230 

Uranium-235 

Uranium-238 

5.93E-05 

7.64E-05 


8.33E-04 

1.19E-06 

1.84E-06 


2.65E-06 

3.85E-06 


3.78E-06 

3.53E-06 

3.86E-06 

3.52E-06 

26 

26 

52 

43 

46 

2 

2 

2 

2 

43 

2 

Arsenic 5.54E-06 3.00E-04 a 1.85E-02 


Cobalt 

1.06E-05 

Lead 

1.36E-05 


7.81E-05 

Sodium 

1.49E-04 

Thallium 

2.12E-07 


1.64E-07 

Aroclor-1260 

3.92E-08 


2.37E-07 


3.44E-07 


3.89E-07 

Dibenzofuran 

3.37E-07 


Naphthalene 

3.45E-07 

e 

Phenanthrene 

3.14E-07 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Thorium-230 

Uranium-235 

Uranium-238 

Pathway Total 

WAG 7. SWMU 8b, RSO-Residential Ingestion of Soil for Child 

Aluminum 1.39E-01 

Arsenic 5.18E-OS 3.00E-04 a 1.73E-01 


Cobalt 

9.88E-05 

Lead 

1.27E-04 


7.29E-04 

Sodium 

1.39E-03 

Thallium 

1.98E-06 


1.53E-06 

Aroclor-1260 

3.66E-07 

Benzo(a)anthmcene 

2.21E-06 

1.87E-02 

Page 12 of 53






3.21E-06 


3.63E-06 

Dibenzofuran 

3.15E-06 


Naphthalene 

3.22E-06 

e 

Phenanthrene 

2.93E-06 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Thorium-230 

Uranium-23 5 

Uranium-238 

Pathwav Total 1.74E-01 

WAG 7, SWMU 8b, RSO-Residential Ingestion of Vegetables 

Aluminum 

Arsenic 

Beryllium 

Cobalt 

Iron 

Lead 

8.74E-06 

Manganese 4.09E+00 5.00E-03 

Nickel 1.00E-01 2.00E-02 


Silica 

Silicon 

Sodium 

Sulfate 

Sulfide 

Thallium 

1,1 -Dichloroethene 

1.70E-08 

1.71E-03 9.00E-03 


4.64E-02 9.00E-03 


Aroclor- 1260 



Benzo(h)fluoranthene 

Dibenzofuran 


Naphthalene 

Phenanthrene 


Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium228 

Thorium-230 

Uranium-234 

Uranium-235 

Uranium-238 

Pathwav Total 

2.24E-08 

1.06E-06 

8.37E-07 

9.47E-07 


3.63E-05 

1.59E-04 

R’AG 7. SWMU 8b, RSO-Residential Inhalation of Soil 

Aluminum 

6.95E-07 

Arsenic 

2.59E-10 

Beryllium 


Cobalt 


Lead 

6.37E-I0 


3.64E-09 

Sodium 6.95509 

Thallium 

9.88E-12 

2-Methvlnaphthalene 

7.67E-12 

Aroclor-1260 1.83E- 12 


1.lOE-I1 

6.66E-06 3.00E-04 a 2.22E-02 

8.04E-03 5.00E-03 a 1.61E+00 

Page 13 of 53 

a 

a 

a 

b 

e 

8.19E+02 

5.02E+00 

1.90E-01 

5.15E+00 

8.31E+02






1.6lE-11 

Benzo(b)fluoranthene 1.82E- 11 

Dibenzofuran 1.57E- 11 


Naphthalene 1.61E- 11 

Phenanthrene 

1.47E-11 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Thorium-230 

Uranium-235 

Uranium-238 

Pathway Total 

S WMU Total 

9.80E+02 

WAG 1, SWMU 100% CSE-Recreational Dermal Contact with Sediment 


Arsenic 

3.38E-06 1.23E-04 8 2.75E-02 

Beryllium 


Cobalt 

9.73E-06 26 

Lead 

6.82E-06 26 

Sodium 

8.01E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

3.73E-02 

WAG 1, SWMU 100% CSE-Recreational Ingestion of Deer 

Aluminum 

Cadmium 5.00E-04 a 

Cobalt 

Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-238 

Pathway Total 

WAG 1, SWMU 100% CSE-Recreational Ingestion of Sediment for Adult 

Aluminum 

7.52E-04 

Arsenic 3.49E-07 3.00E-04 a 1.16E-03 

Beryllium 5.08E-08 5.00E-03 a 1.OZE-05 

Cobalt 

1.00E-06 

Lead 

7.03E-07 

Sodium 

8.26E-06 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

1.17E-03 

WAG 1, SWMU 100% CSE-Recreational Ingestion of Sediment for Child 

Aluminum 

7.02E-03 

Arsenic 3.25E-06 3.00E-04 a 1.08E-02 

Beryllium 4.74E-07 5.OOE-03 a 9.47E-05 

Cobalt 

9.36E-06 

Lead 

6.56E-06 

Sodium 

7.71E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

1.09E-02 

WAG 1, SWMU 100% CSE-Recreational Inhalation of Sediment 

Aluminurn 

3.51E-08 

Arsenic 

1.63E-11 

Beryllium 

2.37E-12 

Page 14 of 53


I'U 1AL 




Cobalt 


Lead 

Sodium 

3.28E-11 

3.85E-10 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 1, SWMU 100% CSW-Recreational Dermal Contact with Water 

Aluminum 4,5 

Cadmium 

Cobalt 

Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-238 

8.82E-07 5.00E-06 16, 1 1.76E-01 

26 

1.03E-06 26 


WAG 1, SWMU 100% RGW-Recreational Ingestion of Fish 

Aluminum 

Cadmium 

5.00E-04 a 

Cobalt 

Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-238 

Pathway Total 

S WMU Total 

WAG 1, SWMU 100b, CSE-Recreational Dermal Contact with Sediment 


Arsenic 

3.08E-06 1.23E-04 8 2.5lE-02 

Beryllium 

3.80E-07 5.OOE-05 13, 1 7.59E-03 

Cobalt 


Lead 

5.99E-06 26 

Sodium 

7.47E-05 

Gross Alpha 

Gross Beta 

Uranium-235 

Uranium-238 

Pathway Total 

WAG 1, SWMU 100b, CSE-Recreational Ingestion of Deer 

Aluminum 

Arsenic 3.00E-04 a 

Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-235 

Uranium-238 

Pathwav Total 

N'AG 1. SWMU 100b, CSE-Recreational Ingestion of Sediment for Adult 

Aluminum 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-235 

5.86E-04 

3.18E-07 3.00E-04 a 1.06E-03 

3.91E-08 5.00E-03 a 7.83E-06 

5.08E-07 

6.18E-07 

7.71E-06 

Page 15 of 53 

3.27E-02 

2.25E-01


IUIAL 



ANALYSIS CDI DOSE SOURCE QUOTIEhT INDEX INDEX 

Uranium-238 

Pathway Total 

WAG 1, SWMU 100b. CSE-Recreauonal Ingestion of Sediment for Child 

1.07E-03 

Aluminum 

5.47E-03 

Arsenic 2.97E-06 3.00E-04 a 9.89E-03 

Beryllium 3.65E-07 5.OOE-03 a 7.3 1E-05 

Cobalt 


Lead 

5.76E-06 

Sodium 

7.19E-05 

Gross Alpha 

Gross Beta 

Uranium-23 5 

Uranium-238 

Pathway Total 

9.97E-03 

WAG 1, SWMU 100b, CSE-Recreational Inhalation of Sediment 

Aluminum 

2.73E-08 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodiuh 

1.48E-11 

1.83E- 12 

2.37E-11 

2.88E-11 

3.60E- 10 

Gross Alpha 

Gross Beta 

Uranium-235 

Uranium-238 

Pathway Total 

WAG 1, SWMU 100b, CSW-Recreational Dermal Contact with Water 

Alummum 

4s 

Arsenic 

9.29E-08 1.23E-04 8 7.55E-04 

Lead 

1.80E-06 26 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-235 

Uranium-238 

Pathway Total 

7.55E-04 

WAG 1, SWMU 100b, RGW-Recreational Ingestion of Fish 

Aluminum 


Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-235 

Uranium-238 

Pathway Total 

S WMU Total 


WAG 1. SWMU IOOc, CSE-Recreational Ingestion of Deer 

Alummum 

Arsenic 5.45E-11 3.00E-04 a 1.82E-07 


Cobalt 

Lead 

2.01E-11 

Sodium 

Thallium 9.706-12 




Endrin ketone 

Naphthalene 7.91 E- 13 e 

Phenanthrene 

8.23E-12 

Page 16 of 53





Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-238 

Pathway Total 

l.82E-07 

SWMU Total 

1.82E-07 

WAG 1, SWMU 136, CSE-Recreahonal Ingestion of Deer 

Aluminum 

Arsenic 

1.38E- 12 3.00E-04 a 4.59E-09 

Beryllium 

5.77E- 14 5.00E-03 a 1.15E-I1 

Cobalt 

Lead 

Sodium 

Sulfate 

Thallium 

I,l,l-Trichloroethane 


5.25E-13 

3.62E- 13 

1.41E- 15 


e 

a 5.30E-14 


Benzo(a)p yrene 



Dibenzo(4h)anthracene 


Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

6.20E-13 

1.44E-12 

1.5 1 E- 12 

2.35E-13 

2.97E- 12 


Pathway Total 


SWMUTO~~~ 




Beryllium 

Cobalt 

Lead 

Sodium 

Vanadium 

Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

9.49E-07 5.00E-05 13, 1 1.90E-02 

5.99E-06 26 

5.46E-06 26 

2.46E-05 

5.77E-05 7.00E-05 58, 5 8.24E-01 

1.19E-07 2 

Lead 

Sodium 

Chloroform 

1.00E-02 a 


2.00E-02 a 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathwav Total 

WAG 1. SWMU 38% CSE-Recreational Ingestion of Sediment for Adult 

Aluminum 

2.8 IE-04 


Cobalt 

6.18E-07 

Lead 

5.63E-07 

Sodium 2.54E-06 

Vanadium 5.94E-06 7.00E-03 b 8.49E-04 

Phenanthrene 

6.12E-09 

Gross Alpha 

Gross Beta 

Page 17 of 53


IUlAL 


REFERENCE RFD HAZARD HAZARD 

~~ 

HAZARD 

ANALYSIS 


Pathway Total 

8.69E-04 


Aluminum 

2.63E-03 

Beryllium 

9.13E-07 5.00E-03 a 1.83E-04 

Cobalt 

Lead 

Sodium 

Vanadium 

5.76E-06 

5.25E-06 

2.37E-05 

5.55E-05 7.00E-03 b 7.93E-03 

Phenanthrene 

5.71E-08 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 8.11E-03 

WAG 1. SWMU 38% CSE-Recreational Inhalation of Sediment 

Aluminum 

1.31E-08 

Beryllium 

Cobalt 

Lead 

Sodium 

Vanadium 

Phenanthrene 

4.57E- 12 

2.88E-11 

2.63E-11 

1.18E-10 

2.77E- 10 

2.85E-13 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Arsenic 7.30E-08 1.23E-04 8 5.93E-04 

Lead 3.78E-07 26 

Sodium 

Chloroform 2.37E-06 2.00E-03 24 1.18E-03 

bis(2-Ethylhexy1)phthalate 3.09E-06 3.80E-03 15 8.13E-04 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 1, SWMU 38q RGW-Recreational Ingestion of Fish 

2.59E-03 


Lead 

Sodium 

Chloroform 

1.00E-02 a 


2.00E-02 a 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

S WMU- Total 

8.53E-01 

WAG 1. SWMU 38b, CSE-Recreational Dermal Contact with Sediment 


Arsenic 

2.14E-06 1.23E-04 8 1.74E-02 

Beryllium 

2.79E-07 5.00E-05 13, 1 5.58E-03 

Cobalt 

3.97E-06 26 

Lead 

1.08E-05 26 

Sodium 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathwav Total 

2.29E-02 


Aluminum 

Sodium 

Gross Alpha 

Gross Beta 

Neptunium-237 

Page 18 of 53


IWlAL 




Plutonium-238 

Uranium-234 

Uranium-238 

Pathway Total 

WAG 1. SWMU 38b, CSE-Recreational Ingestion of Sediment for Adult 

Aluminum 5.43 E-04 

Arsenic 2.20E-07 3.00E-04 a 7.34E-04 


Cobalt 


Lead 

l.llE-06 

Sodium 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

7.40E-04 

WAG 1, SWMU 38b, CSE-Recreational Ingestion of Sediment for Child 

Aluminum 

5.07E-03 

Arsenic 2.05E-06 3.00E-04 a 6.85E-03 


Cobalt 

3.82E-06 

Lead 

1.04E-05 

Sodium 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

6.90E-03 

WAG 1, SWMU 38b, CSE-Recreational Inhalation of Sediment 

Aluminum 

2.54E-08 

Arsenic 

1.03E-11 

Beryllium 1.34E- 12 

Cobalt 

1.9lE-11 

Lead 

5.20E-11 

Sodium 

2.01E-10 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Aluminum 495 

Sodium 

Gross Alpha 

Gross Beta 

Neptunium-237 

Plutonium-238 

Uranium-234 

Uranium-238 

Pathway Total 

WAG 1. SWMU 38b, RGW-Recreational Ingestion of Fish 

Aluminum 

Sodium 

Gross Alpha 

Gross Beta 

Neptunium-237 

Plutonium-238 

Uranium-234 

Uranium-238 

Pathway Total 

SWMU Total 

2.98E-02 

WAG 1, SWMU 38c, CSE-Recreational Ingestion of Deer 

Aluminum 

Arsenic 2.12E-IO 3.00E-04 a 7.08E-07 


Page 19 of 53



REFERENCE RFD HAZZARD HAZARD HAZARD 


Lead 

8.91E-11 

Sodium 

Thallium 

6.72E-11 

2-Hexanone 

Aroclor- 1260 2.24E- 10 

Benzo(a)anthracene 4.47E- 11 


8.46E-11 


1.24E-10 

Phenanthrene 

1.59E-11 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

Pathway Total 

7.10E-07 

S WMU Total 

7.10E-07 

WAG 7, SWMU 130, CSE-Recreational Ingestion of Deer 

Lead 

2.63E-13 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

S WMU Total 

WAG 7. SWMU 131, CSE-Recreational Ingestion of Deer 

Lead 5.03E- 14 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

SWMU Total 


Lead 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

S WMU Total 

R’AG 7, SWMU 133, CSE-Recreational Ingestion of Deer 

Lead 




5.98E-12 


9.80E-12 


1.06E-11 

Benzo( g.h,i)perylene 


8.81E-12 

Dihenzo(a,h)anthracene 

3.35E-13 

Indeno( 1,2.3-cd)pyrene 1.10E-11 

Phenanthrene 

1.14E-12 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

SWMU Total 


Lead 

7.67E-13 

Benzo(a)anthracene 2.04E- 13 




6.20E-13 


Phenanthrene 

9.62E-14 

Gross Alpha 

Gross Beta 

Page 20 of 53


IUlAL 




Uranium-238 

Pathway Total 

S WMU Total 

WAG 7, SWMU 8% CSE-Recreational Dermal Contact with Sedunent 

Alummum 2.38E-03 4,5 

Arsenic 

5.05E-06 1.23E-04 8 4.10E-02 

Beryllium 

5.33E-07 5.OOE-05 13, 1 1.07E-02 

Cobalt 

9.03E-06 26 

Lead 

6.77E-06 26 

Sodium 

7.88E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

5.17E-02 

WAG 7, SWMU 8a, CSE-Recreational Ingestion of Deer 

Aluminum 

Antimony 

Arsenic 

Barium 

Beryllium 

Cadmium 

Cobalt 

Iron 

Lead 

Manganese 

Nickel 

Phosphate (oriho) 

Ruthenium 

Silicon 

Sodium 

Sulfate 

Tantalum 

Thallium 

Tungsten 

Vanadium 

Zirconium 


1,2-Dichioroethene 


Aroclor-1260 

Benzo(a)anihracene 



Dibenzofuran 



Naphthalene 

Phenanthrene 


his(2-Ethylhexy1)phthalate 

cis- 1,2-Dichloroethene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Thorium-230 

Uranium-234 

Uranium-235 

Uranium-238 

Pathway Total 

3.46E-09 

3.51E-09 

3.07E-07 

7.95E-08 

1.84E-09 


6.80E-05 

8.22E-06 

5.31E-05 


1.45E-11 

6.60E-12 

3.85E-09 

1.23E-09 

3.91E-09 


8.16E-09 

9.96E-11 

3.44E-10 

3.26E-13 

8.38E-12 


3.00E-04 

7.00E-02 

5.OOE-03 

5.OOE-04 

5.00E-03 

2.00E-02 

7.00E-03 

9.00E-03 

9.00E-03 

6.00E-02 

2.00E-02 

1.00E-02 

a 

a 

a 

a 

a 

a 

a 

b 

a 

b 

a 

e 

8.64E-06 

1.17E-05 


1.59E-05 

3.67E-06 

1.36E-02 


6.36E-04 

1.61E-09 

7.34E-10 

a 1.63E-11 

b 8.38E- 10 

WAG 7, SWMU 8a, CSE-RecreAonal Ingesbon of Sedunent for Adult 

Alummum 

2.46E-04 

Arsenic 5.20E-07 3.00E-04 a 173E-03 

Page21 of53 

1.47E-02






Cobalt 

Lead 

Sodium 

9.31E-07 

6.98E-07 

8.12E-06 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

1.75E-03 

WAG 7, SWMU 8a, CSE-Recreational Ingestion of Sediment for Child 

Aluminum 

2.29E-03 

Arsenic 4.86E-06 3.00E-04 a 1.62E-02 

Beryllium 5.12E-07 5.00E-03 a 1 .O2E-04 

Cobalt 

8.69E-06 

Lead 

6.51E-06 

Sodium 

7.58E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

1.63E-02 

WAG 7. SWMU 8a, CSE-Recreational Inhalation of Sediment 

Aluminum 

1.15E-08 

Arsenic 

2.43E-11 

Beryllium 

2.56E-12 

Cobalt 


Lead 3.26511 

Sodium 3.79E- 10 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Aluminum 4.5 

Antimony 

Arsenic 

Barium 

Beryllium 

Cadmium 

Cobalt 

Iron 

Lead 

Manganese 

Nickel 

Ruthenium 

Silicon 

Sodium 

Sulfate 

Tantalum 

lkallium 

Tungsten 

Vanadium 

Zirconium 





bis(2-Ethy1hexyl)phthalate 

cis- 1.2-Dichloroethene 

Gross Alpha 

Gross Beta 

Xeptunium-237 

Thorium-228 

Uranium-234 

Uranium-238 

1.24E-06 

7.46E-08 

2.80506 

2.08E-07 

1.59E-07 

2.3 1E-05 

1.16E-03 

3.31E-06 

3.58E-05 

1.59E-07 

1.95E-07 

8.44E-07 

1.09E-07 

1.54E-07 

1.43E-06 

8.00E-06 7 

1.23E-04 8 


5.00E-05 13, 1 

5.00E-06 16, 1 

26 

26 

26 

2.00E-04 38 

5.40E-03 44 

52 

7.00E-05 58, 5 

12 

9.00E-03 31 

9.00E-03 

5.70E-02 41 

57 

3.80E-03 15 

1 .OOE-02 83 

Page 22 of 53 

1.55E-01 

6.07E-04 

5.71E-04 

4.1 5E-03 

3.19E-02 

5.82E+00 

6.14E-04 

5.12E-0 1 

1.77E-05 

2.17E-05 

1.48E-05 


1.43E-04


- 




Pathway Total 

6.52E-tOO 


Aluminum 

Antimony 

Arsenic 

Barium 

Beryllium 

Cadmium 

Cobalt 

Iron 

Lead 

Manganese 

Nickel 

Ruthenium 

Silicon 

Sodium 

Sulfate 

Tantalum 

Thallium 

Tungsten 

Vanadium 

Zirconium 


1,2-DichIoroethene 


1.71E-04 

1.20E-05 


1.04E-04 

5.66E-01 

1.27E-03 

5.1 IE-04 

1.75E-06 


3.00E-04 

7.00E-02 

5.00E-03 

5.00E-04 

5.00E-03 

2.00E-02 

7.00E-03 

9.00E-03 

9.00E-03 

6.00E-02 

a 

a 

a 

a 

a 

a 

a 

b 

a 

b 

a 



9.64E-02 

1.13E+02 

7.30E-02 

2.91E-05 




Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-234 

Uranium-238 

2.00E-02 

1.00E-02 

a 

b 

Pathway Total 

1.14E+02 

SWMU Total 

1.20E+02 

WAG 1, SWMU 100% ESE-Excavation Dermal Contact with Sediment 


Arsenic 1.34E-06 1.23E-04 8 1.09E-02 

Beryllium 1.95E-07 5.00E-05 13, 1 3.90E-03 

Cobalt 3.85E-06 26 

Lead 2.70E-06 26 

Sodium 

3.17E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

1.48E-02 

WAG 1, SWMU 100% ESE-Excavation Ingestion of Sediment 

Aluminum 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-238 


2.14E-06 3.00E-04 a 7.14E-03 

3.12E-07 5.00E-03 a 6.24E-05 

6.16E-06 


5.07E-05 

Pathway Total 

WAG 1. SWMU 100% ESE-Excavation Inhalation of Sediment 

Aluminum 

7.01E-08 

Arsenic 

3.25E-11 

Beryllium 


Cohalt 

9.35E-11 

Page 23 of 53 

7.20E-03


I u I'AL 


REFERENCE FWD HAZARD HAZARD HAZARD 

ANALYSIS 

Lead 

CDI 

6.56E-11 

DOSE SOURCE QUOTIENT INDEX INDEX 

Sodium 

7.70E-10 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

SWMU-Total 

2.20E-02 

WAG 1, SWMU 100b, ESE-Excavation Dermal Contact with Sediment 


Arsenic 1.22E-06 1.23E-04 8 9.93E-03 

Beryllium 1.50E-07 5.00E-05 13, 1 3.01E-03 

Cobalt 1.95E-06 26 

Lead 2.37E-06 26 

Sodium 

2.96E-05 

Gross Alpha 

Gross Beta 

Uranium-235 

Uranium-23 8 

Pathway Total 

1.29E-02 

WAG 1, SWMU 100b, ESE-Excavation Ingestion of Sediment 

Aluminum 

3.60E-03 

Arsenic 

1.95E-06 3.00E-04 a 6.51E-03 

Beryllium 

2.40E-07 5.OOE-03 a 4.81E-05 

Cobalt 

Lead 

Sodium 

3.12E-06 

3.79E-06 


Gross Alpha 

Gross Beta 

Uranium-235 

Uranium-238 

Pathway Total 

6.56E-03 

WAG 1, SWMU 100b, ESE-Excavation Inhalation of Sediment 

Aluminum 

5.46E-08 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

2.96E-11 

3.65E-12 


5.76E-11 

7.18E-10 

Gross Alpha 

Gross Beta 

Uranium-235 

Uranium-238 

Pathway Total 

SWMU Total 

WAG 1, SWMU IOOc, ESO-Excavation Dermal Contact with Soil 

1.95E-02 

Aluminum 

Arsenic 

2.47E-03 

1.48E-06 1.23E-04 

4s 

8 1.20E-02 

Beryllium 

1.32E-07 5.00E-05 13, 1 2.64E-03 

Cobalt 

2.09E-06 26 

Lead 

3.05E-06 26 

Sodium 

Thallium 

9.86E-05 

1.68E-08 52 


1 S5E-07 43 



Endrin Ketone 

Naphthalene 

Phenanthrene 

3.80E-08 

5.19E-10 

5.35E- 10 

9.39E-08 

2.58E-07 

43 

2 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thonum-228 

Uranium-238 

Page 24 of 53


IUIAL 




Pathway Total 

1.46E-02 

WAG 1, SWMU lOOc, ESO-Excavation Ingestion of Soil 

Aluminum 

3.95E-03 

Arsenic 

2.36E-06 3.00E-04 a 7.87E-03 

Beryllium 

2.1 1E-07 5.00E-03 a 4.22E-05 

Cobalt 

Lead 

Sodium 

Thallium 




Endrin Ketone 

Naphthalene 

3.34E-06 


1 S8E-04 

2.69E-08 

1.24E-07 

3.04E-08 



7.51E-08 

e 

Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-238 

2.06E-07 

' Pathway Total 

7.92E-03 

WAG 1, SWMU lOOc, ESO-Excavation Inhalation of Soil 

Aluminum 

6.OOE-08 

Arsenic 

3.58E-11 

Beryllium 

3.20E-12 

Cobalt 

5.06E-11 

Lead 

7.41E-11 

Sodium 

2.39E-09 

Thallium 



1.89E-12 

3-Nitroaniline 4.62E- 13 


6.29E-15 

Endrin Ketone 

6.50E-15 


Phenanthrene 

3.13E-12 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-238 

Pathway Total 

SWMU Total 

2.26E-02 

WAG 1. SWMU 136, ESO-Excavation Dermal Contact with Soil 


Arsenic 9.33E-07 1.23E-04 8 7.58E-03 

Beryllium 1.16E-07 5.00E-05 13, 1 2.33E-03 

Cobalt 

2.67E-06 

26 

Lead 

1.99E-06 

26 

Sodium 

7.29E-05 

Sulfate 

2.28E-04 


1,l. 1 -Trichloroethane 2.17E-08 55 

1,l -Dichloroethene 1.41E-08 9.00E-03 31 1.57E-06 

Benzo(a)anthracene 1 .OZE-07 2 



Benzo(g,h,i)perylene 9.62E-08 2 

Dibenzo(a,h)anthracene 3.80E-08 2 



Gross Alpha 

Gross Beta 

Uranium-238 

Page 25 of 53


lUlAL 




Pathway Total 

9.91E-03 

WAG 1. SWMU 136. ESO-Excavation Ineestion of Soil 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Sulfate 

Thallium 

1.1,1 -Trichloroethane 

1,l-Dichloroethene 







Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

1.49E-06 3.00E-04 a 4.97E-03 

1.86E-07 5.00E-03 a 3.73E-05 


3.19E-06 

1.17E-04 

3.65E-04 

2.5 1E-08 

6.95E-09 

e 

4.51E-09 9.00E-03 a 5.01E-07 

8.17E-08 

8.71E-08 

9.13E-08 

7.70E-08 

3.04E-08 

7.87E-08 

2.97E-08 


WAG 1, SWMU 136, ESO-Excavation Inhalation of Soil 

Aluminum 

6.30E-08 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Sulfate 

?ballium 

1,l. 1 -Trichloroethane 








Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

2.26E-11 

2.83E-12 

6.48E- 11 


1.77E-09 

5.54E-09 

3.81E- 13 

2.70E-08 


1.24E-12 

1.32E-12 

1.38E- 12 

1.17E- 12 


1.19E- 12 


e 

Beryllium 3.76E-07 5.00E-05 13, 1 7.51E-03 

Cobalt 2.37E-06 26 

Lead 2.16E-06 26 

Sodium 

9.75E-06 

Vanadium 2.28E-05 7.00E-05 58, 5 3.26E-01 

Phenanthrene 4.70E-08 2 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

U'AG 1. SWMU 38% ESE-Excavation Ingestion of Sediment 

Aluminum 

1.73E-03 


Cobalt 

3.79E-06 

Lead 

3.46E-06 

3.34E-01 

Page 26 of 53

~~ ~ 


I'Ul'AL 




Sodium 

1.56E-05 

Vanadium 

3.65E-05 7.00E-03 b 5.22E-03 

Phenanthrene 

3.76E-08 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

5.34E-03 

WAG 1, SWMU 38% ESE-Excavation Inhalation of Sediment 

Aluminum 

Beryllium 

Cobalt 

Lead 

Sodium 

Vanadium 

Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

2.62E-08 

9.12E-12 

5.76E-11 

5.24E-11 

2.37E-10 

5.54E-10 

5.70E- 13 

S WMU Total 3.39E-0 1 

WAG 1, SWMU 38b, ESE-Excavation Dermal Contact with Sediment 


Arsenic 8.45E-07 1.23E-04 8 6.87E-03 

Beryllium l.lOE-07 5.00E-05 13, 1 2.21E-03 

Cobalt 1.57E-06 26 


Sodium 

1.65E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

9.08E-03 


Aluminum 

3.34E-03 

Arsenic 

1.35E-06 3.00E-04 a 4.5 IE-03 

Beryllium 

1.77E-07 5.00E-03 a 3.53E-05 

Cobalt 

Lead 

Sodium 

2.52E-06 

6.84E-06 

2.65E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 4.546-03 


Aluminum 

5.06E-08 

Arsenic 

2.05E-11 

Beryllium 

2.68E-12 

Cobalt 

3.82E-11 

Lead 1.04E- 10 

Sodium 4.0 1E- 10 

Gross Alpha 

Gross Beta 

Uranium-23 8 

Pathway Total 

SWMU Total 

1.36E-02 

WAG 1, SWMU 38c, ESO-Excavation Dermal Contact with Soil 


Arsenic 

1.38E-06 3.23E-04 8 l.12E-02 

Beryllium 

1.28E-07 5.00E-05 13, 1 2.56E-03 

Cobalt 

2.21E-06 26 

Lead 

3.24E-06 26 

Sodium 

Thallium 


2.78E-08 52 

2-Hexanone 

1.17E-08 36 

Page 27 of 53


IUlAL 




Ar0clor-126O 1.87E-08 46 


7.05E-08 

Benzo(a)pyrene 6.11E-08 


8.92E-08 

Phenanthrene 

1.19E-07 

Gross Alpha 

Gross Beta 

Neptunium-23 7 

Thorium-228 

Uranium-235 

Uranium-238 

Pathway Total 

1.37E-02 

WAG 1, SWMU 38c, ESO-Excavation Ingestion of Soil 

Aluminum 

3.42E-03 

Arsenic 2.20E-06 3.00E-04 a 7.33E-03 

Beryllium 2.05E-07 5.00E-03 a 4.09E-05 

Cobalt 

3.54E-06 

Lead 

5.18E-06 

Sodium 

7.46E-05 

Thallium 


2-Hexanone 

3.76E-09 

Aroclor- 1260 

1.5OE-08 

Benzo(a)anthracene 5.64E08 




7.14E-08 

Phenanthrene 

9.50E-08 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-23 8 

Pathway Total 

7.38E-03 

WAG 1, SWMU 38c, ESO-Excavation Inhalation of Soil 

Aluminum 

5.19E-08 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Thallium 

2-Hexanone 

Aroclor- 1260 




Phenanthrene 

3.34E-11 

3.1 OE- 12 

5.37E-11 

7.86E-11 

1.13E-09 

6.76E-13 

5.70E- 14 

2.27E-13 

8.55E-13 

7.41 E- 13 

1.08E-12 

1.44E- 12 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

Pathway Total 

SWW-Total 2.1 1E-02 

WAG 7, SWMU 130, ESO-Excavation Dermal Contact with Soil 

Lead 2.65E-06 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 7, SWMU 130, ESO-Excavation Ingestion of Soil 

1 asd 4 25F-06 

Page 28 of 53





Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 6.44E- 11 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

S WMU Total 



Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

7.48E-06 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

1.13E-10 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

SWMU Total 


Lead 2.75E-05 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

6.69E-10 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

S WMU- Total 

WAG 7, 7. SWMU 133, 133. ESO-Excavation Dermal Contact with Soil 

Lead 3.80E-05 26 









Phenanthrene 

2.75E-07 

2.06E-06 

1.55E-06 

1.67E-06 

9.21E-07 

1.39E-06 

1.14E-07 

7.63E-07 

1.87E-06 

Gross Alpha 

Gross Beta 

Uranium-238 

Page 29 of 53


IUlAL 




Pathway Total 


Lead 

6.09E-05 


2.20E-07 


1.65E-06 


1.24E-06 


1.34E-06 


7.37E-07 

Benzo(k)fluoranthene 1 .I 1E-06 


Indene( 1,2,3-cd)pyrene 6.11E-07 

Phenanthrene 

1.49E-06 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

9.23E-10 


3.34E-12 


2.50E-11 


1.88E-11 


2.03E-11 



1.69E-11 

Dibenzo(a,h)anthracene 1.38E- 12 


Phenanthrene 

2.26E-11 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

SWMU Total 

WAG 7, SWMU 134, ESO-Excavation Demal Contact with Soil 

Lead 6.1 1E-06 26 


7.05E-08 


6.58E-08 


9.81E-08 


3.48E-08 

Phenanthrene 

1.58E-07 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

9.77E-06 


5.64E-08 


5.26E-08 


7.85E-08 


2.78E-08 

Phenanthrene 

1.26E-07 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathwav Total 


Lead 1.48E- 10 


8.55E-13 


7.98E-13 


1.19E-12 

Benzo(g,h,i)perylene 4.22E- 13 

Phenanthrene 

1.92E-12 

Gross Alpha 

Gross Beta 

Page 30 of 53


IUlAL 



ANALYSIS CDI DOSE SOURCE QUOTIENT INDEX R\IDEX 

Uranium-238 

Pathway Total 

S WMU Total 

WAG 7, SWMU 8b, ESO-Excavation Dermal Contact with Soil 


Arsenic 9.51E-07 1.23E-04 8 7.73E-03 

Beryllium 1.63E-07 5.00E-05 13, 1 3.27E-03 

Cobalt 1.81E-06 26 

Lead 2.34E-06 26 


1.34E-05 

Sodium 

2.55E-05 



Aroclor-1260 1.34E-08 46 

Benzo( a)anthracene 8.11E-08 2 



Dihenzohran 

1.16E-07 




Gross Alpha 

Gross Beta 

Neptunium-237 

Thonum-228 

Thonum-230 

Uranium-235 

Uranium-238 

Pathway Total 

l.lOE-02 

WAG 7, SWMU 8h, ESO-Excavation Ingestion of Soil 

Aluminum 


Arsenic 1.52E-06 3.00E-04 a 5.07E-03 


Cobalt 

2.90E-06 

Lead 

3.74E-06 


2.14E-05 

Sodium 4.08B05 

Thallium 5.81 E-08 



Aroclor- 1260 

1.07E-08 


6.49E-08 


9.44E-08 


1.07E-07 

Dibenzofuran 

9.25E-08 


Naphthalene 

9.46E-08 

e 

Phenanthrene 

8.62E-08 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Thorium-230 

Uranium-235 

Uranium-238 

Arsenic 

2.31E-11 

Beryllium 

3.97E-12 

Cobalt 4.40E- 11 

Lead 

5.68E-11 


3.25E-10 

Sodium 

6.19E-10 

Page 31 of 53





Thallium 

8.81E-13 


Aroclor-1260 




Dibenzofuran 


Naphthalene 

Phenanthrene 

6.84E- 13 

1.63E-13 

9.85E-13 

1.43E-12 

1.62E-12 

1.40E- 12 

1.31E-12 

1.43E-12 

1.31E-12 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Thorium-230 

Uranium-235 

Uranium-238 

Pathway Total 

S W MU Total 

1.61E-02 

WAG 1, SWMU 100% ISE-Current Industrial Dermal Contact with Sediment 


Arsenic 9.30E-07 1.23E-04 8 7.56E-03 

Beryllium 1.35E-07 5.00E-05 13, 1 2.71E-03 

Cobalt 2.68E-06 26 

Lead 1.88E-06 26 

Sodium 

2.20E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

1.03E-02 

WAG 1, SWMU 100% ISE-Current Industrial Ingestion of Sediment 

Aluminurn 

1.96E-03 

Arsenic 

9.06E-07 3.00E-04 a 3.02E-03 

Beryllium 

1.32E-07 5.00E-03 a 2.64E-05 

Cobalt 

Lead 

Sodium 

2.61E-06 

1.83E-06 

2.15505 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

3.05E-03 

WAG 1, SWMU 100% ISE-Current Industrial Inhalation of Sediment 

Aluminum 

1.83E-07 

Arsenic 

8.46E-11 

Beryllium 

1.23E-11 

Cobalt 

2.43E-10 

Lead 

1.71E-10 

Sodium 

2.00E-09 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 1, SWMU 100% ISW-Current Industrial Dermal Contact with Water 

Aluminum 495 

Cadmium 1.04506 5.00E-06 16, 1 2.08E-01 

Cobalt 26 

Lead 1.22E-06 26 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-238 

Pathway Total 

2.08E-01 

Page 32 of 53


IUlAL 




S WMU Total 2.22E-0 1 

WAG 1, SWMU 100b, ISE-Current Industrial Dermal Contact with Sediment 

Aluminum 1.56E-03 4,5 

Arsenic 

8.49E-07 1.23E-04 8 6.90E-03 

Beryllium 

1.04E-07 5.00E-05 13, 1 2.09E-03 

Cobalt 

1.35E-06 26 

Lead 

1.65E-06 26 

Sodium 

2.06E-05 

Gross Alpha 

Gross Beta 

Uranium-235 

Uranium-238 

Pathway Total 

8.99E-03 

WAG 1, SWMU 100h, ISE-Current Industrial Ingestion of Sediment 

Aluminum 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-235 

Uranium-238 

1.52E-03 

8.27E-07 3.00E-04 a 2.76E-03 

1.02E-07 5.00E-03 a 2.04E-05 

1.32E-06 

1.61E-06 

2.00E-05 

Pathway Total 

WAG 1, SWMU 100b, ISE-Current Industrial Inhalation of Sediment 

Aluminum 

1.42E-07 

Arsenic 7.72E- 11 

Beryllium 9.50E- 12 

Cobalt 1.23E- 10 

Lead 1. SOE- 10 

Sodium 

1.87E-09 

Gross Alpha 

Gross Beta 

Uranium-235 

Uranium-23 8 

Pathway Total 

WAG 1, SWMU 100b, ISW-Current Industrial Dermal Contact with Water 

Aluminum 4,5 

Arsenic l.lOE-07 1.23E-04 8 8.92E-04 

Lead 2.12E-06 26 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-235 

Uranium-238 

Pathway Total 

SWMU Total 

WAG 1. SWMU lOOc, ISO-Current Industrial Dermal Contact with Soil 


Arsenic 6.22E-07 1.23E-04 8 5.06E-03 

Beryllium 4.80E-08 5.00E-05 13, 1 9.60E-04 

Cohalt 7.23E-07 26 

Lead 1.93E-06 26 

Sodium 

1.70E-05 


1.79E-08 

Gross Alpha 

Gross Beta 

Thorium-228 

Uranium-235 

Uranium-238 

Pathway Total 

Page 33 of 53 

2.78E-03 

8.92E-04 

6.02E-03 

1.27E-02


IUlAL 

EXPOSURE 

PATHWAY 



WAG 1, SWMU IOOc, ISO-Current Industrial Ingestion of Soil 


Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 


Gross Alpha 

Gross Beta 

Thorium-228 

Uranium-235 

Uranium-238 

6.06E-07 3.00E-04 a 2.02E-03 

4.68E-08 5.00E-03 a 9.35E-06 

7.04E-07 

1.88E-06 

1.65E-05 

8.72E-09 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sod& 


5.66E-11 


6.57E-11 

1.75E-I0 

1.54E-09 

8.14E- 13 

Gross Alpha 

Gross Beta 

Thorium-228 

Uranium-235 

Uranium-238 

Pathway Total 

S WMU Total 

WAG 1, SWMU 136, ISO-Current Industrial Dermal Contact with Soil 

Aluminum 3.2OE-05 4s 

Arsenic 

2.70E-08 1.23E-04 8 2.19E-04 

Beryllium 

1.90E-09 5.00E-05 13, 1 3.80E-05 

Cobalt 

Lead 

1.19E-07 

2.87E-08 

26 

26 

Sodium 

3.83E-07 

Sulfate 


Thallium 

6.19E-10 

52 


3.36E-09 

2 



2 


5.66E-09 

2 

Benzo( g,h,i)perylene 

2.39E-09 

2 

Dibenzo(qh)anthracene 7.16E-10 

2 


2 

Phenanthrene 

6.98E-10 

2 

Gross Alpha 

Gross Beta 

Uranium-238 

8.05E-03 

Arsenic 2.63E-08 3.00E-04 a 8.75E-05 


Cobalt 

1.16E-07 

Lead 

2.80E-08 

Sodium 

3.73E-07 

Sulfate 


Thallium 

6.03E-10 


1.64E-09 


2.24E-09 


2.76E-09 


1.16E-09 

Dibenzo( ah)anthracene 3.49E- 10 

Page 34 of 53


IUlAL 






Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

8.79E-05 

WAG 1, SWMU 136, ISO-Current Industrial Inhalation of Soil 


Arsenic 

2.45E-12 

Beryllium 

1.73E-13 

Cobalt 

1.09E-11 

Lead 

2.61E-12 

Sodium 

3.48E-11 

Sulfate 3.91E- 10 

Thallium 

5.63E-14 


1.53E-13 


2.09E-13 


2.57E-13 


1.09E-13 

Dibenzo(qh)anthracene 3.26E-14 

' Indeno( 1,2,3-cd)pyrene 1.25E-13 

Phenanthrene 

3.18E-14 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

S WMU Total 

3.45E-04 



Beryllium 2.61E-07 5.00E-05 13, 1 5.22E-03 

Cobalt 1.65E-06 26 

Lead 1.50E-06 26 

Sodium 

6.77E-06 

Vanadium 1.59E-05 7.00E-05 58, 5 2.27E-01 


Gross Alpha 

Gross Beta 

Uranium-238 





Cobalt 

1.61E-06 

Lead 

1.46E-06 

Sodium 

6.60E-06 

Vanadium 1.55E-05 7.00E-03 b 2.2 IE-03 

Phenanthrene 

1.59E-08 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

2.26E-03 

WAG 1. SWMU 38% ISE-Current Industrial Inhalation of Sediment 

Aluminum 

6.83E-08 

Beryllium 

2.38E-11 

Cobalt 

1.50E-I0 

Lead 

1.37E-10 


Vanadium 

1.44E-09 

Phenanthrene 

1.48E-12 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

Page 35 of 53


IUlAL 





Arsenic 8.62E-08 1.23E-04 8 7.01E-04 


Sodium 

Chloroform 2.80E-06 2.00E-03 24 1.40E-03 

bis(2-Ethylhexy1)phthalate 3.65E-06 3.80E-03 15 9.60E-04 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

3.06E-03 

S WMU Total 

2.37E-01 



Arsenic 

5.88E-07 1.23E-04 8 4.78E-03 

Beryllium 

7.67E-08 5.00E-05 13, 1 1 S3E-03 

Cobalt 

1.09E-06 26 

Lead 

2.97E-06 26 

Sodium 

1.15E-05 

Gross Alpha 

Gross Beta 

Uranium-238 


WAG 1, SWMU 38b, ISE-Current Industrial Ingestion of Sediment 


Arsenic 

5.72E-07 3.00E-04 a 1.91E-03 

Beryllium 

7.47E-08 5.00E-03 a 1.49E-05 

Cobalt 

Lead 

Sodium 

1.07E-06 

2.89E-06 

1.12E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

1.92E-03 

WAG 1, SWMU 38b, ISE-Current Industrial Inhalation of Sediment 

Aluminum 

1.32E-07 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

5.34E-11 

6.98E-12 

9.95E- 11 

2.70E-10 

1.05E-09 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 1, SWMU 38b, ISW-Current Industrial Dermal Contact with Water 


Sodium 

Gross Alpha 

Gross Beta 

Neptunium-237 

Plutonium-238 

Uranium-234 

Uranium-238 

Pathway Total 

SWMU Total 

8.24E-03 

WAG 1, SWMU 38c, ISO-Current Industrial Dermal Contact with Soil 

Alummum 5.42E-03 4s 

Arsenic 3.18E-06 1.23E-04 8 2.59E-02 

Beryllium 2.65E-07 5.00E-05 13, 1 5.30E-03 

Cobalt 4.91E-06 26 

Lead 9.68E-06 26 

Sodium 


Aroclor-1260 4.36E-08 46 

Page 36 of 53





Benzo(a)anthracene 1.39E-07 2 


1.20E-07 

2 


1.76E-07 

2 

Phenanthrene 

2.46E-07 

2 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-23 5 

Uranium-238 

Pathway Total 

3.12E-02 

WAG 1, SWMU 38c, ISO-Current Industrial Ingestion of Soil 

Aluminum 

5.28E-03 

Arsenic 3.10E-06 3.00E-04 a 1.03E-02 


Cobalt 


Lead 

9.42E-06 

Sodium 


Aroclor- 1260 

2.12E-08 


6.75E-08 


5.85E-08 


8.5SE-08 

Phenanthrene 

1.20E-07 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

Pathway Total 

1.04E-02 

WAG 1, SWMU 38c, ISO-Current Industrial Inhalation of Soil 

Aluminum 



Beryllium 

2.41E-11 

Cobalt 


Lead 8.80E- 10 

Sodium 

3.95E-09 

Aroclor-1260 

1.98E-12 


6.30E-12 

Benzo(a)p yrene 5.46E- 12 


7.98E-12 

Phenanthrene 

1.12E-11 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

Pathway Total 

SWMU Total 

4.1 SE-02 


Lead 3.47E-07 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathwav Total 

WAG 7. SWMU 132, ISO-Current Industnal Ingesbon of Soil 

Lead 

3.38E-07 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Page 37 of 53


IUlAL 


REFERENCE FWD HAZARD HAZARD HAZARD 


Lead 

3.15E-11 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

SWMU Total 


Lead 3.42E-07 26 






Benzo(k)flporanthene 

Dibenzo(dh)anthracene 


Phenanthrene 

2.78E-09 

2.19E-08 

1.65E-08 

1.77E-08 

9.70E-09 

1.48E-08 

1.05E-09 

8.02E-09 

1.98E-08 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 7, SWMU 133, ISO-Current Industrial Ingestion of Soil 

Lead 







Dibenzo(qh)anthracene 

Indene( 1,2,3-cd)pyrene 

Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

3.33E-07 

1.36E-09 

1.07E-08 

8.01E-09 

8.63E-09 


7.19E-09 

5.14E- 10 

3.90E-09 

9.66E-09 

Pathway Total 


Lead 3.11E-11 

Acenaphth ylene 1.27E- 13 


9.98E-13 


7.48E-13 


8.06E-13 




6.71E-13 

Dibenzo(qh)anthracene 4.8OE-14 

Indeno( 1,2,3-cd)pyrene 3.64E- 13 

Phenanthrene 

9.02E-13 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

S WMU Total 


Lead 3.16E-08 26 

Benzo(a)anthracene 5.9 1E- 10 2 

Benzo(a)pyrene 5.9 1 E- 10 2 

Benzo(b)fluoranthene 8.86E- 10 2 

Benzo(g,h,i)perylene 3.04E- 10 2 

Phenanthrene l.lOE-09 2 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

Page 38 of 53






Lead 

3.08E-08 


Benzo( a)pyrene 2.88E- 10 




1.48E-10 

Phenanthrene 

5.34E-10 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

2.88E-12 


2.69E-14 

Benzo(a)pyrene 2.69E- 14 




Phenanthrene 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

S WMU Total 



Arsenic 1.39E-06 1.23E-04 8 1.13E-02 

Beryllium 1.47E-07 5.00E-05 13, 1 2.93E-03 

Cobalt 2.48E-06 26 

Lead 1.86E-06 26 

Sodium 

2.17E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

1.42E-02 


Aluminum 

6.39E-04 

Arsenic 


Beryllium 

1.43E-07 5.00E-03 a 2.85E-05 

Cobalt 

Lead 

Sodium 

2.42E-06 

1.8 IE-06 

2.11E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


WAG 7. SWMU 8% ISE-Current Industrial Inhalation of Sediment 

Aluminum 

5.96E-08 


Beryllium 

1.33E-11 

Cobalt 

2.26E-10 

Lead 

1.69E-10 

Sodium 

1.97E-09 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Aluminum 4,5 

Antimony 

1.32E-06 8.00E-06 7 1.65E-01 

Arsenic 

9.28E-08 1.23E-04 8 7.55E-04 

Cadmium 

1.86E-07 5.00E-06 16, 1 3.72E-02 

Lead 

2.66E-07 26 

Manganese 

1.09E-03 2.00E-04 38 5.46E+OO 

Page 39 of 53


IUlAL 



ANALYSIS 

Silicon 


Sodium 

Sulfate 

Thallium 52 

Vanadium 3.95E-05 7.00E-OS 58, 5 5.64E-01 


Gross Alpha 

Gross Beta 

Pathway Total 

6.23E+00 

S WMU Total 

WAG 7, SWMU 8b, ISO-Current Industrial Dermal Contact with Soil 

6.25E+00 


Arsenic 

Beryllium 

Cobalt 

Lead 


Sodium 

Thallium 


Aroclor-1260 




Dibenzoh 


Naphthalene 

Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

7honum-230 

Uranium-234 

Uranium-235 

Uranium-238 

1.90E-06 

3.55E-07 


5.92E-06 

2.86E-05 

3.18E-05 

6.93E-08 

1.21E-07 

7.63E-08 

3.12E-07 

2.96E-07 

3.77E-07 

2.77E-07 

2.31E-07 

2.99E-07 

9.83E-07 

1.23E-04 8 

52 

43 

46 

2 

2 

2 

2 

43 

2 

Pathway Total 

WAG 7, SWMU 8b, ISO-Current Industrial Ingestion of Soil 

Aluminum 3.43503 

Arsenic 

Beryllium 

Cobalt 

Lead 


Sodium 

Thallium 


Aroclor-1260 




Dibenzofuran 


Naphthalene 

Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thonum-230 

Uranium-234 

Uranium-23 5 

Uranium-238 

1.54E-02 

5.OOE-05 13, 1 7.09E-03 

26 

26 

1.85E-06 3.00E-04 a 6.17E-03 

3.45507 5.00E-03 a 6.91E-OS 


5.77E-06 

2.79E-05 

3.09E-05 

6.75E-08 

5.87E-08 

3.72E-08 

1.52E-07 

1.44E-07 

1.84E-07 

1.3SE-07 

1.13E-07 

1.45E-07 


e 

Pathway Total 

WAG 7. SWMU 8b, ISO-Current Industrial Inhalation of Soil 

Page 40 of 53 

2.25E-02 

6.24E-03





Aluminum 

3.20E-07 


Beryllium 

3.22E-11 

Cobalt 


Lead 5.39E- 10 


2.60E-09 

Sodium 

2.89E-09 

Thallium 

6.30E-12 

2-Methylnaphthalene 5.48E- 12 

Aroclor-1260 3.47E- 12 

Benzo( a)anthracene 1.42E- 11 


1.35E-11 


1.72E-11 

Dibenzohran 

1.26E-11 


Naphthalene 

1.36E-11 

Phenanthrene 


Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-230 

Uranium-234 

Uranium-235 

Uranium-238 

Pathway Total 

SWMU Total 

2.88E-02 

WAG 1. SWMU 100% FSE-Future Industrial Dermal Contact with Sediment 


Arsenic 

3.02E-06 1.23E-04 8 2.46E-02 

Beryllium 

4.40E-07 5.OOE-05 13, 1 8.80E-03 

Cobalt 

8.69E-06 26 

Lead 

6.1 OE-06 26 

Sodium 

7.16E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathwav Total 

3.34E-02 

WAG 1, SWMU 100% FSE-Future Industrial Ingestion of Sediment 

Aluminum 

1.96E-03 

Arsenic 9.06E-07 3.00E-04 a 3.02E-03 


Cobalt 

2.61E-06 

Lead 

1.83E-06 

Sodium 

2.15E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

3.05E-03 

WAG I. SWMU IOOa, FSE-Future Industrial Inhalation of Sediment 

Aluminum 

1.83E-07 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

8.46E-11 

1.23E- 11 

2.43E-10 

1.71E-10 

2.00E-09 

Gross Alpha 

Gross Beta 

Uranium-238 

Path wav Total 

U’AG I. SWMU 100% FSW-Future Industnal Dermal Contact with Surfacewater 

Alummum 

Cadmium 

Cobalt 

4s 

3.38E-06 5.00E-06 16, 1 6.77E-0 1 

26 

Page41 of53


IUlAL 




Lead 3.97E-06 26 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-238 

Pathway Total 

6.77E-01 

S WMU Total 

7.13E-01 

WAG 1, SWMU 100b, FSE-Future Industrial Dermal Contact with Sediment 


Arsenic 2.76E-06 1.23E-04 8 2.24E-02 

Beryllium 3.39E-07 5.00E-OS 13, 1 6.78E-03 


Lead 5.35E-06 26 

Sodium 

6.68s-05 

Gross Alpha 

Gross Beta 

Uranium-235 

Uranium-238 

Pathway Total 

2.92E-02 

WAG 1, SWMU IOOb, FSE-Future Industrial Ingestion of Sediment 

Aluminum 

1.52E-03 

Arsenic 

8.27E-07 3.00E-04 a 2.76E-03 

Beryllium 

1.02E-07 5.00E-03 a 2.04E-05 

Cobalt 

Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-235 

Uranium-238 

1.32E-06 

1.61E-06 

2.00E-05 

Arsenic 7.72E11 

Beryllium 

9.50E-12 

Cobalt 

1.23E-10 

Lead 1 SOE- 10 

Sodium 

1.87E-09 

Gross Alpha 

Gross Beta 

Uranium-235 

Uranium-238 

Pathway Total 

WAG 1, SWMU IOOb, FSW-Future Industrial Dermal Contact with Surfacewater 

Aluminum 

4s 

Arsenic 

3.56E-07 1.23E-04 8 2.90E-03 

Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-235 

Uranium-238 

Pathway Total 

6.89E-06 26 

S WMU Total 

WAG 1, SWMU IOOc, FGW-Future Industrial Dermal Contact with Groundwater 

Aluminum 495 

Barium 3.94E-OS 4.90E-03 9 8.OSE-03 

Manganese 3.63E-04 2.00E-04 38 1.82E+00 


bis(2-Ethylhexy1)phthalate 2.68E-06 3.80B03 15 7.04E-04 

Gross Alpha 

Page 42 of 53 

2.9OE-03 

3.49E-02


IUlAL 




Gross Beta 

Pathway Total 

1.83E+00 

WAG 1, SWMU IOOc, FGW-Future Industrial Ingesaon of Groundwater 

Aluminum 

1.30E-01 

Barium 6.71E-03 7.00E-02 a 9.59E-02 

Manganese 6.18E-02 5.00E-03 a 1.24E+O 1 

Methylene Chloride 4.89E-05 6.00E-02 a 8.15E-04 


Gross Alpha 

Gross Beta 

Pathway Total 

1.25E+01 

WAG 1, SWMU lOOc, FGW-Future Industrial Inhalation of Groundwater 

Aluminum 





Gross Alpha 

Gross Beta 

Pathway Total 

5.95E-06 

WAG 1, SWMU lOOc, FSO-Future Industrial Dermal Contact with Soil 


Arsenic 2.26506 1.23E-04 8 1.83E-02 

Beryllium 2.02E-07 5.00E-05 13, 1 4.03E-03 

Cobalt 3.19E-06 26 


Sodium 1.51 E-04 




5.8 IE-08 


7.92E-10 




Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-238 

Pathway Total 

2.24E-02 

WAG 1. SWMU lOOc, FSO-Future Industrial Ingestion of Soil 

Aluminum 

1.13E-03 

Arsenic 6.77E-07 3.00E-04 a 2.26E-03 


Cobalt 

9.56E-07 

Lead 

1.40E-06 

Sodium 


Thallium 

7.71E-09 


3.56E-08 


8.72E-09 

Endosulfan Sulfate 1.19E- 10 

Endrin Ketone 

1.23E-10 

Naphthalene 

2.15E-08 

e 

Phenanthrene 

5.91E-08 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-238 

Pathway Total 

2.27E-03 

WAG 1, SWMU lOOc, FSO-Future Industrial Inhalation of Soil 

Aluminum 

1.06E-07 

Page 43 of 53


IUlAL 




Beryllium 

5.65E-12 

cobalt 

Lead 

Sodium 

Thallium 




Endrin Ketone 

Naphthalene 

Phenanthrene 

8.92E-11 

1.31E- 10 


7.19E- 13 

3.33E-12 

8.14E- 13 

1.1 IE-14 

1.15E-14 

2.01E-12 

5.52E-12 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-238 

Pathway Total 

SWMU Total 1.43E+O 1 

WAG 1, SWMU 136, FGW-Future Industrial Dermal Contact with Groundwater 


Manianese 3.21E-04 2.00E-04 38 1.61E+00 


bis(2-Ethylhexy1)phthalate 1.34B06 3.80E-03 15 3.52E-04 

Gross Alpha 

Gross Beta 

Pathway Total 

1.61E+00 

WAG 1, SWMU 136, FGW-Future Industrial Ingestion of Groundwater 

Barium 3.23E-03 7.00E-02 a 4.6 1 E-02 



1.08E-03 

bis(2-Ethylhexy1)phthalate 9.78E-06 2.00E-02 a 4.89E-04 

Gross Alpha 

Gross Beta 



1.12E-04 

bis(2-Ethylhexyl)phthalate 

Gross Alpha 

Gross Beta 

Pathway Total 

WAG 1, SWMU 136, FSO-Future Industrial Dermal Contact with Soil 


Arsenic 

5.70E-08 1.23E-04 

Beryllium 

7.12E-09 5.00E-05 

Cobalt 

Lead 

Sodium 

Sulfate 

Thallium 

1.1.1 -Trichloroethane 


1.63E-07 

1.22E-07 


1.39E-05 

9.60E- IO 

1.33E-09 

8.62E-10 9.00E-03 







Phenanthrene 

Gross Alpha 

Gross Beta 

6.24E-09 

6.66E-09 

6.97E-09 

5.88E-09 

2.32E-09 

6.02E-09 

2.27E-09 

8 4.63E-04 

13, 1 1.42E-04 

26 

26 

52 

55 

31 9.57E-08 

2 

2 

2 

2 

2 

2 

2 

Page 44 of 53


IUlAL 



Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Sulfate 

Thallium 

1,1,1 -Trichloroethane 








Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

1.71E-08 3.00E-04 a 5.70E-05 



3.66E-08 

1.34E-06 


2.88E-10 

7.97E-11 

5.17E-11 

9.37E- 10 

9.98E-10 

1.05E-09 

8.82E-10 

3.49E- 10 

9.02E-10 

3.40E- 10 

9.00E-03 

e 

a 

5.74E-09 

Arsenic 

1.60E-12 

Beryllium 

1.99E-13 

Cobalt 4.57E- 12 

Lead 

3.41E-12 

Sodium 

1.25E-IO 

Sulfate 3.91E-10 

lhallium 

2.69E-14 


1.9OE-09 

e 

1,l -DichIoroethene 3.28E-09 

Benzo(a)anihracene 8.74E- 14 


9.32E-14 


9.76E-14 


8.23E-14 

Dibenzo(a,h)anthracene 3.26E- 14 


Phenanthrene 

3.18E-14 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

S WMU Total 

WAG 1, SWMU 38% FSE-Future Industrial Dermal Contact with Sediment 


Beryllium 8.48E-07 5.00E-05 13, 1 1.70E-02 

Cobalt 5.35E-06 26 


Sodium 

2.20E-05 

Vanadium 5.15E-05 7.00E-05 58, 5 7.36E-01 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 1, SWMU 38a, FSE-Future Industrial Ingestion of Sediment 


Beryllium 

2.54E-07 5.00E-03 a 5.09E-05 

Cobalt 

1.61E-06 

Lead 

1.46E-06 

Page 45 of 53 

7.53E-01 

1.26E+01





Sodium 

6.60E-06 

Vanadium 1.55E-05 7.00E-03 b 2.21E-03 

Phenanthrene 

1.59E-08 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

2.26E-03 

WAG 1, SWMU 38% FSE-Future Industrial Inhalation of Sediment 

Aluminum 

6.83E-08 

Beryllium 

2.38E-11 

Cobalt 1 SOE- 10 

Lead 1.37E- 10 

Sodium 

6.16E-10 

Vanadium 

1.44E-09 

Phenanthrene 

1.48E-12 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 1, SWMU 38% FSW-Future Industrial Dermal Contact with Surfacewater 

Arsenic 2.80E-07 1.23E-04 8 2.28E-03 

Lead 1.45E-06 26 

Sodium 

Chloroform 9.08E-06 2.00E-03 24 4.54E-03 

bis(2-Ethylhexy1)phihalate 1.18E-05 3.80E-03 15 3.12E-03 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

9.93E-03 

SWMU Total 7.65E-01 


Aluminum 4.71E-03 4s 

Arsenic 1.91E-06 1.23E-04 8 1.55E-02 

Beryllium 2.49E-07 5.00E-05 13, 1 4.98E-03 

Cobalt 3.55E-06 26 

Lead 9.65E-06 26 

Sodium 

3.73E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

2.05E-02 

WAG 1, SWMU 38b, FSE-Future Industrial Ingestion of Sediment 

Aluminum 1.41 E-03 

Arsenic 5.72E-07 3.00E-04 a 1.91E-03 


Cobalt 

1.07E-06 

Lead 

2.89E-06 

Sodium 

1.12E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathwav Total 

1.92E-03 

WAG 1, SWMU 38b, FSE-Future Industrial Inhalation of Sediment 

Aluminum 

1.32E-07 

Arsenic 5.34E-I 1 

Beryllium 

6.98E-12 

Cobalt 

9.95E-11 

Lead 

2.70E-10 

Sodium 

1.05E-09 

Gross Alpha 

Gross Beta 

Uranium-238 

Page 46 of 53





WAG 1, SWMU 38b, FSW-Future Industrial Dermal Contact with Surfacewater 

Aluminum 4,5 

Sodium 

Gross Alpha 

Gross Beta 

Neptunium-237 

Plutonium-238 

Uranium-234 

Uranium-238 

Pathway Total 

S WMU Total 

2.24E-02 

WAG 1, SWMU 38c, FGW-Future Industrial Dermal Contact with Groundwater 

Barium 1.67E-05 4.90E-03 9 3.41 E-03 

Manganese 

1.62E-04 2.00E-04 38 8.11E-01 


3.34E-05 5.70E-02 41 5.85E-04 

Gross Beta 


WAG 1, SWMU 38c, FGW-Future Industrial Ingestion of Groundwater 

Barium 2.85E-03 7.00E-02 a 4.07E-02 

Manganese 2.76E-02 5.OOE-03 a 5.52E+00 

Methylene Chloride 1.27E-03 6.00E-02 a 2.12E-02 

Gross Beta 

Pathway Total 

5.58E+00 

WAG 1, SWMU 38c, FGW-Future Industrial Inhalation of Groundwater 




Gross Beta 

Pathway Total 

1 .%E-04 

WAG 1, SWMU 38c, FSO-Future Industrial Dermal Contact with Soil 


Arsenic 

8.79E-06 1.23E-04 8 7.14E-02 

Beryllium 

8.17E-07 5.00E-05 13, 1 1.63E-02 

Cobalt 

Lead 

Sodium 

Thallium 

2-Hexanone 

Aroclor-1260 




Phenanthrene 

1.41E-OS 

2.07E-05 

2.98E-04 

1.78E-07 

7.50E-08 

1.20E-07 


3.90E-07 

5.70E-07 

7.59E-07 

26 

26 

52 

36 

46 

2 

2 

2 

2 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

Pathway Total 

8.78E-02 

WAG 1, SWMU 38c, FSO-Future Industrial Ingestion of Soil 

Aluminum 


Arsenic 2.64E-06 3.00E-04 a 8.79E-03 

Beryllium 2.45E-07 5.00E-03 a 4.90E-05 

Cobalt 


Lead 

6.21E-06 

Sodium 

8.94E-05 

Thallium 

5.34E-08 

2-Hexanone 


Aroclor- 1260 

1.79E-08 


6.75E-08 


5.85E-08 


8.55E-08 

Page 47 of 53





Phenanthrene 

1.14E-07 

Gross Alpha 

Gross Beta 

Neptunium-237 

llonum-228 

Uranium-235 

Uranium-238 

Pathway Total 

8.84E-03 

WAG 1, SWMU 38c, FSO-Future Industrial Inhalation of Soil 

Aluminum 

3.83E-07 

Arsenic 

2.46E-10 

Beryllium 

2.29E-11 


Lead 

5.79E-10 

Sodium 

8.34E-09 

Thallium 


2-Hexanone 4.20E- 13 

Aroclor-1260 

1.67E-I2 


6.30E-12 


5.46E-12 

Benzo(b)fluoranthene 7.98512 

Phenanthrene 

1.06E-11 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

Pathway Total 

S WMU Total 

6.49E+00 

WAG 7, SWMU 130, FSO-Future Industrial Dermal Contactwith Soil 

Lead 6.12E-08 26 

Gross Alpha 

Gross Beta 

Uranium-23 8 

Pathwav Total 

WAG 7. SWMU 130, FSO-Future Industrial Ingestion of Soil 

Lead 

1.84E-08 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathwav Total 

WAG 7. SWMU 130. FSO-Future Industrial Inhalation of Soil 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

S WMU Total 

WAG 7. SWMU 131, FSO-Future Industrial Dermal Contact with Soil 

Lead 1.17E-08 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathwav Total 

WAG 7, SWMU 131, FSO-Future Industrial Ingestion of Soil 

Lead 

3.50E-09 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathwav Total 

WAG 7. SWMU 131, FSO-Future Industrial Inhalation of Soil 

Lead 

3.27E-13 

Page 48 of 53


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Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

S WMU Total 


Lead 9.56E-07 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

2.87E-07 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 7, SWMU 132, FSO-Future Industrial Inhalation of Soil 

Lead 

2.68E-11 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

S WMU Total 


Lead 1.11E-06 26 









Phenanthrene 

8.02E-09 

6.02E-08 



2.69E-08 


3.32E-09 

2.23E-08 

5.44E-08 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

3.33E-07 









Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

1.20E-09 

9.02E-09 

6.78E-09 

7.30E-09 


6.10E-09 


3.34E-09 

8.16E-09 


Lead 

3.11E-11 


1.lZE-13 


8.42E-13 

Benzo( alp yrene 

6.33E-13 



Benzo(k)fluoranthene 5.69E- 13 

Dibenzo(ah)anthracene 4.65E-14 

Page 49 of 53


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__- 

3.12E-13 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

S WMU Total 


Lead 1.78E-07 26 


2.05E-09 


1.92E-09 


2.86E-09 

Benzo(g,h,i)perylene 1 .O 1E-09 

Phenanthrene 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 

5.34E-08 


Benzo(a)pyrene 2.88E- 10 




1.52E-10 

Phenanthrene 

6.91E-10 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead 4.99E- 12 


2.88E-14 


2.69E-14 

Benzo@)fluoranthene 4.0 1E-14 


1.42E-14 

Phenanthrene 

6.45E-14 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

S WMU Total 



Arsenic 

4.51E-06 1.23E-04 8 3.67E-02 

Beryllium 


Cobalt 

8.07E-06 26 

Lead 

6.05E-06 26 

Sodium 

7.04E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 



Aluminum 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

6.39E-04 


1.43E-07 5.OOE-03 a 2.85E-05 

2.42E-06 

1.81E-06 

2.1 1E-05 

Page 50 of 53 

4.54E-03




ANALYSIS CDI DOSE SOURCE QUOTENT INDEX INDEX 


Aluminum 

5.96E-08 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

1.26E-10 

1.33E-11 

2.26E-10 

1.69E-10 

1.97E-09 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Aluminum 

4s 

Antimony 

4.28E-06 8.00E-06 7 5.35E-0 1 

Arsenic 

3.01E-07 1.23E-04 8 2.45E-03 

Cadmium 

6.04E-07 5.00E-06 16, 1 1.21E-01 

Lead 

8.65E-07 26 

Manganese 

3.55E-03 2.00E-04 38 1.77E+01 

Silicon 

Sodium 

Sulfate 

Thallium 

52 

Vanadium 

1.28E-04 7.00E-05 58, 5 1.83E+00 


3.41E-06 5.70E-02 41 5.98E-05 

Gross Alpha 

Gross Beta 

Pathway Total 

2.02EM1 

S WMU Total 

2.03E+01 

WAG 7, SWMU 8b, FGW-Future Industrial Dermal Contact with Groundwater 

Aluminum 

4s 

Beryllium 

3.04E-06 5.OOE-05 13, 1 6.08E-02 

Cobalt 

Iron 

26 

26 

Manganese 

1.44E-03 2.00E-04 38 7.18E+00 

Nickel 

3.76E-05 5.40s-03 44 6.96E-03 

Silica 

Silicon 

Sulfate 

Sulfide 

1,1 -Dichloroethene 5.09E-06 9.00E-03 31 5.65E-04 


9.39E-06 9.00E-03 

1.04E-03 

Phenanthrene 

1.57E-05 

2 



57 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-234 

Uranium-235 

Uranium-238 

Pathwav Total 

7.25E+00 

WAG 7, SWMU 8b, FGW-Future Industrial Ingestion of Groundwater 

Aluminum 



Cobalt 

8.35E-03 

Iron 1.20E+O 1 

Manganese 2.44E-01 5.00E-03 a 4.89E+01 

Nickel 6.40E-03 2.00E-02 a 3.20E-01 

Silica 

4.91EM0 

Silicon 1.17E-0 1 

Sulfate 

7.79EMO 

Sulfide 

2.35E-02 

1.1-Dichloroethene 9.49E-05 9.00E-03 a 1.05E-02 

Page 51 of53





1.2-Dichloroethene 1.49E-03 9.00E-03 b 1.66E-01 

Phenanthrene 

9.78E-06 


5.2 IE-05 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-234 

Uranium-235 

Uranium-238 

Pathway Total 4.95E+01 

WAG 7, SWMU 8b, FGW-Future Industrial Inhalation of Groundwater 

Aluminum 

Beryllium 

Cobalt 

Iron 

Manganese 

1.43E-05 a 

Nickel 

Silica 

Silicon 

Sulfate 

Sulfide 


9.89E-06 


Phenanthrene 


5.43E-06 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-234 

Uranium-235 

Uranium-238 

Pathway Total 

WAG 7, SWMU 8b, FSO-Future Industrial Dermal Contact with Soil 


Arsenic 6.60E-06 1.23E-04 8 5.37E-02 

Beryllium 1.14E-06 5.00E-05 13, 1 2.27E-02 

Cobalt 1.26E-05 26 

Lead 1.623-05 26 


9.30E-05 

Sodium 

1.77E-04 



Aroclor-1260 9.33E-08 46 

Benzo( a)anthracene 5.63E-07 2 

Benzo( a)pyrene 8.19E-07 2 


Dibenzohran 

8.03E-07 

Indene( 1,2,3-cd)pyrene 7.50E-07 2 



Gross Alpha 

Gross Beta 

Neptunium-237 

ThOnUm-228 

ThOriUm-230 

Uranium-235 

Uranium-238 

Pathway Total 

7.64E-02 

WAG 7, SWMU 8b, FSO-Future Industrial Ingestion of Soil 

Aluminum 

5.31E-03 

Arsenic 1.98E-06 3.00E-04 a 6.60E-03 

Page 52 of 53


IUlAL 




Bervllium 3.41E-07 5.OOE-03 a 6.81E-05 

cobalt 

Lead 

Phosphate (oriho) 

Sodium 

Thallium 


Aroclor-1260 




Dibenzofuran 


Naphthalene 

3.78E-06 


2.79E-05 

5.32E-05 

7.56E-08 

5.87E-08 

1.40E-08 

8.45E-08 

1.23E-07 

1.39E-07 

1.20E-07 

1.13E-07 

1.23E-07 

e 

Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Thorium-230 

' Uranium-235 

Uranium-238 

1.12E-07 

Pathway Total 

6.67E-03 

WAG 7, SWMU 8b, FSO-Future Industrial Inhalation of Soil 

Aluminum 


Arsenic 

1.85E-10 

Beryllium 

3.18E-11 

Cobalt 

3.53E-10 

Lead 4.5 5E- 10 


2.6OE-09 

Sodium 


Thallium 

7.06E-12 


Aroclor- 1260 1.31E-12 


7.89E-12 


1.15E-11 




Naphthalene 

1.15E-11 

Phenanthrene 

1.05E-11 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Thorium-230 

Uranium-235 

Uranium-238 

Pathway Total 

SWMU Total 5.68E+01 

Page 53 of 53


Excess Lifetime Cancer Risks 

SLOPE OF SF SPECIFIC PATHWAY EXPOSUR 

ANALYTE CDI FACTOR EVIDENCE SOURCE RISK RISK ERISK 

WAG 1. SWMU IOOc, RGW-Residential Dermal Contact with Water 


Barium 3.15E-05 NA 9 

Manganese 2.9 IE-04 D 38 

Methylene Chloride 1.03E-06 7.89E-03 B2 41 8.10E-09 

bis(2-Ethylhexyl)phthalate 2.14E-06 7.37E-02 B2 15 1.58E-07 

Gross Alpha 

Gross Beta 

Pathway Total 

1.66E-07 

WAG 1, SWMU lOOc, RGW-Residential Ingestion of Water 

Aluminum 

2.08E-01 

Barium 1.07E-02 NA 

Manganese 9.89E-02 D 

Methylene Chloride 7.83E-05 7.50E-03 B2 a 5.87E-07 

bis(2-Ethylhexy1)phthalate 3.13E-05 1.40E-02 B2 a 4.38E-07 

Gross Alpha 

1.19E+05 

Gross Beta 

2.06E+05 

Pathway Total 

1.03E-06 

WAG 1, SWMU IOOc, RGW-Residential Inhalation of Water 

Aluminum 

Barium 

Manganese 



Gross Alpha 

Gross Beta 


NA 

D 

B2 

B2 

Arsenic 1.21E-05 3.66E+00 A 8 4.44E-05 

Beryllium 1.08E-06 4.30E+02 B2 13, 1 4.66E-04 

Cobalt 1.7 IE-05 26 

Lead 2.5 1 E-05 B2 26 

Sodium 

8.10E-04 

Thallium 1.38E-07 NA 52 



3.12E-07 

Endosulfan Sulfate 4.26E-09 

Endrin Ketone 

Naphthalene 

Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-238 


7.72E-07 

2.12E-06 

D 43 

D 2 

Pathway Total 

WAG 1. SWMU lOOc, RSO-Residential External Exposure to Soil 

Aluminum 

h 

Arsenic A h 

Beryllium B2 h 

Cobalt 

b 

Lead B2 b 

Sodium 

b 

Thallium NA b 


b 


b 


b 

Endrin Ketone 

b 

Naphthalene 

D 

h 

Phenanthrene 

D 

b 

Gross Alpha 1.92E+02 b 

Gross Beta 3.05E+02 h 

Neptunium-237 2.03E+00 4.62E-07 h 9.36E-07 

5.10E-04 

Page 1 of 64

Excess Lifetime Cancer Risks (continued) 



ThoriUm-228 1.78E+01 9.94E-07 b 1.776-05 

Uranium-238 1.74E+01 5.25E-08 b 9.16E-07 

Pathway Total 

1.96E-05 

WAG 1, SWMU lOOc, RSO-Residential Ingestion of Soil for Adult 

Aluminum 

8.15E-03 

Arsenic 

4.87E-06 1.50E+00 

Beryllium 

4.35E-07 4.30E+00 

Cobalt 

6.88E-06 

Lead 

Sodium 

Thallium 




Endrin Ketone 

Naphthalene 

Phenanthrene 

Gross Alpha 

Gross Beta 

1.OlE-05 

3.25E-04 

5.55E-08 

2.57E-07 

6.28E-08 

8.56510 

8.83E-10 

1 S5E-07 


1.01E+04 

1.60E+04 

B2 

NA 

D 

D 

Neptunium-237 

1.06E+02 3.00E-10 

Thorium-228 

9.35E+02 2.31E-10 

Uranium-238 

9.15E+02 6.20E-11 

Pathway Total 

WAG 1, SWMU lOOc, RSO-Residential Ingestion of Soil for Child 

Aluminum 

8.15E-03 

Arsenic 


Beryllium 

4.35507 4.30E+00 

Cobalt 

6.88506 

Lead 

1.OlE-05 

BZ 

Sodium 

3.25504 

Thallium 

5.55E-08 

NA 



6.28E08 

Endosulfan Sulfate 8.56510 

Endrin Ketone 

8.83E-10 

Naphthalene 

1 .ME-07 

D 

Phenanthrene 


D 

Gross Alpha 

1 .O 1E+04 

Gross Beta 

1.60E+04 

Neptunium-237 

1.06E+02 3.00E-10 

Ihonum-228 

9.35E+02 2.31E-10 

Uranium-238 

9.15E+02 6.20E-11 

A a 7.31E-06 

B2 a 1.87E-06 

3.19E-08 

2.16E-07 

5.67E-08 

A a 7.31E-06 

B2 a 1.87E-06 

3.19E-08 

2.16E-07 

5.67E-08 

9.49E-06 

Arsenic 

Barium 

Beryllium 

Cobalt 

Lead 

Manganese 

Sodium 

Thallium 




Endrin Ketone 


Naphthalene 

Phenanthrene 


Gross Alpha 

Gross Bcta 

2.60E-06 

7.28E-08 

2.87E-06 

1.98E-09 

5.78E-04 

7.24E-06 

3.88506 

3.18E-04 

1.50E+00 

4.30E+00 

7.50E-03 

1.4OE-02 

A a 3.90E-06 

NA 

BZ a 3.13E-07 

B2 

D 

NA 

BZ a 4.34E-06 

D 

D 

B2 a 4.45E-06 

Neptunium-237 2.96E+03 3.00E-10 8.88E-07 

Page 2 of 64




Thorium-228 6.01E+04 2.31E-10 3.39E-05 

Uranium-238 1.63E+03 6.20E-11 1.01E-07 

Pathway Total 

2.79E-05 

WAG 1, SWMU IOOc, RSO-Residential Inhalation of Soil 

Aluminum 

1.69E-07 

Arsenic 1 .O 1E- 10 5.OOE+O 1 A h 5.05E-09 

Beryllium 9.03E-12 8.40E+00 B2 h 7.59E-11 


Lead 2.09E-10 B2 

Sodium 

6.75E-09 

Thallium 1.15E- 12 NA 


3-Nitroaniline 1.30E- 12 


1.78E-14 

Endrin Ketone 

1.83E-14 

Naphthalene 3.22E- 12 D 

Phenanthrene 8.83E-12 D 

Gross Alpha 


Gross Beta 6.49E-01 

Neptunium-237 4.31E-03 3.45E-08 

1.49E-10 

Thorium-228 3.80E-02 9.68E-08 3.68E-09 

Uranium-238 3.72E-02 1.24E-08 4.61E- 10 

Pathway Total 

9.42E-09 

SWMU Total 

5.68E-04 

WAG 1, SWMU 136, RGW-Residential Dermal Contact with Water 


Manganese 2.57E-04 D 38 

Trichloroethene 7.96E-05 7.33E-02 NA 57 5.83E-06 

his(2-Ethylhexy1)phthalate 1.07E-06 7.37E-02 B2 15 7.89E-08 

Gross Alpha 

Gross Beta 

Pathwav Total 

5.9 IE-06 

WAG 1. SWMU 136, RGW-Residential Ingestion of Water 



Trichloroethene 1.72E-03 1.1 OE-02 NA e 1.89E-05 

his(2-Ethylhexy1)phthalate 1.57E-05 1.40E-02 BZ a 2.19E-07 

Gross Alpha 8.71E+04 

Gross Beta 

2.24E+05 

Pathway Total 

1.92E-05 

WAG 1, SWMU 136, RGW-Residential Inhalahon of Water 

Banum 

NA 

Manganese 

D 

Trichloroethene 8.97E-05 6.OOE-03 NA e 5.38507 

his(2-Ethylhexy1)phthalate 

B2 

Gross Alpha 

Gross Beta 

Pathway Total 

5.38E-07 

WAG 1. SWMU 136, RSO-Residential Dermal Contact with Soil 


Arsenic 3.06E-07 3.66E+00 A 8 l.lZE-06 

Beryllium 3.83E-08 4.30E+02 BZ 13, 1 1.65E-05 

Cobalt 8.78E-07 26 

Lead 6.55E-07 BZ 26 

Sodium 

2.39E-05 

Sulfate 

7.50E-05 


l.l,l-Trichloroethane 7.14E-09 D 55 

1.1 -Dichloroethene 4.63E-09 6.00E-01 C 31 2.78E-09 

Benzo(a)anthracene 3.36E-08 2.35E+00 BZ 2 7.90E-08 

Benzo( a)pvrene 3.58E-08 2.35E+01 B2 2 8.43E-07 

Benzo(h)fluoranthene 3.75E-08 2.35EMO BZ 2 8.82E-08 

Benzo(g,h,i)perylene 3.16E-08 D 2 

Dihenzo(ah)anthracene 1.25E-08 2.35E+01 BZ 2 2.94E-07 

Page 3 of 64




Indeno( 1,2,3-cd)pyrene 3.23E-08 2.35E+00 B2 2 7.61E-08 

Phenanthrene 

1.22E-08 

D 2 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

1.90E-05 

WAG 1, SWMU 136, RSO-Residential External Exposure to Soil 

Aluminum 

h 

Arsenic A b 

Beryllium B2 b 

Cobalt 

h 

Lead B2 b 

Sodium 

h 

Sulfate 

h 

Thallium NA h 

1,1, I-Trichloroethane D b 

1,1 -Dichloroethene C h 

Benzo(a)anthracene B2 b 

Benzo(a)pyrene B2 h 

Benzo(h)fluoranthene B2 b 

Benzo(g,h,i)perylene D b 

Dibenzo(a,h)anthracene B2 h 

Indeno( 1,2,3-cd)pyrene B2 b 

Phenanthrene D h 

Gross Alpha 5.52E+00 h 

Gross Beta 8.04E+OO b 

Uranium-238 4.36E-01 5.25E-08 h 2.29E-08 

Pathway Total 

2.29E-08 


Aluminum 

3.42E-04 

Arsenic 

1.23E-07 1.50E+00 A a 1.85E-07 

Beryllium 

1.54E-08 4.30E+00 B2 a 6.61E-08 

Cobalt 

Lead 

Sodium 

Sulfate 

Thallium 

1 , 1,1 -Trichloroethane 

1.1 -Dichloroethene 

3.53E-07 

2.63E-07 

9.62E-06 

3.01E-05 

2.07E-09 

5.74E-10 

3.72E-10 6.00E-01 

BZ 

NA 

D 

C a 2.23E-10 

Benzo(a)anthracene 6.74E-09 7.30E-01 B2 



7.19E-09 7.30E+00 B2 a 5.25E-08 

Benzo(b)fluoranthene 7.53E-09 7.30E-01 B2 

5.50E-09 



6.35E-09 

2.51E-09 7.30E+00 

D 

B2 

1.83E-08 

Indeno( 1,2,3-cd)pyrene 6.50E-09 7.30501 B2 


Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

2.49509 

2.90E+02 


2.29EM1 6.20E-11 

D 

1.42E-09 

Pathway Total 

3.38E-07 


Alummum 

3.42E-04 

Arsenic 1.23E-07 1.50E+00 A a 1.85E-07 

Beryllium 1.54E-08 4.30E+00 B2 a 6.61E-08 

Cobalt 

3.53E-07 

Lead 2.63E-07 B2 

Sodium 

9.62E-06 

Sulfate 

3.01E-05 

Thallium 2.07E-09 NA 

1,I.l -Trichloroethane 5.74E- 10 D 

1.1 -Dichloroethene 3.72E-10 6.00E-01 C a 2.23E-10 

Benzo(a)anthracene 6.74E-09 7.30E-01 B2 4.92E-09 

Benzo(a)pyrene 7.19E-09 7.30EM0 B2 a 5.25E-08 

Benzo(b)fluoranthene 7.53E-09 7.30E-01 B2 5.50E-09 

Page 4 of 64




Benzo(g,h,i)perylene 6.35E-09 D 

Dibenzo(a,h)anthracene 2.51E-09 7.30E+00 BZ 1.83E-08 

Indeno(l,2,3-cd)pyrene 6.50E-09 7.30E-01 BZ 4.74E-09 


Gross Alpha 

2.90E+02 

Gross Beta 


Uranium-238 2.29E+01 6.20E-11 1.42E-09 



Aluminum 

Arsenic 

6.57E-08 

1.50Et00 A a 9.85E-OX 

Barium 

Beryllium 

2.57E-09 4.30E+00 

NA 

B2 a 1.1 IE-08 

Cobalt 

Lead 

Manganese 

Sodium 

Sulfate 

Thallium 



7.49E-08 

7.42E- 11 

7.09E-08 

1.11E-07 

6.00E-01 

B2 

D 

NA 

D 

C a 6.64E-08 







1.35E-08 

7.77E-09 

8.14E-09 


3.92E-09 

7.30E-01 

7.30E+00 

7.30E-01 

7.30E+00 

7.30E-01 

BZ 

B2 

B2 

D 

B2 

B2 

a 

9.83E-09 

5.67E-08 

5.94E-09 

3.61E-08 

2.86E-09 

Phenanthrene 

Tnchloroethene 

2.23E-08 

1.03E-02 1.1OE-02 

D 

NA e 1.13E-04 


Gross Alpha 

Gross Beta 

Uranium-23 8 

1.59E-04 


1.40E-02 

6.20E-11 

B2 a 2.22E-06 

2.53E-09 

Pathway Total 

1.16E-04 



Arsenic 2.55E-12 5.00E+01 A b 1.28E- 10 

Beryllium 3.19E-13 8.40E+00 B2 b 2.68E-12 

Cobalt 

7.32E-12 

Lead 5.46E-12 B2 

Sodium 

2.00E-10 

Sulfate 

6.25E-10 

Thallium 4.30E- 14 NA 

I,], 1 -Trichloroethane 3.04E-09 D 

1, I -Dichloroethene 5.24E-09 1.20E+00 C b 6.29E-09 

Benzo(a)anthracene 1.40E-13 BZ 

Benzo(a)pyrene 1.49E-13 B2 

Benzo(b)fluoranthene 1.56E- 13 B2 


Dibenzo(a,h)anthracene 5.21E-I4 B2 

Indeno( I ,2,3-cd)pyrene 1.35E-13 B2 


Gross Alpha 

1.18E-02 

Gross Beta 

1.71E-02 

Uranium-238 9.28E-04 1.24E-08 1.15E-11 

Pathway Total 

6.44E-09 

S WMU Total 

1.61E-04 

WAG 1. SWMU 38c, RGW-Residential Dermal Contact with Water 




Gross Beta 


R’AG 1. SWMU 38c, RGW-Residential Ingestion of Water 

Page 5 of 64




Bmum 4.56E-03 NA 

Manganese 4.41E-02 D 


Gross Beta 

1.08E+05 

Pathway Total 

1.53E-05 

WAG 1, SWMU 38c, RGW-Residential Inhalation of Water 

Barium 

NA 

Manganese 

D 

Methylene Chloride 1.06E-04 B2 

Gross Beta 

Pathway Total 

WAG 1, SWMU 38c, RSO-Residential Dermal Contact with Soil 


Arsenic 

2.57E-05 3.66E+00 A 8 9.39E-05 

Beryllium 

2.39E-06 4.30E+02 B2 13, 1 1.03E-03 

Cobalt 


26 

Lead 

6.OSE-05 

B2 26 

Sodium 

Thallium 

2-Hexanone 

8.70E-04 

5.20E-07 

2.19E-07 

NA 52 

36 

Aroclor-1260 

3.49E-07 8.56E+00 B2 46 2.99E-06 

Benzo(a)anthracene 1.32E-06 2.35E+00 B2 2 3.10E-06 


1.14E-06 2.35E+01 B2 2 2.68E-05 

Benzo(b)fluoranthene 1.67E-06 2.35E+00 B2 2 3.92E-06 

Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

2.22E-06 

D 2 

Pathwav Total 

1.16E-03 

WAG 1, SWMC' 38c, RSO-Residenhal External Exposure to Soil 

Alummum 

b 

Arsenic 

A 

h 

Beryllium 

Cobalt 

B2 

h 

h 

Lead 

Sodium 

B2 h 

b 

Thallium 

NA b 

?-Hexanone 

Aroclor- 1260 




Phenanthrene 

B2 

B2 

B2 

B2 

D 

h 

h 

h 

b 

h 

h 

Gross Alpha 

Gross Beta 

Neptunium-237 


6.39E+02 

4.06E+01 4.62E-07 

h 

b 

b 1.88E-05 

Thorium-228 

3.41E+01 9.94E-07 

b 3.39E-05 

Uranium-235 

7.42E+00 2.65E-07 

b 1.97E-06 

Uranium-238 

1.31E+02 5.25E-08 

b 6.89E-06 

Pathwav Total 

6. ISE-05 

WAG 1, SWMU 38c, RSO-Residential Ingestion of Soil for Adult 

Aluminum 

1.60E-02 

Arsenic 1.03E-05 1.50E+00 A a 1.55E-05 

Beryllium 9.59E-07 4.30E+00 B2 a 4.12E-06 

Cobalt 

1.66E-05 

Lead 2.43E-05 B2 

Sodium 

3.50E-04 


2-Hexanone 

1.76E-08 

Aroclor- 1260 7.02E-08 7.70E+00 B2 5.40E-07 

Benzo( a)anthracene 2.64E-07 7.30E-01 B2 1.93E-07 

Page 6 of 64




Benzo(a)p yrene 2.29E-07 7.30E+00 B2 a 1.67E-06 


Phenanthrene 4.45E-07 D 

Gross Alpha 

2.43E+04 

Gross Beta 

3.35E+04 

Neptunium-237 2.13E+03 3.00E-10 6.39E-07 

Thorium-228 1.79E+03 2.31E-10 4.14E-07 

Uranium-235 3.89E+02 4.70E-11 1.83E-08 

Uranium-238 6.88E+03 6.20E-11 4.27E-07 

Pathway Total 

2.37E-05 

WAG 1, SWMU 38c, RSO-Residential Ingestion of Soil for Child 

Aluminum 

1.60E-02 

Arsenic 

1.03E-05 1.50E+00 A a 1 S5E-05 

Beryllium 

Cobalt 

Lead 

Sodium 

Thallium 

2-Hexanone 

Aroclor- 1260 


9.59E-07 

1.66E-05 

2.43E-05 

3.50E-04 

2.09E-07 

1.76E-08 

7.02E-08 

2.64E-07 


7.70E+00 

7.30E-01 

B2 

B2 

NA 

B2 

B2 

a 4.12E-06 

5.40E-07 

1.93E-07 



Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

2.29E-07 

3.35E-07 


2.43E+04 

3.35E+04 

2.13E+03 

1.79E+03 

3.89E+02 

6.88E+03 

7.30E+00 

7.30E-01 

3.00E-10 

2.31E-10 


6.20E-11 

B2 

B2 

D 

a 1.67E-06 

2.44E-07 

6.39E-07 


1.83E-08 


Arsenic 

Barium 

Beryllium 

Cobalt 

Lead 

Manganese 

Sodium 

Thallium 

2-Hexanone 

Aroclor-1260 





Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

Pathway Total 

5.50E-06 

1.60E-07 

6.91E-06 

7.47E-09 

1.78E-08 

5.27E-07 

2.48E-07 

3.62E-07 

1.50E-02 


7.70E+00 

7.30E-0 1 

7.30E+00 

7.30E-01 

7.50E-03 

3.00E-10 

2.31E-10 


6.20E-11 

A 

NA 

B2 

B2 

D 

NA 

B2 

B2 

B2 

B2 

B2 

D 

a 

a 

a 

a 

8.25E-06 

6.90E-07 

1.37E-07 

3.85E-07 

1.8lE-06 

2.64E-07 

1.13E-04 

1.78E-05 

2.666-05 

3.18E-08 

7.6 1 E-07 

WAG 1, SWMU 38c, RSO-Residential Inhalation of Soil 

Aluminum 

3.33E-07 

Arsenic 2.14E-IO 5.00E+01 A b 1.07E-08 

Beryllium 1.99E- 11 8.40E+00 B2 h 1.67E-IO 


Lead 5.04E- 10 B2 

Sodium 

7.25E-09 

Thallium 4.33E-12 NA 

2-Hexanone 

3.65E-13 

1.69E-04 

Page 7 of 64




Aroclor-1260 1.46E-12 B2 

Benzo(a)anthracene 5.48E- 12 B2 

Benzo(a)pyrene 4.75E-12 B2 

Benzo(b)fluoranthene 6.94E-12 B2 

Phenanthrene 9.24E- 12 D 

Gross Alpha 

9.86E-01 

Gross Beta 

1.36E+00 

Neptunium-237 8.65E-02 3.45E-08 2.98E-09 

'Ihorium-228 7.27E-02 9.68E-08 7.03E-09 

Uranium-235 1.58E-02 1.30E-08 2.05E-10 

Uranium-238 2.79E-01 1.24E-08 3.46E-09 

Pathway Total 

2.46E-08 

SWMU Total 

1.43E-03 

WAG 7, SWMU 130, RSO-Residential Demal Contact with Soil 

Lead 3.29E-07 B2 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead B2 b 

Gross Alpha 

1.35E+00 

b 

Gross Beta 

3.42E+00 

b 

Uranium-23 8 2.08E-01 5.25E-08 

b 1.09E-08 

Pathway Total 

1.09E-08 


Lead 1.323-07 B2 

Gross Alpha 

7.08E+01 

Gross Beta 

1.80E+02 

Uranium-238 1.09E+01 6.20E-11 

6.76E- 10 

Pathway Total 

6.76E-10 


Lead 1.32E-07 B2 

Gross Alpha 7.08EM 1 

Gross Beta 

1.80E+02 

Uranium-238 1.09E+01 6.20E-11 6.76E- 10 

Pathway Total 

6.76E-10 


Lead 3.76E-08 B2 

Gross Alpha 

Gross Beta 

Uranium-238 1.94E+O 1 6.20E- 11 1.21E-09 

Pathway Total 

1.21E-09 


Lead 2.74E- 12 B2 

Gross Alpha 

Gross Beta 

2.87E-03 

7.29E-03 

Uranium-238 

4.43E-04 1.24E-08 5.49B 12 

Pathway Total 

5.49E-12 

SWMU Total 

1.28E-08 

WAG 7, SWMU 131, RSO-Residenbal Dermal Contact with Soil 

Lead 6.28E-08 B2 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead B2 b 

Gross Alpha 2.76E-01 b 

Gross Beta 4 07E-01 b 

Uranium-238 2.56E-02 5.25E-08 b 1.35E-09 

Pathwav Total 

1.35E-09 

WAG 7, SWMU 131, RSO-Residenbal Ingestion of Soil for Adult 

Lead 2.52E-08 B2 

Page 8 of 64




Gross Alpha 

1.45E+01 

Gross Beta 

2.13E+01 

Uranium-238 1.34E+00 6.20E-11 8.34E-11 

Gross Alpha 1.45E+O 1 

Gross Beta 

2.13E+01 

Uranium-238 1.34E+00 6.20E-11 8.34E-11 

Pathway Total 


Lead 7.18E-09 B2 

Gross Alpha 

Gross Beta 

Uranium-238 2,40E+00 6.20E-11 1.49E-10 

8.34E-11 

Lead 

5.24E-13 

Gross Alpha 

5.88E-04 

Gross Beta 

8.66E-04 

Uranium-238 5.46E-05 1.24E-08 

6.77E-13 

Pathway Total 

S WMU Total 


Lead 5.14E-06 B2 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead BZ b 


Gross Beta 6.56E+00 b 

Uranium-238 4.44E-01 5.25E-08 b 2.33E-08 

Pathway Total 


Lead 2.07E-06 B2 

Gross Alpha 

1.97E+02 

Gross Beta 

3.44E+02 

Uranium-238 

2.33E+01 6.20E-11 1.44E-09 

Pathway Total 

WAG 7. SWMU 132, RSO-Residential Ingestion of Soil for Child 

Lead 2.07E-06 B2 

Gross Alpha 

1.97E+02 

Gross Beta 

3.44Ei-02 

Uranium-238 2.33E+01 6.20E-11 1.44E-09 

Pathwav Total 

U'AG 7. SWMU 132, RSO-Residential Ingestion of Vegetables 

Lead 5.88E-07 B2 

Gross Alpha 

Gross Beta 

Uranium-238 4.15E+01 6.20E-11 2.57E-09 

Pathway Total 

WAG 7, SWMU 132, RSO-Residenhal Inhalation of Soil 

Lead 4.29E-11 BZ 

Gross Alpha 

8.01E-03 

Gross Beta 

1.40E-02 

Uranium-238 9.45E-04 1.24E-08 1.17E- 11 

Pathway Total 

S WMU Total 

WAG 7. SWMU 133. RSO-Residential Dermal Contact with Soil 

Lead 5.97E-06 B2 26 

Acenaphthylene 4.3 1E-08 2 

Benzo( a)anthracene 3.23E-07 2.35E+00 B2 2 7.62E-07 

Page 9 of 64 

6.77E- 13 

2.33E-08 

1.44E-09 

1.44E-09 

2.57E-09 

1.17E-11 

1.58E-09 

2.73E-08




Benzo(a)p yrene 2.43E-07 2.35E+01 B2 2 5.73E-06 


Benzo( g,h,i)perylene 1.44E-07 D 2 

Benzo(k)fluoranthene 2.18E-07 2.35E-01 B2 2 5.14E-08 

Dibenzo(a,h)anthracene 1.78E-08 2.35E+01 B2 2 4.20E-07 


Phenanthrene 2.93E-07 D 2 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

7.86E-06 


Lead B2 b 



Benzo( a)p yrene 






Phenanthrene 

B2 

B2 

B2 

D 

B2 

B2 

B2 

D 

b 

b 

b 

b 

b 

b 

b 

b 

b 

Gross Alpha 

Gross Beta 

Uranium-238 

5.00E+00 

5.86Bi-00 

3.95E-01 5.25E-08 

b 

b 

b 2.07E-08 



Lead 2.40E-06 B2 



8.66E-09 

6.50E-08 7.30E-01 B2 



4.88E-08 7.30E+00 B2 a 3.57E-07 

Benzo(b)fluoranthene 5.266-08 7.30E-01 B2 

3.84E-08 



2.90E-08 


D 

B2 

3.20E-09 

Dibenzo(a,h)anthracene 3.58E-09 7.30E+00 B2 

2.62E-08 

Indene( 1,2,3-cd)pyrene 2.40E-08 7.30E-01 B2 

1.76E-08 

Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

5.88E-08 

2.62E+02 

3.07E+02 

2.07E+01 6.20E-11 

D 

1.28E-09 

Pathway Total 



Lead 2.40E-06 B2 



8.66E-09 

6.50E-08 7.30E-01 B2 



4.88E-08 7.30E+00 B2 a 3.57E-07 


3.84E-08 



2.90E-08 


D 

B2 

3.20E-09 


2.62E-08 

Indeno( 1,2,3-cd)pyrene 2.40E-08 7.30E-01 B2 

1.76E-08 

Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

5.88E-08 

2.62E+02 

3.07E+02 

2.07E+01 6.20E-11 

D 

1.28E-09 

Pathway Total 



Lead 6.82E-07 B2 


Benzo(a)anthracene 1.30E-07 7.30E-01 B2 9.47E-08 

Benzo(a)pyrene 5.28E-08 7.30E+00 B2 a 3.85E-07 

Benzo(b)fluoranthene 5.68E-08 7.30E-01 B2 4.15E-08 


D 

Benzo(k)fluoranthene 4.74E-08 7.306-02 B2 3.46E-09 

Page 10 of 64




Dibenzo(a,h)anthracene 7.06649 7.30E+00 B2 5.16E-08 

Indeno( 1,2,3-cd)pyrene 1.45E-08 7.30E-01 B2 1.06E-08 


Gross Alpha 

Gross Beta 

Uranium-238 3.69E+01 6.20E-11 2.29E-09 

Pathway Total 

5.90E-07 


Lead 4.97E-11 B2 

Acenaphth ylene 








Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

1.80E-13 

1.35E-12 

1.OlE-12 

1 a9E-12 

6.02E-13 

9.1 1E-13 

7.44E- 14 


1.22E-12 

1.06E-02 

1.25E-02 

8.41E-04 

1.24E-08 

B2 

B2 

B2 

D 

B2 

B2 

B2 

D 

1.04E- 1 1 

S WMU- Total 


Lead 9.57E-07 B2 26 

Benzo(a)anthracene 1.lOE-08 2.35E+00 B2 2 2.60E-08 

Benzo(a)pyrene 1.03E-08 2.35E+01 B2 2 2.43E-07 




Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead B2 b 


B2 

b 


B2 b 


B2 b 


D 

h 

Phenanthrene 

D b 

Gross Alpha 

3.83E+00 

b 

Gross Beta 


b 

Uranium-238 

2.94E-01 5.2SE-08 

b 1.54E-08 

Pathway Total 


Lead 3.85E-07 B2 





Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

1.09E-09 


D 

D 

2.22E-09 7.30E-01 B2 1.62E-09 

2.07E-09 7.30E+00 B2 a 1.51 E-08 

3.09E-09 7.30E-01 B2 2.26E-09 

2.01E+02 

2.27E+02 

1.54E+01 6.20E-11 9.56E-10 

Pathway Total 


Lead 3.85E-07 B2 




2.26E-09 



1.04E-11 

3.05E-07 

1.54E-08 

2.00E-08 

8.96E-06 

Page 11 of 64




Gross Beta 

2.27E+02 

Uranium-238 1.54E+01 6.20E-11 9.56E-10 

Pathway Total 

2.00E-08 


Lead 1.09E-07 B2 

Benzo( a)anthracene 4.43E-09 7.30E-01 B2 3.23E-09 




D 


Gross Alpha 

Gross Beta 

Uranium-23 8 2.75E+01 6.20E-11 1.70E-09 

Pathway Total 2.378-08 


Lead 7.98E- 12 B2 

Benzo(a)anthracene 4.60E-14 

B2 



B2 

Benzo(b)fluoranthene 6.41E-14 

B2 

Benzo(g,h,i)perylene 2.27E-14 

D 

Phenanthrene 

1.03E- 13 

D 

Gross Alpha 

Gross Beta 

8.16E-03 

9.22E-03 

Uranium-238 

6.26E-04 1.24E-08 

7.76E-12 

Pathwav Total 

7.76E- 12 

S WMU Total 

3.64E-07 

WAG 7. SWMU 8b. RGW-Residential Dermal Contact with Water 

Aluminum 

Beryllium 

2.43E-06 

Cobalt 

Iron 

Manganese 

1.15E-03 

Nickel 3.01E-05 

Silica 

Silicon 

Sulfate 

Sulfide 

1,1 -Dichloroethene 4.07E-06 


Phenanthrene 


Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-234 

Uranium-235 

Uranium-238 

7.51E-06 

1.26E-05 

3.85E-06 


6.00E-01 

7.33E-02 

4,5 

B2 13, 1 

26 

26 

D 38 

NA 44 

C 31 

NA 

D 2 

NA 57 

1.05E-03 

2.44E-06 

2.83E-07 

Pathway Total 

WAG 7, SWMU 8b, RGW-Residential Ingestion of Water 

Aluminum 

7.56E-01 


Cobalt 

1.34E-02 

Iron 1.93Ei-O 1 

Manganese 3.9 1E-01 D 

Nickel 1.OZE-02 NA 

Silica 

7.86E+00 

Silicon 

1.88E-01 

Sulfate 

1.25E+01 

Sulfide 

3.76E-02 

1.1-Dichloroethene 1.52E-04 6.00E-01 C a 9.12E-05 

I ,2-Dichloroethene 2.39E-03 NA 


Trichloroethene 8.34E-05 1.1OE-02 NA e 9.17E-07 

Page 12 of 64 

1.05E-03




Gross Abha 


Gross Beta 

2.23E+06 

Neptunium-237 6.64E+04 3.00E-10 

1.99E-05 

Thorium-228 2.18E+04 2.31E-10 

5.05E-06 

Uranium-234 3.72E+05 4.44E-11 

1.65E-05 

Uranium-23 5 3.12E+04 4.70E-11 

1.47E-06 

Uranium-238 7.83E+05 6.20E-11 


Beryllium 

Cobalt 

Iron 

Manganese 

Nickel 

Silica 

Silicon 

Sulfate 

Sulfide 

1, I-Dichloroethene 7.9 1E-06 


Phenanthrene 



Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-234 

Uranium-235 

Uranium-238 

Pathway Total 

8.40E+00 

1.20E+00 

6.00E-03 

3.45E-08 

9.68E-08 

1.40E-08 

1.30E-08 

1.24E-08 

B2 

D 

NA 

h 

C b 9.49E-06 

NA 

D 

NA e 2.61E-08 

WAG 7, SWMU 8h, RSO-Residential Dermal Contact with Soil 

Aluminum 4.76E-02 4,5 

Arsenic 1.77E-05 3.66E+00 A 8 6.49E-05 

Beryllium 3.05E-06 4.30E+02 B2 13, 1 1.31E-03 

Cobalt 3.39E-05 26 

Lead 4.37E-05 B2 26 


2.50E-04 

Sodium 




Aroclor- 1260 2.51E-07 8.56E+00 B2 46 2.14E-06 




Dibenzofuran 

2.16E-06 

Indeno(l,2,3-cd)pyrene 2.02E-06 2.35E+00 B2 2 4.75E-06 

Naphthalene 2.21E-06 D 43 


Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Thorium-230 

Uranium235 

Uranium-238 

Pathwav Total 

WAG 7. SWMU 8b. RSO-Residential External Exposure to Soil 

Aluminum 

h 

Arsenic A h 


Cobalt 

h 

Lead B2 h 


h 

9.52E-06 

1.45E-03 

Page 13 of 64




Sodium 

b 

Thallium NA b 


b 

Aroclor- 1260 B2 b 


Benzo(a)pyrene B2 b 

Benzo(b)fluoranthene B2 b 

Dibenzofuran 

b 


Naphthalene D b 

Phenanthrene D b 


Gross Beta 5.41 E+02 b 

Neptunium-237 6.14E+01 4.62E-07 b 2.84E-05 

Thorium-228 3.44E+01 9.94E-07 b 3.42E-05 

Thorium-230 1.60E+04 4.40E-11 b 7.02E-07 

Uranium-235 5.92E+00 2.65E-07 h 1.57E-06 

Uranium-238 1.16E+02 5.25E-08 b 6.11E-06 

Pathway Total 

7.09E-05 

WAG 7, SWMU 8b, RSO-Residential Ingestion of Soil for Adult 

Aluminum 

1.91E-02 

Arsenic 7.13E-06 1.50E+00 A a 1.07E-05 


Cobalt 

1.36E-05 

Lead 1.75E-05 B2 


1.00E-04 

Sodium 

1.91E-04 



Aroclor-1260 5.04E-08 7.70E+00 B2 

3.88E-07 


2.22E-07 

Benzo(a)p yrene 4.42E-07 7.30E+00 B2 a 3.23E-06 


3.65E-07 

Dibenzofuran 


Indene( 1,2,3-cd)pyrene 4.05E-07 7.30E-0 1 B2 

2.96E-07 

Naphthalene 4.43E-07 D 


Gross Alpha 

1.69E+04 

Gross Beta 

2.84E+04 

Neptunium-237 3.22E+03 3.00E-10 9.66E-07 

Thorium-228 1.80E+03 2.31E-10 4.17E-07 

Thorium-230 8.37E+05 3.75E-11 3.14E-05 

Uranium-23 5 3.11E+02 4.70E-11 1.46E-08 

Uranium-238 6.10EM3 6.20E-I 1 3.78E-07 

Pathway Total 

5.36E-05 

WAG 7. SWMU 8b. RSO-Residential Ineestion of Soil for Child 

Arsenic 7.13E-06 1.50E+00 A a 1.07E-05 


Cobalt 

1.36E-05 

Lead 1.75E-05 B2 


1.00E-04 

Sodium 

1.91E-04 



Aroclor-1260 5.04E-08 7.70E+00 B2 3.88E-07 


Benzo(a)pyrene 4.42E-07 7.30E+00 B2 a 3.23E-06 


Dibenzofuran 


Indeno( 1.2.3-cd)pyrene 4.05E-07 7.30E-01 B2 

2.96E-07 

Naphthalene 4.43E-07 D 


Gross Alpha 

1.69E+04 

Page 14 of 64




Gross Beta 

2.84E+04 

Neptunium-237 3.22E+03 3.00E-10 

9.66E-07 

Thorium-228 1.80E+03 2.3 1E- 10 


Thorium-230 8.37E+05 3.75E-11 

3.14E-05 

Uranium-235 3.11E+02 4.70E-11 

1.46E-08 

Uranium-238 6.10E+03 6.20E-11 

3.78E-07 

Pathway Total 

5.36E-05 

WAG 7, SWMU 8b, RSO-Residential Ingestion of Vegetables 

Aluminum 

Arsenic 

3.80E-06 1.50E+00 

Beryllium 

4.59E-03 4.30E+00 

Cobalt 

Iron 

Lead 

Manganese 

Nickel 


Silica 

Silicon 

Sodium 

Sulfate 

Sulfide 

Thallium 



9.74E-09 

9.79E-04 6.00E-01 



Aroclor-1260 

1.28E-08 7.70E+00 

Benzo(a)anthracene 6.07E-07 7.30E-01 



Benzo(b)fluoranthene 5.41E-07 7.30E-01 

Dibenzofuran 

Indeno(l,2,3-cd)pyrene 2.44E-07 7.30E-01 

Naphthalene 

Phenanthrene 


2.07E-05 

9.1 OE-05 


Gross Alpha 

Gross Beta 

Neptunium-237 

4.61E+05 3.00E-10 

Thorium-228 

2.35E+05 2.31E-10 

Thorium-230 

2,92E+O5 3.75E-11 

Uranium-234 

2.06E+06 4.44E-11 

Uranium-235 

1.74E+O5 4.70E-11 

Uranium-238 

Pathwav Total 


A a 5.71E-06 

B2 a 1.98E-02 

B2 

D 

NA 

NA 

C 

NA 

B2 

B2 

B2 

B2 

B2 

D 

D 

NA 

a 

a 

e 

5.88E-04 

9.85E-08 


3.49E-06 

3.95E-07 

1.78E-07 

5.49E-06 

1.38E-04 

5.43E-05 

1.09E-05 

9.16E-05 

8.16E-06 

2.70E-04 

WAG 7, SWMU 8b, RSO-Residential Inhalation of Soil 

Aluminum 

3.97E-07 

Arsenic 1.48E-10 5.00E+01 A b 7.40E-09 

Beryllium 2.54E-11 8.40E+00 B2 b 2.14E- 10 

Cohalt 2.82E- 10 

Lead 3.64E- 10 B2 


2.08E-09 

Sodium 

3.97E-09 


2-Methvlnaphthalene 4.38E- 12 

Aroclor- 1260 1.04E- 12 B2 

Benzo(a)anthracene 6.3 1E- 12 B2 




Indeno( 1,2,3-cd)pyrene 8.40E-12 B2 

Naphthalene 9.20E-12 D 


Gross Alpha 

6.87E-01 

Gross Beta 

1,15E+00 

Page 15 of 64 

2.09E-02

~~ 




Neptunium-237 1.31E-01 3.45E-08 4.51E-09 

Thorium-228 7.32E-02 9.68E-08 7.09E-09 

Thorium-230 3.40E+01 1.72E-08 5.85E-07 

Uranium-235 1.26E-02 1.30E-08 1.64E- 10 

Uranium-238 2.48E-01 1.24E-08 3.076-09 

Pathway Total 

6.07E-07 

Arsenic 1.93E-06 3.66E+00 A 8 7.07E-06 


Cobalt 5.56E-06 26 

Lead 3.90E-06 B2 26 

Sodium 


Gross Alpha 

Gross Beta 

Uranium-238 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Gross Alpha 

1.25E+01 

Gross Beta 

2.56E+01 

Uranium-238 

1.74E+00 5.25E-08 

Pathway Total 


Aluminum 

Cadmium 

Cobalt 

Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 4.44E- 11 

Uranium-238 

6.20E-11 

Pathway Total 

A 

B2 

B2 

B1 

B2 

b 

b 

b 

b 

b 

b 

b 

b 

9.13E-08 


Aluminum 

9.67E-04 

Arsenic 4.48E-07 1.50E+00 A a 6.72E-07 

Beryllium 6.53E-08 4.30E+00 BZ a 2.81E-07 

Cobalt 

1.29E-06 

Lead 9.04E-07 BZ 

Sodium 

1.06E-05 

Gross Alpha 

6.56E+02 

Gross Beta 

1.34E+03 

Uranium-238 9.13E+01 6.20E-11 5.66E-09 

Pathway Total 


Aluminum 

9.67E-04 

Arsenic 

4.48E-07 1.50E+00 A a 6.72E-07 

Beqllium 

6.53E-08 4.30E+00 BZ a 2.81E-07 

Cobalt 

1.29E-06 

Lead 

9.04E-07 

BZ 

Sodium 

1.06E-05 

Gross Alpha 

6.56E+02 

Gross Beta 

1.34E+03 

Uranium-238 

9.13E+01 6.20E-11 5.66E-09 

Pathway Total 

WAG 1. SWMU lOOa CSE-Recreational Inhalation of Sediment 

Aluminum 

2.01E-08 

9.13E-08 

9.59E-07 

9.59E-07 

Page 16 of 64




Arsenic 9.30E-12 5.OOE+01 A b 4.65E-10 


Cobalt 

2.68E-11 

Lead 1.88E-11 B2 

Sodium 

2.20E-10 

Gross Alpha 

2.66E-02 

Gross Beta 

5.46E-02 

Uranium-238 3.71E-03 1.24E-08 4.59E-11 

Pathway Total 

5.22E-10 

WAG 1, SWMU IOOa, CSW-Recreational Dermal Contact with Water 

Aluminum 4,5 

Cadmium 5.04E-07 B1 16, 1 

Cobalt 26 

Lead 5.91 E-07 B2 26 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-238 

Pathway Total 

WAG 1, SWMU 100% RGW-Recreational Ingestion ofFish 

Aluminum 

Cadmium 

B1 

Cobalt 

Lead 

B2 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-238 


6.20E-11 

Pathway Total 

S WMU Total 

1.29E-04 

WAG 1, SWMU 100b, CSE-Recreational Demal Contact with Sediment 

Alummum 3.25E-03 4s 

Arsenic 1.76E-06 3.66E+00 A 8 6.45E-06 


Cobalt 2.81E-06 26 

Lead 3.42E-06 B2 26 

Sodium 


Gross Alpha 

Gross Beta 

Uranium-23 5 

Uranium-238 

Pathway Total 

9.97E-05 

WAG 1, S WMU 1 OOb, CSE-Recreational External Exposure to Sediment 

Aluminum 

b 

Arsenic 

A b 

Beryllium 

Cobalt 

B2 b 

b 

Lead 

Sodium 

B2 b 

b 

Gross Alpha 

1.96E+01 

b 

Gross Beta 

3.15E+OI 

b 

Uranium-235 

1.85E+00 2.65E-07 b 4.90E-07 

Uranium-238 

5.59E+00 5.25E-08 b 2.93E-07 

Pathway Total 

7.83E-07 

WAG 1. SWMU 100b, CSE-Recreational Ingestion of Deer 

Aluminum 

Arsenic 1.50E+00 A a 

Lead 

B2 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 4.44E- 11 

Page 17 of 64


AN- 



Uranium-235 


Uranium-238 

6.20E-11 

Pathway Total 

WAG 1, SWMU 100h, CSE-Recreational Ingestion of Sediment for Adult 

Aluminum 

7.53E-04 

Arsenic 

4.09E-07 1.50E+00 A a 6.13E-07 

Beryllium 


Cobalt 

Lead 

6.53E-07 

7.94E-07 

B2 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-235 

9.91E-06 

1.03E+03 

1.65E+03 

9.70E+01 4.70E-11 4.56E-09 

Uranium-238 

2.93E+02 6.20E-11 1.82E-08 

Pathwav Total 

8.52E-07 

WAG 1, SWMU IOOb, CSE-Recreational Ingestion of Sediment for Child 

Aluminum 

7.53E-04 



Cobalt 

6.53E-07 

Lead 7.94E-07 B2 

Sodih 

9.91E-06 

Gross Alpha 

1.03E+03 

Gross Beta 

1.65E+03 

Uranium-23 5 9.70E+01 4.70E-11 4.56E-09 

Uranium-238 2.93E+02 6.20E-11 1.82E-08 

Pathway Total 

8.52E-07 

WAG 1, SWMU IOOb, CSE-Recreational Inhalation of Sediment 

Aluminum 

1.56E-08 

Arsenic 

8.48E-12 5.OOE+01 A b 4.24E-10 

Beryllium 

1.04E-12 8.40E+00 B2 h 8.77E-12 

Cobalt 

Lead 

1.35E-11 

1.6SE-11 

B2 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-235 

2.06E-10 


6.71E-02 

3.94E-03 1.30E-08 5.12E-I1 

Uranium-238 

1.19E-02 1.24E-08 1.48E- 10 

Pathway Total 6 32E-10 

WAG 1, SWMU 100b, CSW-Recreahonal Dermal Contact with Water 

Alummum 

4s 

Arsenic 5 31E-08 3 66E+00 A 8 194E-07 

Lead 103E-06 B2 26 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-235 

Uranium-238 

Pathway Total 

1.94E-07 

Q'AG 1, SWMU 100b. RGW-Recreahonal Ingeshon of Fish 

Alummum 

Arsenic 

1.50E+00 A a 

Lead 

B2 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-235 

Uranium-238 

Pathway Total 



6.20E-11 

Page 18 of 64




Arsenic 3.12E-11 1.50E+00 A a 4.68E-11 

Beryllium 9.34E-13 4.30E+00 B2 a 4.02E- 12 

Cobalt 

Lead 1. ME-1 1 B2 

Sodium 





Endrin Ketone 

Naphthalene 4.52E- 13 D 

Phenanthrene 4.71E- 12 D 

Gross Alpha 

Gross Beta 

Neptunium-237 4.74E-08 3.00E-10 1.42E- 17 

Thorium-228 3.63E-03 2.31E-10 8.39E-13 

Uranium-238 4.52E-08 6.20E-11 2.80E-18 

Pathway Total 

5.16E-11 

S WMU Total 

5.16E-11 


Aluminum 

Arsenic 

7.88E-13 1.50E+00 A a 1.18E-12 

Beryllium 


Cobalt 

Lead 

Sodium 

Sulfate 

Thallium 



3.00E- 13 

2.07E- 13 

8.04E-16 

2.73E-16 6.00E-01 

B2 

NA 

D 

C a 1.64E- 16 


2.59E-13 


8.24E-13 7.30E+00 B2 a 6.02E-12 


6.30E-13 


Dibenzo(a,h)anthracene 1.34E-13 7.30E+00 

D 

B2 

9.79E- 13 


1.24E- 12 

Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

2.71E- 14 

7.05E-10 6.20E-11 

D 


Pathway Total 

1.04E-11 

SWMU Total 1.04E- 11 

WAG I, SWMU 38% CSE-Recreational Dermal Contact with Sediment 



Cobalt 3.42E-06 26 

Lead 3.12E-06 B2 26 

Sodium 

1.41E-05 

Vanadium 3.29E-05 NA 58, 5 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

2.33E-04 

WAG 1, SWMU 38a, CSE-Recreational External Exposure to Sediment 

Aluminum 

b 

Beryllium 

Cobalt 

B2 b 

b 

Lead 

Sodium 

B2 b 

b 

Vanadium 

NA b 

Phenanthrene 

D b 

Gross Alpha 

1.14Ei-01 

b 

Gross Beta 

1.49E+O 1 

b


Y '1'6 '1'0 I'AL I'U'IAL 



Uranium-238 3.58E+00 5.25E-08 

b 1.88E-07 

Pathway Total 

1.88E-07 



Lead 

B2 

Sodium 

Chloroform 6.10E-03 B2 a 

bis(2-Ethylhexy1)phthalate 1.40E-02 B2 a 

Gross Alpha 

Gross Beta 

Uranium-238 

6.20E-11 

Pathway Total 


Aluminum 

3.62E-04 


Cobalt 

7.94E-07 

Lead 7.23E-07 B2 

Sodium 

3.26E-06 

Vanadium 7.64E-06 NA 


Gross Alpha 

5.99E+02 

Gross Beta 

7.83E+02 

Uranium-238 1.88E+02 6.20E-11 1.16E-08 

Pathway Total 

5.53E-07 


Aluminum 

3.62E-04 

Beryllium 1.26E-07 4.30E+00 B2 a 5.41 E-07 

Cobalt 

7.94E-07 

Lead 7.23E-07 B2 

Sodium 

3.26E-06 



Gross Alpha 

5.99E+02 

Gross Beta 

7.83E+02 

Uranium-238 1.88E+02 6.20E-11 1.16E-08 

Pathway Total 

5.53E-07 

WAG 1, SWMU 38% CSE-Recreational Inhalation of Sediment 

Aluminum 

7.50E-09 

Beryllium 

2.6lE-12 8.40E+00 B2 h 2.19E-11 

Cobalt 

Lead 

1.65E-11 

1.50E-11 

B2 

Sodium 

Vanadium 

6.77E-11 

1.59E- 10 

NA 

Phenanthrene 

1.63E- 13 

D 

Gross Alpha 

Gross Beta 

Uranium-238 

2.43E-02 

3.18E-02 

7.61E-03 1.24E-08 9.44E-11 

~ ~. 

Pathway Total 

1.16E-10 

WAG 1. SWMU 38% CSW-Recreational Dermal Contact with Water 

Arsenic 4.17E-08 3.66E+00 A 8 1.53E-07 

Lead 2.16E-07 B2 26 

Sodium 

Chloroform 1.35E-06 3.05E-02 B2 24 4.13E-08 

bis(2-Ethylhexy1)phthalate 1.76E-06 7.37E-02 B2 I5 1.30E-07 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

3.24E-07 

K'AG 1, SWMU 38% RGW-Recreational Ingestion of Fish 


Lead 

B2 

Sodium 

Chloroform 6.10E-03 B2 a 

bis(2-Ethvlhexyl)phth~atr 1.40E-02 B2 a 

Page 20 of 64




Gross Alpha 

Gross Beta 

Uranium-238 

6.20E-11 

Pathway Total 

SWN-Total 

2.34E-04 

WAG 1, SWMU 38b, CSE-Recreational Dermal Contact with Sediment 

Aluminum 3.0 1E-03 4s 



Cobalt 2.27E-06 26 

Lead 6.17E-06 B2 26 

Sodium 

2.39E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

7.30E-05 

WAG 1, SWMU 38b, CSE-Recreational External Exposure to Sediment 

Aluminum 

b 

Arsenic 

A b 

Beryllium 

Cobalt 

B2 b 

b 

Lead 

Sodium 

B2 b 

b 

Gross Alpha 

1.36E+O 1 

b 

Gross Beta 

2.88E+01 

b 

Uranium-238 

2.84E+00 5.25E-08 b 1.49E-07 

Pathway Total 

1.49E-07 


Aluminum 

Sodium 

Gross Alpha 

Gross Beta 

Neptunium-237 

Plutonium-238 

Uranium-234 

Uranium-238 

3.00E- 10 

2.95E-10 

4.44E- 1 1 

6.20E-11 

Pathway Total 

WAG 1, SWMU 38b, CSE-Recreational Ingestion of Sediment for Adult 

Aluminum 

6.98E-04 



Cobalt 

5.27E-07 

Lead 1.43E-06 B2 

Sodium 

5.54E-06 

Gross Alpha 

7.12E+02 

Gross Beta 1.51E+03 

Uranium-238 1.49E+02 6.20E- 11 9.22E-09 

Pathway Total 

WAG 1, SWMU 38b, CSE-Recreational Ingestion of Sediment for Child 

Aluminum 

6.98E-04 



Cobalt 

5.27E-07 

Lead 1.43E-06 B2 

Sodium 

5.54E-06 

Gross Alpha 

7.12E+02 

Gross Beta 1.51E+03 

Uranium-238 1.49E+02 6.20E-11 9.22E-09 

Pathway Total 

WAG 1. SWMU 38b, CSE-Recreational Inhalation of Sediment 

Aluminum 

1.45E-08 

Arsenic 

5.87E-12 S.OOE+O 1 A b 2.94E-10 

Beryllium 

7.67E-13 8.40E+00 B2 b 6.44E- 12 

5.93E-07 

5.93E-07 

Page 21 of64


A N m T o r - 



Lead 2.97E-11 B2 


Gross Alpha 

2.89E-02 

Gross Beta 

6.13E-02 

Uranium-238 6.04E-03 1.24E-08 7.49E- 11 

Pathway Total 

3.75E-10 


Aluminum 

4s 

Sodium 

Gross Alpha 

Gross Beta 

Neptunium-237 

Plutonium-238 

Uranium-234 

Uranium-238 

Pathway Total 

WAG 1. SWMU 38b. RGW-Recreational Ineestion of Fish 

Aluminum 

Sodium 

Gross Alpha 

Gross Beta 

Neptunium-237 

Plutonium-238 

Uranium-234 

Uranium-23 8 

3.00E- 10 

2.95E-10 


6.20E-11 

Pathway Total 

S WMU Total 

7.37E-05 

WAG 1, SWMU 38c, CSE-Recreational Ingestion of Deer 

Alummum 

Arsenic 

Beyllium 

Cobalt 

Lead 

Sodium 

Thallium 

2-Hexanone 

Aroclor-1260 




Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

Pathway Total 

SWhKJ Total 

1.2 1E- 10 

3.79E- 12 

5.09E-11 

3.84E-11 

1.28E-10 

2.56E-11 


7.06E- 1 1 

9.06E-12 

1.54E-05 

1.08E-02 

6.28E-09 

2.07E-06 

1.50E+00 


7.70E+00 

7.30E-01 

7.30E+00 

7.3OE-01 

3.00E- IO 

2.3 1E- 10 


6.20E-11 

A 

B2 

B2 

NA 

B2 

B2 

B2 

B2 

D 

R’AG 7. SWMU 130, CSE-Recreational Ingestion of Deer 

Lead 1.51E- 13 B2 

Gross Alpha 

Gross Beta 

Uranium-238 4.25E-10 6.20E-11 

Pathway Total 

S WMU Total 

R’AG 7, SWMU 131, CSE-Recreabonal Ingestion of Deer 

Lead 2.87E- 14 B2 

Gross Alpha 

Gross Beta 

a 

a 

a 

1.82E-10 

1.63E-11 

9.88E- 10 

1.87E-11 

3.53E-10 

5.15E- 11 


2.49E-12 

2.95E-19 

1.28E-16 

2.63E-20 

Uranium-238 5.96E-11 6.20E-11 3.69E-21 

Pathway Total 

SWMU Total 

WAG 7. SR’MU 132. CSE-Recreabonal Ingestion of Deer 

Page 22 of 64 

1.61E-09 

2.63E-20 

3.69E-21 

1.61E-09 

2.63E-20 

3.69E-21





Gross Alpha 

Gross Beta 

Uranium-238 1.29E-09 6.20E- 11 7.98E-20 

Pathway Total 

7.98E-20 

S WMU Total 

7.98E-20 




Benzo(a)anthracene 3.42E-12 7.30E-01 

2.49E- 12 


5.60E-12 7.30E+00 

a 4.09E-11 

Benzo(b)fluoranthene 6.03E-12 7.30E-01 



Benzo(k)fluoranthene 5.03E-12 7.30E-02 

3.67E- 13 

Dibenzo(a,h)anthracene 1.91E-13 7.30E+00 

1.40E-12 

Indeno( 1,2,3-cd)pyrene 6.29E-12 7.30E-01 


Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

6.50E-13 

1.21E-09 6.20E-11 

7.51E-20 

Pathway Total 

5.41E-11 

SWMU-Total 

5.41E-11 




Benzo(a)pyrene 2.38E-13 7.30E+00 B2 a 1.73E- 12 



D 


Gross Alpha 

Gross Beta 

Uranium-238 6.71510 6.20E-11 4.16E-20 

Pathway Total 2.08E- 12 

SWMU Total 2.08E- 12 



Arsenic 2.88E-06 3.66E+00 A 8 1.06E-05 

Beryllium 3.04E-07 4.30E+02 BZ 13, 1 1.31E-04 

Cobalt 5.16E-06 26 

Lead 3.87E-06 BZ 26 

Sodium 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

1.41E-04 

WAG 7. SWMU 8a CSE-Recreational External Emosure to Sediment 

Aluminum 

b 

Arsenic 

A b 

Beryllium 

Cobalt 

B2 b 

b 

Lead 

Sodium 

B2 b 

b 

Gross Alpha 

9.64E+00 

b 

Gross Beta 

1.59E+01 

b 

Uranium-238 

1.16E+00 5.25E-08 b 6.06E-08 

Pathway Total 

6.06E-08 


Aluminurn 

Antimony 

NA 

Arsenic 2.01E-09 1.50E+00 A a 3.0 1E-09 

Barium 

NA 

Beryllium 4.54E-08 4.30E+00 BZ a 1.95E-07 

Cadmium 

B1 

Cobalt 

Page 23 of 64




Iron 

Lead 

Manganese 

Nickel 


Ruthenium 

Silicon 

Sodium 

Sulfate 

Tantalum 

Thallium 

Tungsten 

Vanadium 

Zirconium 

2.50E-06 

3.03E-05 

B2 

D 

NA 

NA 

NA 




Aroclor- 1260 




Dibenzofuran 



Naphthalene 

Phenanthrene 




Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Thorium-230 

Uranium-234 

Uranium-235 

Uranium-238 

8.28E-12 

2.20E-09 

7.04E-10 

2.23E-09 

2.52E-09 


5.69E-11 

1.96E-10 

1.14E-I1 

1.86E- 13 

1.02E-03 

2.80E-01 

9.64E-03 

3.75E+00 

9.55E-08 

2.71E-04 

6.00E-01 

7.70E+00 

7.30E-01 

7.30E+00 

7.30E-01 

7.30E-01 

7.50E-03 

1.1 OE-02 

1.40E-02 

3.00E- 10 

2.3 1E-10 

3.75E-11 



6.20E-11 

C 

NA 

B2 

B2 

B2 

B2 

B2 

B2 

D 

D 

NA 

B2 

D 

a 

a 

a 

e 

a 


1.70E-08 

5.14E- 10 

1.63E-08 

1.84E-09 

3.40E-09 

1.26E-13 

2.6 1 E- 15 

3.05E-13 

6.48E-11 

3.62E- 13 

1.67E- 10 


1.68E-14 

Pathwav Total 

2.37E-07 


Aluminum 

3.16E-04 

Arsenic 

6.69E-07 1.50E+00 A a 1.00E-06 

Beryllium 


Cobalt 

Lead 

1.20E-06 

8.97E-07 

B2 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-238 

1.04E-05 

5.06E+02 

8.34E+02 

6.06E+01 6.20E-11 3.76E-09 



Aluminum 

3.16E-04 

Arsenic 6.69E-07 1.50E+00 A a 1.00E-06 


Cobalt 

1.20E-06 

Lead 8.97E-07 B2 

Sodium 

1.04E-05 

Gross Alpha 

5.06E+02 

Gross Beta 

8.34E+02 

Uranium-238 6.06E+01 6.20E-11 3.76E-09 


WAG 7. SWMU 8a CSE-Recreational Inhalation of Sediment 

Aluminum 

6.55E-09 

Arsenic 1.39E-11 5.OOE+01 A h 6.94E- 10 


Page 24 of 64




Cobalt 

2.48E-11 

Lead 1.86E-11 B2 

Sodium 

2.17E-10 

Gross Alpha 

2.05E-02 

Gross Beta 

3.38E-02 

Uranium-238 2.46E-03 1.24E-08 3.05E-11 



Aluminum 

4s 

Antimony 

Arsenic 

Barium 

Beryllium 

Cadmium 

Cobalt 

Iron 

Lead 

Manganese 

Nickel 

Ruthenium 

Silicon 

Sodium 

Sulfate 

Tantalum 

Thallium 

Tungsten 

Vanadium 

Zirconium 






7.09E-07 


1.60E-06 

1.19E-07 

9.1 IE-08 

1.32E-05 

6.65E-04 

1.89E-06 

2.05E-05 

9.11E-08 

1.12E-07 


6.26E-08 

8.826-08 

3.66E+00 


6.00E-01 

7.89E-03 

7.33E-02 

7.37E-02 

NA 

A 

NA 

B2 

B1 

B2 

D 

NA 

NA 

NA 

C 

NA 

B2 

NA 

B2 

7 

8 

9 

13, 1 

16, 1 

26 

26 

26 

38 

44 

52 

58, 5 

12 

31 

41 

57 

15 

1.56E-07 

5.10E-05 

5.46E-08 

3.81E-09 


6.50E-09 


Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-234 

Uranium-238 

8.15E-07 

D 83 

Pathway Total 

5.12E-OS 


Aluminum 

Antimony 

9.75E-05 

Arsenic 

Barium 

Bevllium 

Cadmium 

2.75E-05 

Cobalt 

Iron 

Lead 

5.9 IE-05 

Manganese 

3.23E-01 

Nickel 

Ruthenium 

Silicon 

Sodium 

Sulfate 

Tantalum 

Thallium 

7.25E-04 

Tungsten 

Vanadium 

2.92E-04 

Zirconium 


NA 

6.87E-06 1.50E+00 A a 1.03E-05 

NA 

4.30E+00 B2 a 

B1 

B2 

D 

NA 

NA 

NA 

6.00E-01 C a 

Page 25 of 64




Methylene Chloride 9.98E-07 7.50E-03 B2 a 7.486-09 

Trichloroethene 1.1OE-02 NA e 

bis(2-Ethylhexy1)phthalate 1.40E-02 B2 a 


D 

Gross Alpha 

Gross Beta 

Neptunium-237 

3.00E-IO 

Thorium-228 

2.31E-10 

Uranium-234 


Uranium-238 

6.20E-11 

Pathway Total 

1.03E-05 

SWMU Total 

2.05E-04 

WAG 1, SWMU lOOa ESE-Excavation Dermal Contact with Sediment 


Arsenic 1.91E-OS 3.66E+00 A 8 7.00E-08 


Cobalt 5.5OE-08 26 

Lead 3.86E-08 B2 26 

Sodium 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

1.27E-06 

WAG 1. SWMU lOOa ESE-Excavation External ExDosure to Sediment 

Aluminum 

Arsenic 

A b 

Beryllium 

Cobalt 

B2 b 

b 

Lead 

Sodium 

B2 b 

b 

Gross Alpha 

1.33E-01 

b 

Gross Beta 

2.73E-01 

b 

Uranium-238 

1.86E-02 5.25E-08 b 9.74E- 10 



Aluminum 

6.60E-05 

Arsenic 3.06E-08 1.50E+00 A a 4.59E-OX 

Beryllium 4.46E-09 4.30E+00 B2 a 1.92E-08 

Cobalt 

8.80E-08 

Lead 6.17E-08 B2 

Sodium 

7.25E-07 

Gross Alpha 

8.76EM1 

Gross Beta 

1.80EM2 

Uranium-238 1.22EM1 6.20E-11 7.56E- 10 

Pathway Total 

6.58E-08 


Aluminum 

1.00E-09 

Arsenic 

4.64E-13 5.OOE+01 A b 2.32E-11 

Beryllium 

6.76E-14 8.40E+00 B2 b 5.68E-13 

Cobalt 

Lead 

1.34E-12 

9.36E- 13 

B2 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-238 

1.1OE- 11 

1.33E-03 

2.72E-03 

1.85E-04 1.24E-08 2.29E-12 

Pathway Total 

2.61E-11 

Arsenic 1.74E-08 3.66EM0 A 8 6.38E-08 


Cobalt 2.78E-08 26 

Lead 3.39E-08 B2 26 

Sodium 


Page 26 of 64




Gross Alpha 

Gross Beta 

Uranium-235 

Uranium-238 

Pathway Total 

9.87E-07 

WAG 1, SWMU 100b, ESE-Excavation External Exposure to Sediment 

Aluminum 

b 

Arsenic 

A b 

Beryllium 

Cobalt 

B2 b 

b 

Lead 

Sodium 

B2 

h 

b 

Gross Alpha 

2.09E-01 

b 

Gross Beta 

3.36E-01 

b 

Uranium-235 

1.97E-02 2.65E-07 b 5.23E-09 

Uranium-238 

5.96E-02 5.25E-08 b 3.13E-09 

Pathway Total 

8.36E-09 


Aluminum 

5.14E-05 

Arsenic 

2.79E-08 1.5OE+00 A a 4.19E-08 

Beryllium 


Cobalt 

Lead 


5.42E-08 

B2 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-235 

6.76E-07 

1.37E+02 

2.21E+02 

1.30E+01 4.70E-11 6.09E-10 

Uranium-238 

3.92E+01 6.20E-11 2.43E-09 

Pathway Total 

5.97E-08 

WAG 1, SWMU IOOb, ESE-Excavation Inhalation of Sediment 

Aluminum 7.80E- 10 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-235 

Uranium-238 

Pathway Total 

SWMU Total 

4.23E-13 5.00E+01 A b 2.12E-11 

5.21E-14 8.40E+00 B2 b 4.38E- 13 

6.76E-13 

8.22E-13 

B2 

1.03E- 11 

2.08E-03 

3.35E-03 

1.97E-04 1.30E-08 2.56E-12 

5.94E-04 1.24E-08 7.37E-12 

WAG 1, SWMU lOOc, ESO-Excavation Dermal Contact with Soil 

Alummum 3.53E-05 45 

Arsenic 

2.1 1E-08 3.66E+00 A 

Beryllium 

1.88E-09 4.30E+02 B2 

Cobalt 

Lead 

2.98E-08 


B2 

Sodium 

1.41 E-06 

Thallium 

2.40E-IO 

NA 52 




Endrin Ketone 

Naphthalene 

2.22E-09 

5.43E-IO 

7.41E-12 

7.65E-12 

1.34E-09 

D 

43 

43 

Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-238 

3.69E-09 

D 2 

Pathwav Total 

WAG 1, SWMU IOOc, ESO-Excavation External Exposure to Soil 

8 7.72E-08 

13, 1 8.10E-07 

26 

26 

3.15E-11 

8.88E-07 

1.06E-06 

Page 27 of 64

~ 




Arsenic A b 


Cobalt 

b 

Lead B2 b 

Sodium 

b 

Thallium NA b 

2-Methvlnaphthalene 

b 


b 


b 

Endrin Ketone 

b 




Gross Beta 3.30E-01 b 

Neptunium-237 2.19E-03 4.62E-07 b 1.01E-09 

Thorium-228 1.93E-02 9.94E-07 b 1.92E-08 

Uranium-238 1.89E-02 5.25E-08 b 9.91 E- 10 

Pathway Total 

2.12E-08 

WAG 1. SWMU IOOc, ESO-Excavation Ingestion of Soil 

Aluminum 

5.65E-05 

Arsenic 3.37E-08 1.50E+00 A a 5.06E-08 


Cobalt 


Lead 6.98E-08 B2 

Sodium 

2.25E-06 





Endosulfan Sulfate 5.93E-12 


Naphthalene 

1.07E-09 

D 

Phenanthrene 

2.95E-09 

D 

Gross Alpha 

1.37E+02 

Gross Beta 

2.17E+02 

Neptunium-237 1.44E+00 3.00E-10 4.32E-10 

Thorium-228 1.27E+01 2.31E-10 2.93E-09 

Uranium-238 1.24E+O 1 6.20E- 11 7.69E-10 

Pathwav Total 

6.77E-08 

WAG 1, SWMU lOOc, ESO-Excavation Inhalation of Soil 

Aluminum 

8.57E-10 

Arsenic 

5.12E-13 5.00E+01 A b 2.56E-11 

Beryllium 

4.57E-14 8.40E+00 B2 b 3.84E- 13 

Cobalt 

Lead 

Sodium 

Thallium 




Endrin Ketone 

Naphthalene 

Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

7.23E-13 

1.06E-12 

3.42E-11 

5.83E- 15 

2.70E- 14 

6.6OE-15 

8.99E- 17 

9.28E-17 

1.63E- 14 


2.08E-03 

3.29E-03 

2.18E-05 3.45E-08 

B2 

NA 

D 

D 

7.54E-13 

Thorium-228 

3.92E-04 9.68E-08 

1.86E- 11 

Uranium-238 

1.88E-04 1.24E-08 

2.33E-12 

Pathway Total 


SWMU Total 

9.77s-07 


A I u m m u m 3.71E-05 4s 



Cobalt 3.82E-08 16 

Page 28 of 64


AN- 



Lead 2.85E-08 B2 26 

Sodium 

Sulfate 

Thallium 

I,], I-Trichloroethane 

I.04E-06 

3.26E-06 

2.24E-10 

3.10E- 10 

NA 

D 

52 

55 

1,1 -Dichloroethene 2.01E-10 6.00E-01 C 31 1.21E- 10 



1 S6E-09 2.35E+01 B2 

2 3.66E-08 



D 2 

Dihenzo(qh)anthracene 5.43E-10 2.35E+01 B2 2 1.28E-08 

Indeno( 1,2,3-cd)pyrene 1.41E-09 2.35E+00 B2 2 3.31 E-09 

Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

5.30E- 10 

D 

2 

Pathway Total 

WAG 1. SWMU 136. ESO-Excavation External Exoosure to Soil 

8.24E-07 

Aluminum 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Sulfate 

Thallium 

I,],]-Trichloroethane 

1 ,I-Dichloroethene 







Phenanthrene 

A 

B2 

BZ 

NA 

D 

C 

B2 

B2 

BZ 

D 

B2 

BZ 

D 

b 

b 

b 

h 

h 

h 

h 

h 

b 

b 

b 

h 

h 

h 

b 

b 

h 

Gross Alpha 

Gross Beta 

Uranium-238 

1.49E-01 

2.18E-01 

1.18E-02 5.25E-08 

b 

b 

h 6.19E- 10 



Aluminum 

5.93E-05 

2.13E-08 I.50E+00 A a 3.20E-08 


Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Sulfate 

Thallium 

I,],]-Trichloroethane 

I,l-Dichloroethene 





Dihenzo(ah)anthracene 


Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

6.11E-08 


1.67E-06 

5.22E-06 

3.59E-10 

9.93E-11 

6.45E-11 

1.17E-09 

1.24E-09 

1.30E-09 

l.lOE-09 


1.12E-09 


9.82E+01 

1.43E+02 

7.75E+00 

6.00E-01 

7.30E-01 

7.30E+00 

7.30E-01 

7.30E+00 

7.30E-01 

B2 

NA 

D 

C 

B2 

BZ 

B2 

D 

B2 

BZ 

D 

a 

a 

3.87E-11 

8.52E-10 

9.09E-09 

9.52E-10 

3.17E-09 

8.21E-10 

6.20E-11 


Pathwav Total 

WAG 1. SWMU 136. ESO-Excavation Inhalation of Soil 

Aluminum 

9.00E-10 

Arsenic 3.23E-13 5.00E+01 A h 1.62E-11 

Page 29 of 64 

5.88E-08




Beryllium 4.04E-14 8.40E+00 B2 h 3.39E- 13 

Cobalt 

9.26E-13 

Lead 6.91E-13 B2 

Sodium 

2.53E-11 

Sulfate 

7.92E-11 

'Ihallium 5.45E-15 NA 

l,l,l-Trichloroethane 3.85E- 10 D 

1,l-Dichloroethene 6.64E-10 1.20E+00 C h 7.97E-10 

Benzo(a)anthracene 1.77E-14 B2 

Benzo(a)pyrene 1.89E- 14 B2 

Benzo(h)fluoranthene 1.98E- 14 B2 


Dihenzo(qh)anthracene 6.60E-15 B2 

Indene( 1,2,3-cd)pyrene 1.71E- 14 B2 


Gross Alpha 

1.49E-03 

Gross Beta 2.1%-03 

Uranium-238 1.18E-04 1.24E-08 1.46E- 12 

Pathway Total 

8.15E-10 

SWMU Total 

8.85E-07 

WAG 1, SWMU 38q ESE-Excavation Dermal Contact with Sediment 


Beryllium 5.37E-09 4.30E42 B2 13, 1 2.31E-06 

Cobalt 3.39E-08 26 

Lead 3.09E-08 B2 26 

Sodium 

1.39E-07 



Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 1, SWMU 38% ESE-Excavation External Exposure to Sediment 

2.31E-06 

Aluminum 

b 

Beryllium 

Cobalt 

B2 

h 

h 

Lead 

Sodium 

B2 h 

h 

Vanadium 

NA b 

Phenanthrene 

D b 

Gross Alpha 

Gross Beta 

1.22E-01 

1.59E-01 

h 

h 

Uranium-238 3.81E-02 5.25E-08 b 

~ 

2.OOE-09 _. 

Pathway Total 


2.00E-09 

Aluminum 

2.47E-05 


Cobalt 

5.42E-08 


Sodium 

2.23E-07 



Gross Alpha 8.00E41 

Gross Beta 

1.05E+02 

Uranium-238 2.51EMl 6.20E-11 1 SSE-09 

Pathway Total 

3.85E-08 


Aluminum 

3.75E-10 


Cobalt 

8.22E-13 

Lead 7.49E-13 B2 

Sodium 

3.38E-12 



Page 30 of 64




Gross Alpha 1.21E-03 

Gross Beta 

1.59E-03 

Uranium-238 3.80E-04 1.24E-08 


Pathway Total 

5.81E- 12 


Beryllium 1.58E-09 4.30E+02 BZ 13. 1 6.78E-07 

Cobalt 2.25E-08 26 

Lead 6.11E-08 B2 26 

Sodium 

2.36E-07 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 1, SWMU 38b, ESE-Excavation External Exposure to Sediment 

Aluminum 

b 

Arsenic A b 

Beryllium BZ b 

Cobalt 

b 

Lead B2 b 

Sodium 

b 

Gross Alpha 1.45E-0 1 b 


Uranium-238 3.02E-02 5.25E-08 b 1.59E-09 

Pathway Total 


Aluminum 


Arsenic 1.93E-08 1.50E+00 A a 2.90E-08 


Cobalt 

3.60E-08 


Sodium 

3.78E-07 

Gross Alpha 

9.50E+01 

Gross Beta 

2.02E+02 

Uranium-238 1.99E+01 6.20E-11 1.23E-09 

Pathway Total 


Aluminum 

7.23E-10 

Arsenic 2.93E-13 5.00E+01 A b 1.47E- 11 




Sodium 

5.73E-12 

Gross Alpha 

1.44E-03 

Gross Beta 

3.06E-03 

Uranium-238 3.01E-04 1.24E-08 3.74E- 12 

Pathway Total 

S WMU Total 

N’AG 1. SWMU 38c, ESO-Excavation Dermal Contact with Soil 


Arsenic 

1.96E-08 3.66E+00 A 8 7.19E-08 

Beryllium 


Cobalt 

3.16E-08 

26 

Lead 


B2 26 

Sodium 

6.66E-07 

Thallium 

3.98E-10 

NA 

52 

2-Hexanone 

1.68E-10 

36 

Aroclor-1260 

2.67E-10 8.56E+00 BZ 46 2.29E-09 

Benzo(a)anthracene 1.01E-09 2.35E+00 BZ 2 2.37E-09 


8.72E-10 2.35E+01 BZ 2 2.05E-08 



Page 31 of 64 

7.22E-07 

1.59E-09 


1.87E-11 

7.65E-07




Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

Pathway Total 

8.86E-07 

WAG 1, SWMU 38c, ESO-Excavation External Exposure to Soil 

Aluminum 

h 

Arsenic A b 


Cobalt 

h 

Lead B2 b 

Sodium 

h 

Thallium NA b 

2-Hexanone 

b 

Aroclor- 1260 B2 h 



Benzo(h)fluoranthene B2 b 


Gross Alpha 2.20E-01 h 

Gross Beta 3.04E-01 h 

Neptunium-237 1.93E-02 4.62E-07 h 8.93E-09 

Thorium-228 1.62E-02 9.94E-07 b 1.62E-08 

Uranium-235 3.53E-03 2.65E-07 h 9.37E-10 

Uranium-238 6.25E-02 5.25E-08 b 3.28E-09 

Pathway Total 

2.93E-08 

WAG 1, SWMU 38c, ESO-Excavation Ingestion of Soil 

Aluminum 



Beryllium 2.92E-09 4.30E+00 B2 a 1.268-08 

Cobalt 

5.05E-08 

Lead 7.40E-08 B2 

Sodium 

1.07E-06 


2-Hexanone 

5.37E-11 

Aroclor-1260 2.14E-10 7.70E+00 B2 1.65E-09 


Benzo(a)pyrene 6.98E-10 7.3OE+OO B2 a 5.09E-09 

Benzo(b)fluoranthene 1.02E-09 7.30E-01 B2 7.44E- 10 


Gross Alpha 

1.45E+02 

Gross Beta 

2.00E+02 

Neptunium-237 1.27E+O 1 3.00E- 10 3.81E-09 

Thorium-228 1.07E+01 2.31E-10 2.47E-09 


Uranium-238 4.10E+01 6.20E-11 2.548-09 

Pathway Total 

7.67E-08 

WAG 1, SWMU 38c, ESO-Excavation Inhalation of Soil 

Aluminum 

7.41E-10 

Arsenic 

4.77E-13 5.00E+01 A h 2.38E-11 

Beryllium 

4.43E-34 8.40E+00 B2 h 3.73E-13 

Cobalt 

Lead 

Sodium 

Thallium 

2-Hexanone 

Aroclor- 1260 




Phenanthrene 

7.67E-13 

1.12E- 12 

1.62E-11 

9.66E- 15 

8.14E-16 

3.24E-15 

1.22E-14 

1.06E-14 

1.55E-14 

2.06E-14 

B2 

NA 

B2 

B2 

B2 

B2 

D 

Gross Alpha 

2.20E-03 

Page 32 of 64




Gross Beta 

3.03E-03 

Neptunium-237 1.93E-04 3.45E-08 

6.65E-12 

Thorium-228 1.62E-04 9.68E-08 

1.57E-11 

Uranium-235 3.52E-05 1.30E-08 


Uranium-238 6.23E-04 1.24E-08 

7.72E-12 

Pathwav Total 

5.47E-11 

SWMU Total 

9.92E-07 


Lead 3.79E-08 B2 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 7, SWMU 130, ESO-Excavation External Exposure to Soil 

Lead BZ b 



Uranium-238 1.49E-02 5.25E-08 b 7.82E-10 

Pathway Total 

7.82E-10 


Lead 6.07E-08 B2 

Gross Alpha 

6.36E+01 

Gross Beta 

1.61E+02 

Uranium-238 9.79E+00 6.20E-11 6.07E-10 

Pathway Total 

6.07E-10 



Gross Alpha 

9.64E-04 

Gross Beta 

2.45E-03 

Uranium-238 1.49E-04 1.24E-08 1.84E- 12 


SWMU Total 

1.39E-09 


Lead 6.68E-08 B2 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead BZ b 

Gross Alpha 

1.83E-01 

h 

Gross Beta 

2.69E-01 

b 

Uranium-238 1.69E-02 5.25E-08 

b 8.90E- 10 

Pathway Total 

8.90E-10 


Lead 1.07E-07 B2 

Gross Alpha 

1.20E+02 

Gross Beta 

1.77E+02 

Uranium-238 l.llE+Ol 6.20E-11 6.90E-10 

Lead 

1.62E-12 

Gross Alpha 

1.82E-03 

Gross Beta 

2.68E-03 

Uranium-238 1.69E-04 1.24E-08 

Pathwav Total 

SWMU Total 


Lead 3.93E-07 BZ 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 7. SWMU 132. ESO-Excavation External Exposure to Sod 

2.09E- 12 

2.09E-12 

1.58E-09 

Page 33 of 64

~ 


I.UIAL IOTAL 



Lead B2 b 


b 


h 

Uranium-238 2.11E-02 5.25E-08 

b l.llE-09 



Lead 6.30E-07 B2 

Gross Alpha 

1.18E+02 

Gross Beta 

2.05E+02 

Uranium-23 8 1.39E+01 6.20E-11 8.61 E- 10 




Gross Alpha 

1.79E-03 

Gross Beta 

3.11E-03 

Uranium-238 2.11E-04 1.24E-08 2.61E-12 

Pathway Total 

2.61E-12 

SWMU Total 

1.97E-09 


Lead 5.43E-07 BZ 26 



3.93E-09 

2.95E-08 2.35E+00 BZ 

2 

2 6.94E-08 


2.22E-08 2.35E+01 BZ 2 5.22E-07 

Benzo@)fluoranthene 2.38E-08 2.35E+00 B2 2 5.6 1E-08 


D 2 

Benzo(k)fluoranthene 1.99E-08 2.35E-01 B2 2 4.69E-09 

Dibenzo(a,h)anthracene 1.63E-09 2.35E+01 BZ 2 3.83E-08 

Indene( 1,2,3-cd)pyrene 1.09E-08 2.35E+00 BZ 2 2.57E-08 

Phenanthrene 

2.67E-08 

D 2 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

7.16E-07 


Lead B2 b 









Phenanthrene 

BZ 

B2 

B2 

D 

BZ 

B2 

BZ 

D 

b 

b 

b 

b 

b 

b 

b 

b 

b 

Gross Alpha 

Gross Beta 

Uranium-238 

2.83501 

3.32E-01 

2.24E-02 5.25E-08 

b 

b 

b 1.18E-09 

Pathway Total 

1.18E-09 

WAG 7. SWMU 133. ESO-Excavation Ingestion of Soil 

Lead 8.70E-07 B2 


3.14E-09 


Benzo(a)pyrene 1.77E-08 7.30E+00 BZ a 1.29E-07 



Benzo(k)fluoranthene 1.59E-08 7.30E-02 B2 1.16E-09 

Dibenzo(qh)anthracene 1.30E-09 7.30EM0 B2 9.49E-09 

Indene( 1,2,3-cd)pyrene 8.72E-09 7.30E-0 1 BZ 6.37E-09 


Gross Alpha 

1.86E+02 

Gross Beta 

2.18E+02 

Uranium-238 1.47EM1 6.20E-11 9.12E- LO 

Pathway Total 

1.78E-07 

WAG 7, SWMU 133, ESO-Excavation Inhalabon of Soil 

Page 34 of 64


A N m 'IO'IAL IO'I'AL 



Lead 1.32E- 11 B2 









Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


3.58E- 13 

2.69E-13 

2.89E- 13 

1.60E- 13 

2.42E- 13 

1.97E-14 

1.32E- 13 

3.23E-13 

2.83E-03 

3.31E-03 

2.23E-04 

B2 

B2 

B2 

D 

B2 

B2 

B2 

D 

1.24E-08 

2.77E- 12 

2.77E- 12 

SWMU Total 

8.95E-07 


Lead 8.72E-08 B2 26 

Benzo( a)anthracene 1.01E-09 2.35E+00 B2 2 2.37E-09 


Benzo(h)fluoranthene 1.40E-09 2.35E+00 B2 2 3.30E-09 

Benzo(g,h,i)perylene 4.97E-10 D 2 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

2.78E-08 

WAG 7. SWMU 134. ESO-Excavation External Emosure to Soil 




Benzo(g.h,i)perylene 

Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

2.17E-0 1 

2.45E-01 

1.67E-02 

5.25E-08 

B2 

B2 

B2 

D 

D 


Lead 1.40E-07 B2 


Benzo( a)p yrene 



Phenanthrene 

Gross Alpha 

Gross Beta 

3.97E-10 

1.80E-09 

1.43E+02 

1.61E+02 

D 

D 

Uranium-238 

1.09E+01 6.20E-11 

h 

h 

b 

b 

h 

h 

b 

h 

8.75E-10 

8.05E-10 7.30E-01 B2 5.88E-10 

7.51E-10 7.30E+00 B2 a 5.49E-09 

l.12E-09 7.30E-01 B2 8.18E-10 

8.75E-10 

6.79E- 10 

Pathway Total 

7.57E-09 


Lead 2.12E-12 B2 

Benzo( a)anthracene 1.22E-14 B2 

Benzo(a)pyrene 1.14E- 14 B2 

Benzo@)fluoranthene 1.70E-14 B2 

Benzo( g,h,i)perylene 6.03E-15 D 


Gross Alpha 

2.16E-03 

Gross Beta 

2.45E-03 

Uranium-238 1.66E-04 1.24E-08 2.06E-12 


SWMU Total 

WAG 7, SWMU 8b, ESO-Excavation Dermal Contact with Soil 



Bervllium 2.34E-09 4.30E+02 B2 13. 1 1.00E-06 

3.62E-08 

Page 35 of 64




Cobalt 2.59E-08 26 

Lead 

3.34E-08 

B2 26 


Sodium 

Thallium 


1.91E-07 

3.64E-07 

5.19E- 10 

8.05E-10 

NA 52 

43 

Aroclor-1260 

1.92E-10 8.56E+00 B2 46 1.64E-09 



1.69E-09 2.35E+01 B2 2 3.97E-08 

Benzo(b)fluoranthene 1.91E-09 2.35E+00 B2 2 4.49E-09 

Dibenzofuran 


1.65E-09 

1.54E-09 2.35E+00 B2 2 3.63E-09 

Naphthalene 

1.69E-09 

D 43 

Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

llorium-228 

Thorium-230 

Uranium-235 

Uranium-238 

1.54E-09 

D 2 

Padway TO~~I 1.llE-06 

~~ 

WAG 7, SWMU 8b, ESO-Excavation External Exposure to Soil 

Aluminum 

b 

Arsenic 

Beryllium 

Cobalt 

Lead 


Sodium 

Thallium 


Aroclor-1260 




Dibenzofuran 


Naphthalene 

Phenanthrene 

A 

B2 

B2 

NA 

B2 

B2 

B2 

B2 

B2 

D 

D 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

Gross Alpha 

Gross Beta 

Neptunium-237 

1.54E-01 

2.58E-01 

2.92E-02 4.62E-07 

b 

b 

b 1.35E-08 

Thorium-228 

1.64E-02 9.94E-07 

b 1.63E-08 

Thorium-230 


b 3.34E- 10 

Uranium-235 

2.82E-03 2.65E-07 

b 7.47E-10 

Uranium-238 

5.54E-02 5.25E-08 

b 2.91E-09 

Pathway Total 

3.38E-08 

WAG 7, SWMU 8b, ESO-Excavation Ingestion of Soil 

Aluminum 

5.83E-05 

Arsenic 2.17E-08 1.50E+00 A a 3.26E-08 


Cobalt 


Lead 5.35E-08 B2 


3.06E-07 

Sodium 

5.83E-07 



Aroclor-1260 1.53E-10 7.70E+00 B2 1.18E-09 


Benzo(a)pyrene 1.3SE-09 7.30E+00 B2 a 9.84E-09 

Benzo(b)fluoranthene 1.52E-09 7.30E-01 B2 1.1 IE-09 

Dibenzohran 

1.32E-09 

Indene( 1,2,3-cd)pyrene 1.23E-09 7.30E-01 B2 9.01E-10 

Page 36 of 64

~~~ ~ ~ 






Gross Alpha 

1.01E+02 

Gross Beta 

1.69E+02 

Neptunium-237 1.92E+O 1 3.00E- 10 5.76E-09 

Thorium-228 1.08E+O 1 2.3 1E-10 2.48E-09 

Thorium-230 4.99E+03 3.75E-11 1.87E-07 


Uranium-238 3.64E+01 6.20E-11 

2.26E-09 

Pathway Total 

2.60E-07 

Q'AG 7, SWMU 8b, ESO-Excavation Inhalation of Soil 

Aluminum 

8.85E-10 

Arsenic 

3.30E-13 5.00E+01 A b 1.65E-11 

Beryllium 

5.67E-14 8.40E+00 B2 b 4.76E-13 

Cobalt 

Lead 


Sodium 

Thallium 


Aroclor-1260 

' Benzo(a)anthracene 



Dibenzofuran 


Naphthalene 

Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

6.29E- 13 

8.11E- 13 


8.85E- 12 

1.26E-14 

9.77E-15 

2.33E-15 

1.41E-14 

2.05E-14 

2.31E-14 

2.01E-14 

1.87E-14 

2.OSE-14 

1.87E- 14 

1.53E-03 

2.57E-03 

2.91E-04 3.45E-08 

BZ 

NA 

B2 

BZ 

BZ 

BZ 

BZ 

D 

D 

1 .OOE- 11 

Thorium-228 

1.63E-04 9.68E-08 

1.58E-11 

Thonum-230 

7.57E-02 1.72E-08 

1.30E-09 

Uranium-235 

2.81E-05 1.30E-08 

3.65E-13 

Uranium-238 

5.52E-04 1.24E-08 

6.85E-12 

Pathway Total 

1.35E-09 

SWMU Total 

1.40E-06 

WAG 1. SWMU lOOa ISE-Current Industrial Dermal Contact with Sediment 


Arsenic 3.32E-07 3.66E+00 A 8 1.22E-06 

Beryllium 4.84E-08 4.30E+02 B2 13, 1 2.08E-OS 

Cobalt 9.56E-07 26 

Lead 6.70E-07 B2 26 

Sodium 

7.87E-06 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

2.20E-05 

WAG 1, SWMU 100% ISE-Current Industrial External Exposure to Sediment 

Aluminum 

b 

Arsenic 

A 

b 

Beryllium 

B2 b 

Cobalt 

b 

Lead 

BZ b 

Sodium 

b 

Gross Alpha 

1.35E+01 

b 

Gross Beta 

2.78E+01 

b 

Liranium-238 

1.88E+00 5.2SE-08 b 9.89E-08 

Pathway Total 

9.89E-08 

a'AG 1. SWMU 100% ISE-Current Industrial Ingestion of Sedment 

Aluminum 

6.98E-04 

Arsenic 

3.24E-07 1.50E+00 A a 4.86E-07 

Beryllium 

4.71E-08 4.30E+00 B2 a 2.03E-07 

Cobalt 9.31E-07 

Page 37 of 64




Lead 6.53E-07 B2 

Sodium 

7.67E-06 

Gross Alpha 

3.57E+02 

Gross Beta 

7.30E+02 




Alummum 

6.52E-08 

Arsenic 3.OZE-11 5.00E+01 A b 1.51E-09 

Beryllium 4.40E-12 8.40E+00 B2 b 3.70E-11 

Cobalt 

8.69E-11 

Lead 6.10E-11 B2 


Gross Alpha 

8.66E-02 


Uranium-238 1.20E-02 1.24E-08 1.49E- 10 

Pathway Total 

1.70E-09 

WAG I. SWMU 100% ISW-Current Industrial Dermal Contact with Water 

Aluminum 

4s 

Cadmium 

Cobalt 

3.72E-07 

B1 16, 1 

26 

Lead 


B2 26 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-238 

Pathway Total 

S WMU Total 

2.28E-05 

WAG 1, SWMU IOOb, ISE-Current Industrial Dermal Contact with Sediment 

Aluminum 5 S9E-04 4,5 

Arsenic 

3.03E-07 3.66E+00 A 8 l.llE-06 

Beryllium 


Cobalt 


Lead 

5.89E-07 B2 26 

Sodium 

7.35E-06 

Gross Alpha 

Gross Beta 

Uranium-235 

Uranium-238 

Pathway Total 

1.72E-05 

WAG 1, SWMU 100b, ISE-Current Industrial External Exposure to Sediment 

Aluminum 

b 

Arsenic A b 


Cobalt 

b 

Lead BZ b 

Sodium 

b 

Gross Alpha 2.12E+O 1 h 


Uranium-235 2.00E+00 2.65E-07 b 5.31E-07 

Uranium-238 6.05E+00 5.25E-08 b 3.18E-07 

Pathway Total 

8.49E-07 

WAG 1, SWMU 100b, ISE-Current Industrial Ingestion of Sediment 

Alummum 

5.44E-04 



Cobalt 4.71 E-07 

Lead 5.74E-07 B2 

Sodium 

7.16E-06 

Gross Alpha 

5.59E+02 

Gross Beta 

8.98E+02 

Uranium-235 5.27E+O 1 4.70E- 11 

2.48E-09 

Uranium-238 1.59E+02 6.20E-11 9.88E-09 

Page 38 of 64




Pathway Total 

6.12E-07 

WAG 1, SWMU 100b, ISE-Current Industrial Inhalation ofsediment 

Aluminum 

5.08E-08 

Arsenic 

2.76E-11 5.00E+01 A b 1.38E-09 

Beryllium 

3.39E-12 8.40E+00 B2 b 2.85E-11 

Cobalt 

Lead 


5.35E-11 

B2 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-235 

6.68E-10 

1.36E-01 

2.18E-01 

1.28E-02 1.30E-08 1.66E- 10 

Uranium-238 

3.87E-02 1.24E-08 4.80E- 10 

Pathway Total 

2.05E-09 

WAG 1, SWMU lob, ISW-Current Industrial Dermal Contact with Water 

Aluminum 4,5 

Arsenic 3.92E-08 3.66E+00 A 8 1.43E-07 

Lead 7.58E-07 B2 26 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-235 

Uranium-238 

Pathway Total 

1.43E-07 

S WMU Total 

1.88E-05 

WAG 1, SWMU lOOc, ISO-Current Industrial Dermal Contact with Soil 


Arsenic 2.22E-07 3.66E+00 A 8 8.13E-07 


Cobalt 2.58E-07 26 

Lead 6.88E-07 B2 26 

Sodium 

6.07E-06 


6.39E-09 

Gross Alpha 

Gross Beta 

Thorium-228 

Uranium-235 

Uranium-238 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 


Gross Alpha 

Gross Beta 

Thorium-228 

Uranium-235 

Uranium-238 

Pathway Total 

1.32E+01 

2.07E+01 

1.19E+00 


1.79E+00 

9.94E-07 

2.65E-07 

5.2fE-08 

A 

B2 

B2 

b 

b 

b 

b 

b 

ti 

b 

b 

b 

b 

b 

1.18E-06 

1.13E-07 

9.40E-08 

WAG 1, SWMU IOOc, ISO-Current Industrial Ingestion of Soil 

Aluminum 

3.15E-04 

Arsenic 2.16E-07 1.50E+00 A a 3.25E-07 


Cobalt 2.51E-07 

Lead 6.71E-07 B2 

Sodium 

5.9 IE-06 


3.11E-09 

Gross Alpha 

9.02E+02 

Gross Beta 

1.41E+03 

Thorium-228 8.11E+01 2.31E-10 1.87E-08 

1.39E-06 

Page 39 of 64





Uranium-238 1.23E+02 6.20E-11 7.60E-09 

Pathway Total 


WAG 1, SWMU lOOc, ISO-Current Industrial Inhalation of Soil 

Aluminum 

2.94E-08 

Arsenic 

2.02E-11 5.00E+01 A h 1 .O 1E-09 

Beryllium 

1.56E-12 8.40E+00 B2 h 1.31E-11 

Cobalt 

Lead 

2.35E-11 

6.26E-11 

B2 

Sodium 


Gross Alpha 

Gross Beta 

Thonum-228 

5.52E- 10 

2.91E-13 

8.42E-02 

1.32E-01 

7.57E-03 9.68E-08 7.33E-10 

Uranium-23 5 

2.73E-03 1.30E-08 3.55E-11 

Uranium-23 8 

1.14E-02 1.24E-08 1.42E- 10 

Pathway Total 

1.93E-09 

S WMU Total 

1 .OOE-05 



Arsenic 9.63E-09 3.66E+00 A 8 3.52E-08 



Lead 1.03E-08 B2 26 

Sodium 

1.37E-07 

Sulfate 

1.53E-06 

Thallium 2.2 1E- 10 NA 52 



Benzo@)fluoranthene 2.02E-09 2.35E+00 B2 2 4.76E-09 


Dibenzo(a,h)anthracene 2.56E-10 2.35E+01 B2 2 6.02E-09 

Indeno(l,2,3-cd)pyrene 9.79E-10 2.35E+00 B2 2 2.30E-09 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

3.82E-07 

WAG 1, SWMU 136, ISO-Current Industrial External Exposure to Soil 

Aluminum 

b 

Arsenic A h 


Cobalt 

h 

Lead B2 h 

Sodium 

b 

Sulfate 

h 

Thallium NA h 

Benzo(a)anthracene B2 h 

Benzo( a)pyrene B2 h 


Benzo(g,h,i)perylene D h 

Dibenzo(a,h)anthracene B2 h 

Indene( 1,2,3-cd)pyrene B2 h 


Gross Alpha 2.26E-0 1 h 


Uranium-238 3.50E-02 5.25E-08 h 1.84E-09 

Pathwav Total 

1.84E-09 



Arsenic 9.38E-09 1.50E+00 A a 1.41E-08 

Beryllium 6.61E-10 4.30E+00 B2 a 2.84509 

Cobalt 


Page 40 of 64




Sodium 

1.33E-07 

Sulfate 

Thallium 

1.49E-06 

2.15E-10 

NA 




8.00E-10 7.30E+00 B2 a 5.84E-09 

Benzo(h)fluoranthene 9.84E-10 7.30E-01 B2 

7.18E-10 


Dihenzo(qh)anthracene 

4.15E-IO 

1.25E-10 7.30E+00 

D 

B2 

9.09E-10 

Indeno( 1,2,3-cd)pyrene 4.77E-10 7.30E-01 B2 

3.48E-10 

Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

1.2 IE- 10 

1.55E+O 1 

1.77E+O 1 

2.39E+00 6.20E-11 

D 

1.48E-10 

Pathway Total 

2.53E-08 

WAG 1, SWMU 136, ISO-Current Industrial Inhalation ofsoil 

Aluminum 

1.04E-09 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Sulfate 

Thallium 







Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

8.76E-13 

6.17E-14 

3.88E- 12 

9.33E-13 

1.24E-11 

1.40E-10 

2.01E-14 

5.45E- 14 

7.46E- 14 

9.19E- 14 

3.88E- 14 

1.16E- 14 


1.13E- 14 

1.45E-03 

1.65E-03 

2.23E-04 

5.00E+01 

8.40E+00 

1.24E-08 

A h 4.38E-11 

B2 h 5.19E- 13 

B2 

NA 

B2 

B2 

B2 

D 

B2 

B2 

D 

2.77E-12 

S WMU Total 




Cobalt 5.89E-07 26 

Lead 5.36E-07 B2 26 

Sodium 

2.42E-06 



Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 1. SWMU 38% ISE-Current Industrial External Exposure to Sediment 

Aluminum 

h 


Cobalt 

h 

Lead B2 h 

Sodium 

h 

Vanadium NA h 



Gross Beta 1.62E+O 1 h 

Uranium-238 3.87E+00 5.25E-08 h 2.03E-07 

Pathway Total 

M'AG 1. SWMU 38% ISE-Current Industrial Ingestion of Sediment 

Aluminum 

2.61E-04 

Beqllium 9.09E-08 4.30E+00 B2 a 3.91E-07 

Cobalt 

5.74E-07 



2.03E-07 


Page41 of64


W I i 7 7 T i - i - 



Sodium 

2.36E-06 



Gross Alpha 

3.25E+02 

Gross Beta 


Uranium-238 1.02E+02 6.20E-11 6.32E-09 

Pathway Total 

3.97E-07 


Aluminum 

2.44E-08 

Beryllium 

8.48E-12 8.40E+00 B2 h 7.13E-11 

Cobalt 

Lead 

5.35E-11 


B2 

Sodium 

Vanadium 

2.20E-10 

5.15E- 10 

NA 

Phenanthrene 

5.30E- 13 

D 

Gross Alpha 

Gross Beta 

Uranium-238 

7.90E-02 

1.03E-0 1 

2.47E-02 1.24E-08 3.07E- 10 

Lead 1.60E-07 B2 26 

Sodium 

Chloroform 9.98E-07 3.05E-02 B2 24 3.OSE-08 

bis(2-Ethylhexy1)phthalate 1.30E-06 7.37E-02 B2 15 9.60E-08 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

SWMU Total 



Arsenic 2.10E-07 3.66E+00 A 8 7.68E-07 


Cobalt 3.91E-07 26 

Lead 1.06E-06 B2 26 

Sodium 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 1, SWMU 38b, ISE-Current Industrial External Exposure to Sediment 

Aluminum 

h 

Arsenic A h 


Cobalt 

h 

Lead B2 b 

Sodium 

b 


Gross Beta 3.12E+O 1 b 

Uranium-238 3.07E+OO 5.25E-08 b 1.61E-07 

Pathway Total 

WAG 1. SWMU 38h, ISE-Current Industrial Ingestion of Sediment 

Aluminum 

5.04E-04 

Arsenic 2.04E-07 1.50E+00 A a 3.07E-07 


Cobalt 

3.80E-07 

Lead 1.03E-06 B2 

Sodium 


Gross Alpha 

3.87E+02 

Gross Beta 

8.20E+02 

Uranium-238 8.09E+O 1 6.20E- 11 5.01E-09 

Pathway Total 

WAG 1, SWMLJ 38b, ISE-Current Industrial Inhalation of Sediment 

Page 42 of 64 

2.39E-07 

1.26E-05 

1.61E-07 






Aluminum 


Arsenic 

1.91E- 11 5.00E+O 1 A h 9.54E- 10 

Beryllium 

2.49E-12 8.40E+00 B2 b 2.09E-11 

Cobalt 

Lead 

3.55E-11 

9.65E-11 

B2 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-238 

3.73E- 10 

9.39E-02 

1.99E-01 

1.96E-02 1.24E-08 2.43E-10 

Sodium 

Gross Alpha 

Gross Beta 

Neptunium-237 

Plutonium-238 

Uranium-234 

Uranium-238 

Pathway Total 

S WMU Total 

WAG 1, SWMU 38c, ISO-Current Industrial Dermal Contact with Soil 


Arsenic 

1.14E-06 3.66E+00 A 

Beryllium 

9.46E-08 4.30E+02 B2 

Cobalt 

Lead 

Sodium 

Aroclor-1260 

1.75E-06 

3.46E-06 

1.55E-05 

1.56E-08 8.56E+00 

B2 

B2 

Benzo(a)anthracene 4.95E-08 2.35E+00 B2 


4.29E-08 2.35E+01 B2 

Benzo(b)fluoranthene 6.27E-08 2.35E+00 B2 

Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

8.77E-08 

D 

Pathway Total 

WAG 1, SWMU 38c, ISO-Current Industrial External Exposure to Soil 

Alummum 

Arsenic 

A 

Beryllium 

B2 

Cobalt 

Lead 

B2 

Sodium 

Aroclor- 1260 

B2 


B2 


B2 


B2 

Phenanthrene 

D 

Gross Alpha 

8.53E+O 1 

Gross Beta 

1.27E+02 

Neptunium-237 


Thorium-228 

5.08E+00 9.94E-07 

Uranium-235 


Uranium-238 

5.77E+01 5.25E-08 

Pathway Total 

U’AG 1. SWMU 38c, ISO-Current Industrial Ingestion of Soil 

Aluminum 

1.89E-03 


13, 1 4.07E-05 

26 

26 

46 1.33E-07 

2 1.17E-07 

2 1.01E-06 

2 1.48E-07 

2 

b 

h 

h 

b 

h 

b 

h 

h 

b 

b 

b 

h 

h 

h 

b 

h 

h 

2.68E-06 

5.05E-06 

1.24E-06 

3.03E-06 

Arsenic l.llE-06 1.50E+00 A a 1.66E-06 

Ben.llium 9.21E-08 4.30E+00 B2 a 3.96E-07 

Cobalt 

1.71E-06 

Page 43 of 64 


1.20E-05 

1.3 IE-05

~~ 




Lead 3.37E-06 B2 

Sodium 

Aroclor-1260 




Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-235 

Uranium-238 

Pathwav Total 

1.5 1E-05 

7.58E-09 

2.41E-08 

2.09E-08 

3.05E-08 


5.84E+03 

8.71E+03 

3.97E+02 

3.48E+02 

3.2 lE+OZ 

3.95E+03 

7.70E+00 

7.30E-01 

7.30E+00 

7.30E-01 

3.00E- 10 

2.31E-10 


6.20E-11 

B2 

B2 

B2 

B2 

D 

a 

5.83E-08 

1.76E-08 

1.53E-07 

2.23E-08 

1.19E-07 

8.04E-08 

1.5 1 E-08 

2.45E-07 

WAG 1, SWMU 38c, ISO-Current Industrial Inhalation of Soil 

Aluminum 

1.76E-07 

Arsenic 1.03E- 10 S.OOE+O 1 A b 5.17E-09 

Beryllium 8.60E-12 8.40E+00 B2 b 7.22E- 11 


Lead 3.14E- 10 B2 

Sodium 1.41 E-09 

Aroclor- 1260 7.07E-13 B2 





Gross Alpha 

5.45E-01 

Gross Beta 

8.13E-01 

Neptunium-237 3.70E-02 3.45E-08 1.28E-09 

Thorium-228 3.25E-02 9.68E-08 3.14E-09 

Uranium-235 2.99E-02 1.30E-08 3.89E-10 

Uranium-238 3.69E-0 1 1.24E-08 4.57E-09 

Pathway Total 

S WMU Total 


Lead 1.24E-07 B2 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 7. SWMU 132, ISO-Current Industrial External Exposure to Soil 

Lead B2 b 


Gross Beta 4.29E-01 b 

Uranium-238 3.42E-02 5.25E-08 b 1.80E-09 

Pathway Total 


Lead 1.21E-07 B2 

Gross Alpha 

1.54E+01 

Gross Beta 

2.94E+01 

Uranium-238 2.34E+00 6.20E-11 1.45E-10 

Pathway Total 

WAG 7, SWMU 132,ISO-Current Industrial Inhalation of Soil 

Lead 1.13E-I1 B2 

Gross Alpha 

1.43E-03 

Gross Beta 

2.74E-03 

Uranium-238 2.19E-04 1.24E-08 

2.71E-12 

Pathwav Total 

S WMU Total 

WAG 7. SWMU 133, ISO-Current Industrial Dermal Contact with Soil 

Lead 1.22E-07 B2 26 

Acenaphthylene 9.95E-10 2 

Benzo(a)anthracene 7.84509 2.35E+00 B2 2 l.85E-08 

Benzo(a)pyrene 5.88E-09 2.3SE+01 B2 2 1.38E-07 

Page 44 of 64 

2.77E-06 

1.46E-08 

1.80E-09 

1.45E-10 

2.71E- 12 

6.10E-OS 

1.95E-09

~~ ~~~ 


Y'IE 'IUIAL 



Benzo(b)fluoranthene ., 6.33E-09 2.35E+00 B2 2 1.49E-08 

~ 


Benzo(k)fluoranthene 5.27E-09 2.35E-01 B2 2 1.24E-09 

Dibenzo(a,h)anthracene 3.77E-10 2.35E+01 B2 2 8.87E-09 

Indeno(l,2,3-cd)pyrene 2.86E-09 2.35E+00 B2 2 6.74E-09 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

1.89E-07 


Lead B2 b 

Acenaphthy lene 







lndeno( 1,2,3-cd)pyrene 

Phenanthrene 

B2 

B2 

B2 

D 

B2 

B2 

B2 

D 

b 

b 

b 

b 

b 

b 

b 

b 

h 

Gross Alpha 

Gross Beta 

Uranium-238 

2.42E-01 

3.15E-0 1 

3.05E-02 5.25E-08 

b 

b 

b 1.60E-09 

Pathway Total 

1.60E-09 


Lead 1.19E-07 B2 




3.82E-09 7.30E-01 B2 

2.79E-09 


2.86E-09 7.30E+00 B2 a 2.09E-08 


2.2SE-09 



1.69E-09 

2.57E-09 7.30E-02 

D 

B2 

1.88E-I0 


1.34E-09 


1.02E-09 

Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

3.4SE-09 

1.65E+01 

2.1 SE+O 1 

2.09E+00 6.20E-11 

D 

1.29E-10 

Pathway Total 

2.86E-08 


Lead 1.11E-11 B2 

Acenaphthylene 4.52E- 14 

Benzo(a)anthracene 3 S6E- 13 B2 


Benzo@)fluoranthene 2.88E-13 B2 

Benzo(g,h,i)perylene 1.58E- 13 D 

Benzo(k)fluoranthene 2.40E-13 B2 

Dibenzo(a,h)anthracene 1.71 E- 14 B2 

lndeno( 1,2,3-cd)pyrene 1.30E-I3 B2 


Gross Alpha 

1.54E-03 

Gross Beta 

2.0 IE-03 

Uranium-238 1.95E-04 1.24E-08 

2.42E-12 

Pathway Total 

2.42E- 12 

S WMU Total 

2.19E-07 

WAG 7. SWMU 134. ISO-Current Industrial Dermal Contact with Soil 

Lead 1.13E-08 B2 26 

Benzo( a)anthracene 2.11E-10 2.35E+00 B2 2 4.97E- 10 

Benzo(a)pyrene 2.11E-10 2.35E+01 B2 2 4.97E-09 

Benzo(b)fluoranthene 3.16E-10 2.35E+00 B2 2 7.4SE- 10 



Gross Alpha 

Page 45 of 64




Gross Beta 

Uranium-238 

Pathway Total 

6.21E-09 


Lead B2 b 

Benzo( a)anthracene B2 b 


Benzo(b)fluoranthene B2 h 





Uranium-238 2.19E-02 5.25E-08 b 1.15E-09 

Pathway Total 

1.15E-09 


Lead 1.lOE-08 B2 



Benzo(b)fluoranthene 1.54E-10 7.30E-01 B2 1.13E- 10 


Phenanthrene 1.9 1E- 10 D 

Gros’s Alpha 

1.02E+01 

Gross Beta 

2.13E+01 

Uranium-238 1.50E+00 6.20E-11 9.28E-11 

Pathway Total 

1.03E-09 


Lead 1.03E- 12 B2 




Benzo(g,h,i)perylene 4.93E-15 D 


Gross Alpha 

9.53E-04 

Gross Beta 

1.99E-03 

Uranium-238 1.40E-04 1.24E-08 1.73E- 12 

Pathway Total 

1.73E-12 

S WMU Total 

8.39E-09 

WAG 7. SWMU 8% ISE-Current Industrial Dermal Contact with Sediment 


Arsenic 

4.96E-07 3.66E+00 A 8 1.81E-06 

Beryllium 


Cobalt 

8.87E-07 26 

Lead 

6.65E-07 B2 26 

Sodium 

7.74E-06 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

2.43E-05 

WAG 7, SWMU 8% ISE-Current Industrial External Exposure to Sediment 

Aluminum 

b 

Arsenic 

A 

b 

Beryllium 

Cobalt 

€32 b 

b 

Lead 

Sodium 

B2 b 

b 

Gross Alpha 

1.04E+O 1 

b 

Gross Beta 

1.72E+O 1 

b 

Uranium-238 

1.25E+00 5.25E-08 b 6.57E-08 

Pathway Total 

6.57E-08 

WAG 7. SWMU 8% ISE-Current Industrial Ingestion of Sediment 

A I u m 111 u m 

2.28E-04 



Cobalt 

8.64E-07 

Page 46 of 64




Lead 6.48E-07 B2 

Sodium 

7.54E-06 

Gross Alpha 

2.75E+02 

Gross Beta 


Uranium-23 8 3.29E+01 6.20E-11 2.04E-09 

Pathway Total 

9.46E-07 

WAG 7, SWMU 8% ISE-Current Industrial Inhalation of Sedlment 

Aluminum 

2.13E-08 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-238 



8.07E-11 

6.05E-11 

7.04E- 10 

6.67E-02 

l.lOE-01 

8.00E-03 

5.00E+01 

8.40E+00 

1.24E-08 

A 

B2 

B2 

b 

b 

2.26E-09 


9.91E-11 

Pathway Total 

- 2 .- 79E-09 .- . 

WAG 7, SWMU 8a, ISW-Current Industrial Dermal Contact with Water 

Aluminum 45 

Antimony 


NA 

Arsenic 

3.31E-08 3.66E+00 A 

Cadmium 

6.65E-08 

B1 

Lead 

9.52E-08 

B2 

Manganese 

3.90E-04 

D 

Silicon 

Sodium 

Sulfate 

Thallium 

NA 

Vanadium 

1.41E-05 

NA 

Methylene Chloride 3.75E-07 7.89E-03 B2 

Gross Alpha 

Gross Beta 

Pathway Total 

S WMU Total 

WAG 7, SWMU 8b, ISO-Current Industrial Dermal Contact with Soil 


Arsenic 

6.78E-07 3.66E+00 A 8 

Beryllium 

1.27E-07 4.30E+02 B2 13, 1 

Cobalt 

1.72E-06 

26 

Lead 

2.12E-06 

B2 26 


1.OZE-05 

Sodium 

1.13E-05 

Thallium 

2.48E-08 

NA 52 

2-Methylnaphthalene 4.3 1E-08 

43 

Aroclor- 1260 

2.73E-08 8.56E+00 B2 46 

Benzo( a)anthracene l.llE-07 2.35E+00 B2 2 


1.06E-07 2,35E+01 B2 2 

Benzo(h)fluoranthene 1.35E-07 2.35E+00 B2 2 

Dibenzofuran 

9.89E-08 

Indeno( 1,2,3-cd)pyrene 8.25E-08 2.35E+00 B2 2 

Naphthalene 

1.07E-07 

D 43 

Phenanthrene 

3.51E-07 

D 2 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-230 

Uranium-234 

Uranium-235 

Uranium-238 

Pathway Total 

WAG 7, SWMU 8b, ISO-Current Industrial External Exposure to Soil 

Aluminum 

b 

Arsenic A b 

Bepllium B2 h 

Page 47 of 64 

7 

8 1.21E-07 

16, 1 

26 

38 

52 

58, 5 

41 2.96E-09 

2.48E-06 

5.45E-05 

2.33E-07 

2.62E-07 

2.49E-06 

3.17E-07 

1.94E-07 

1.24E-07 

6.04E-05 

2.55E-05




Cobalt 

h 

Lead 


Sodium 

Thallium 


Aroclor-1260 




Dibenzofuran 


Naphthalene 

Phenanthrene 

B2 

NA 

B2 

B2 

B2 

B2 

B2 

D 

D 

h 

h 

h 

h 

h 

b 

h 

b 

h 

h 

b 

h 

h 

Gross Alpha 

Gross Beta 

Neptunium-237 


8.35E+01 


b 

b 

b 4.22E-06 

Thonum-230 


b 1.04E-07 

Uranium-234 

1.71E+02 2.14E-11 

b 3.66E-09 

Uranium-235 

3.80E+00 2.65E-07 

h 1.01E-06 

Uranium-238 

2.40E+02 5.25E-08 

b 1.26E-05 

Pathwav Total 

1.79E-05 

WAG 7, SWMU 8b, ISO-Current Industrial Ingestion of Soil 

Aluminum 

1.22E-03 

Arsenic 6.61E-07 1.50E+OO A a 9.9 1 E-07 


Cobalt 

1.68E-06 

Lead 2.06E-06 B2 


9.96E-06 

Sodium 

1.1OE-05 



Aroclor-1260 1.33E-08 7.70E+00 B2 


Benzo(a)pyrene 5.16E-08 7.30E+00 B2 


Dibenzofuran 


Indene( 1,2,3-cd)pyrene 4.02E-08 7.30E-01 B2 


Phenanthrene 1.71 E-07 D 

1 .O2E-07 

3.96E-08 

3.76E-07 


Gross Alpha 

3.1 OE+03 

Gross Beta 5.71 E+03 

Neptunium-237 6.25E+02 3.00E-10 1.88E-07 

Thonum-230 1.63E+OS 3.75E-11 6.09E-06 

Uranium-234 1.17E+04 4.44E- 11 5.19E-07 


Uranium-238 1.64E+O4 6.20E- 11 1.02E-06 

Pathway Total 

WAG 7. SWMU 8h. ISO-Current Industrial Inhalation of Soil 

a 

2.93E-08 

Arsenic 6.17E-11 5.00E+01 A h 3.08E-09 



Lead 1.92E- 10 B2 

Phosphate (ortho) 9.30E- 10 

Sodium 

1.03E-09 



Aroclor- 1260 1.24E- 12 B2 


Benzo(a)pyrene 4.8 1E- 12 B2 


Dibenzofuran 4.5OE- 12 


Page 48 of 64 

9.95E-06


ANALYTE ,- 




Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-230 

Uranium-234 

Uranium-235 

Uranium-238 

Pathway Total 

S WMU Total 

1.60E-11 

2.89E-01 

5.33E-01 

5.84E-02 

1.52E+01 

1.09E+O0 

2.43E-02 

1.53E+00 

3.45E-08 

1.72E-08 

1.40E-08 

1.30E-08 

1.24E-08 

D 

2.0 1E-09 

2.6 1E-07 

1.53E-08 

3.16E- 10 

1.90E-08 



Arsenic 1.08E-06 3.66E+00 A 8 3.95E-06 


Cobalt 3.10E-06 26 

Lead 2.18E-06 B2 26 

Sodium 

2.56E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 1, SWMU 100% FSE-Future Industrial External Exposure to Sediment 

Aluminum 

b 

Arsenic A b 


Cobalt 

b 

Lad B2 b 

Sodium 

b 

Gross Alpha 1.35E+O 1 b 


Uranium238 1.88E+00 5.25E-08 b 9.89E-08 

Pathway Total 


Aluminum 

6.98E-04 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-238 

3.24E-07 1.50E+00 A a 4.86E-07 

4.71E-08 4.30E+00 B2 a 2.03E-07 

9.3 1E-07 

6.53E-07 

B2 

7.67E-06 

9.27EM2 

1.90E+03 

1.29E+02 6.20E-11 8.00E-09 

3.01E-07 

7.15E-05 

9.89E-08 

8.86E-05 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-238 

3.02E-11 5.00E+01 A b 1.51E-09 

4.40E-12 8.40E+00 B2 b 3.70E-11 

8.69E-11 

6.10E-11 

B2 

7.16E-10 

8.66E-02 

1.77E-01 

1.20E-02 1.24E-08 1.49E- 10 

Pathway Total 


Aluminum 475 

Cadmium 1.21E-06 B1 16, 1 

Cobalt 26 

Lead 1.42E-06 B2 26 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

1.70E-09 

Page 49 of 64


SLQPE OF SF SPECIFIC PATHWAY EXPOSUR 


Uranium-238 

Pathway Total 

S W MU Total 

7.23E-05 



Arsenic 9.84E-07 3.66E+00 A 8 3.60E-06 


Cobalt 1.57E-06 26 

Lead 1.91E-06 B2 26 

Sodium 

2.39E-05 

Gross Alpha 

Gross Beta 

Uranium-235 

Uranium-238 

Pathway Total 

5.57E-05 

WAG 1, SWMU 100b, FSE-Future Industrial External Exposure to Sediment 

Aluminum 

b 

Arsenic A b 


Cobalt 

b 

Lead B2 b 

Sodium 

b 



Uranium23 5 2.00E+00 2.65E-07 b 5.31E-07 

Uranium-238 6.05E+00 5.25E-08 b 3.18E-07 

Pathway Total 

8.49E-07 


Aluminum 

5.44E-04 



Cobalt 


Lead 5.74E-07 B2 

Sodium 

7.16E-06 

Gross Alpha 

1.45E+03 

Gross Beta 

2.34E+03 

Uranium-235 1.37E+02 4.70E- 11 6.44E-09 


Pathway Total 

6.31E-07 

WAG 1, SWMU IOOb, FSE-Future Industrial Inhalation of Sediment 

Aluminum 

5.08E-08 

Arsenic 

2.76E-11 5.00E+01 A b 1.38E-09 

Beryllium 

3.39E-12 8.40E+00 B2 b 2.85E-11 

Cobalt 

Lead 


5.35E-11 

B2 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-235 

6.68E-10 

1.36E-01 

2.18E-01 

1.28E-02 1.30E-08 1.66E-10 

Uranium-238 

3.87E-02 1.24E-08 4.80E- 10 

Pathway Total 

2 -. 135~49 -.- - - 

WAG 1. SWhfLJ IOOb, FSW-Future Industrial Dermal Contact with Surfacewater 


Arsenic 

1.27E-07 3.66E+00 A 8 4.65E-07 

Lead 

2.46E-06 B2 26 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-234 

Uranium-235 

Uranium-238 

Pathwav Total 


SWLIUTotal 

5.76E-05 

M’AG 1. SWMU 1OOc. FGW-Future Industrial Dermal Contact with Groundwater 

Page 50 of 64




Aluminum 

4s 



Methylene Chloride 4.58E-07 7.89E-03 B2 41 3.62E-09 

bis(2-Ethylhexyllphthalate 9.55E-07 7.37E-02 B2 15 7.04E-08 

Gross Alpha 

Gross Beta 

Pathway Total 

7.40E-08 

WAG 1, SWMU lOOc, FGW-Future Industrial Ingestion of Groundwater 

Aluminum 





bis(2-Ethylhexy1)phthalate 6.99E-06 1.40E-02 B2 a 9.78E-08 

Gross Alpha 

2.65E+04 

Gross Beta 


Pathway Total 

2.29E-07 

WAG 1, SWMU lOOc, FGW-Future Industrial Inhalation of Groundwater 

Aluminum 

Barium 

NA 

Manganese 

D 

Methylene Chloride l.82E-06 B2 


B2 

Gross Alpha 

Gross Beta 

Pathway Total 

WAG 1, SWMU lOOc, FSO-Future Industrial Dermal Contact with Soil 


Arsenic 8.06B07 3.66E+00 A 8 2.95E-06 


Cobalt 1.14E-06 26 

Lead 1.67E-06 B2 26 

Sodium 

5.38E-05 


2-Methy Inaphthalene 8.48E-08 43 


2.08E-08 

Endosulfan Sulfate 2.83E-10 

Endrin Ketone 

2.92E-10 



Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-238 

Pathway Total 

3.39E-05 

WAG 1, SWMU lOOc, FSO-Future Industrial External Exposure to Soil 

Aluminum 

b 

Arsenic A b 


Cobalt 

b 

Lead BZ b 

Sodium 

b 

Thallium NA b 

?.-Methylnaphthalene 

b 


b 


b 

Endrin Ketone 

b 


Phenanthrene 

D b 

Gross Alpha 

1.43E41 b 

Gross Beta 2.27E41 b 

Neptunium-237 

1.5 1E-01 4.62E-07 b 6.96E-08 

'Ihorium-228 

1.33E40 9.94E-07 b 1.32E-06 

Page 51 of 64




Uranium-238 1.30E+00 5.25E-08 b 6.81E-08 

Pathway Total 

1.46E-06 

WAG 1, SWMU IOOc, FSO-Future Industrial Ingestion of Soil 

Aluminum 


Arsenic 

2.42E-07 1.50E+00 A a 3.63E-07 

Beryllium 


Cobalt 

Lead 

Sodium 

Thallium 




Endrin Ketone 

Naphthalene 

Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-238 

3.41 E-07 

5.00E-07 

1.61E-05 

2.75E-09 

1.27E-08 

3.11E-09 



7.69E-09 

2.11E-08 

9.80E+02 

1.55E+03 

1.03E+01 

9.08E+01 

8.88E+01 

3.00E-10 

2.3 1E-10 

6.20E-11 

B2 

NA 

D 

D 

3.09E-09 

2.10E-08 

5.51E-09 

Pathwav Total 


WAG 1, SWMU lOOc, FSO-Future Industrial Inhalation of Soil 

Aluminum 

3.78E-08 

Arsenic 2.26E-I 1 5.00E+01 A b 1.13E-09 


Cobalt 

3.19E-11 


Sodium 1.51E-09 




2.91E-13 

Endosulfan Sulfate 3.96E- 15 

Endrin Ketone 4.09E- 15 


Phenanthrene 

1.97E-12 



Neptunium-237 9.63E-04 3.45E-08 3.32E-11 

Thorium-228 8.48E-03 9.68E-08 8.2OE- 10 

Uranium-238 8.29E-03 1.24E-08 1.03E-10 

Pathway Total 

SWMU Total 

WAG 1, SWMU 136, FGW-Future Industrial Dermal Contact with Groundwater 




bis(2-Ethylhexy1)phthalate 4.78E-07 7.37E-02 B2 I5 3.52E-08 

Gross Alpha 

Gross Beta 

Pathway Total 

WAG 1. SWMU 136, FGW-Future Industrial Ingestion ofGroundwater 

Banum 1.15E-03 NA 


Trichloroethene 3.84E-04 1.1OE-02 NA e 4.23E-06 

bis(2-Ethylhexy1)phthalate 3.49E-06 1.40E-02 B2 a 4.89E-08 

Gross Alpha 

1.94E+04 

Gross Beta 

5.00E+04 

Pathway Total 

WAG 1. SWMU 136, FGW-Future Industrial Inhalation of Groundwater 

Barium 

NA 

Manganese 

D 

Trichloroethene 4.00E-05 6.00E-03 NA e 2.40E-07 


B2 

D 

D 

Page 52 of 64 

2.1 OE-09 

2.64E-06 


3.61E-05




Gross Alpha 

Gross Beta 

Pathway Total 

2.40E-07 



Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Sulfate 

Thallium 









Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-23 8 

2.04E-08 

2.54E-09 

5.83E-08 


1.59E-06 


3.43E-10 


3.08E- 10 

2.23E-09 

2.38E-09 

2.49E-09 

2.10E-09 

8.30E-10 

2.15E-09 

8.10E- 10 

6.00E-01 

2.35E+00 

2.35E+01 

2.35E+00 

A 

B2 

BZ 

NA 

D 

C 

B2 

B2 

BZ 

D 

BZ 

B2 

D 

8 

13, 1 

26 

26 

52 

55 

31 

2 

2 

2 

2 

2 

2 

2 

7.45E-08 

1.09E-06 

1.85E-10 

5.25E-09 

5.60E-08 

5.86E-09 

1.96E-08 

5.06E-09 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Sulfate 

Thallium 









Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

4.1 1E-0 1 

5.98E-01 

3.24E-02 

5.25E-08 

A 

BZ 

B2 

NA 

D 

C 

BZ 

B2 

B2 

D 

B2 

B2 

D 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

1.70E-09 

Arsenic 6.11E-09 1.50E+00 A a 9.16E-09 

Beryllium 7.63E-10 4.30E+00 BZ a 3.28E-09 

Cobalt 

1.75E-08 

Lead 1.31E-08 B2 

Sodium 


Sulfate 

1.49E-06 


1,1,1 -Trichloroethane 2.85E-11 D 

1,1 -Dichloroethene 1.85E-11 6.00E-01 C a 1.11E- 11 

Benzo(a)anthracene 3.34E-10 7.30E-01 BZ 2.44E- 10 


Benzo(b)fluoranthene 3.73E-10 7.3OE-01 B2 

2.73E- 10 


Dibenzo(a,h)anthracene 1.25E-10 7.30E+00 B2 9.09E-10 

Indeno( 1,2,3-cd)pyrene 3.22E-10 7.3OE-01 BZ 2.35E-10 

Page 53 of 64






Gross Beta 4.09E+O 1 

Uranium-238 2.22E+00 6.20E-11 1.38E- 10 

Pathway Total 


1.69E-08 

Aluminum 

1.59E-09 

Arsenic 5.70E-13 5.00E+01 A b 2.85E-11 



Lead 1.22E-12 B2 

Sodium 


Sulfate 

1.40E-10 


I,], 1 -Trichloroethane 6.79E-10 D 

1,l-Dichloroethene 1.17E-09 1.20E+00 C b 1.40E-09 





Dibenzo(a,h)anthracene 1.16E-14 B2 



Gross Alpha 

2.62E-03 

Gross Beta 

3.82E-03 

Uranium-238 2.07E-04 1.24E-08 

2.57E- 12 

Pathway Total 

S WMU Total 

1.44E-09 

8.44E-06 

WAG 1, SWMU 38a, FSE-Future Industrial Dermal Contact with Sediment 



Cobalt 1.91E-06 26 

Lead 1.74E-06 B2 26 

Sodium 

7.86E-06 



Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


1.30E-04 

Aluminum 

b 

Beryllium 

B2 b 

Cobalt 

b 

Lead B2 b 

Sodium 

b 

Vanadium NA b 




Uranium-238 3.87E+00 5.25E-08 b 2.03E-07 

Pathway Total 


2.03E-07 

Aluminum 

2.61E-04 

Beryllium 


Cobalt 

5.74E-07 

Lead 

5.22E-07 

B2 

Sodium 

2.36E-06 

Vanadium 

5.52E-06 

NA 

Phenanthrene 

5.68E-09 

D 

Gross Alpha 

8.46E+02 

Gross Beta 

l.llE+03 

Uranium-238 

2.65E+02 6.20E-I 1 1.64E-08 

Pathway Total 


Page 54 of 64





Aluminum 

2.44E-08 

Beryllium 

8.48E-12 8.40E+00 BZ b 7.13E-11 

Cobalt 

Lead 

5.35E-11 


B2 

Sodium 

Vanadium 

2.20E-10 

5.15E- 10 

NA 

Phenanthrene 

5.30E-13 

D 

Gross Alpha 

Gross Beta 

Uranium-238 

7.90E-02 

1.03E-01 

2.47E-02 1.24E-08 3.07E- 10 



Arsenic 9.99E-08 3.66E+00 A 8 3.66E-07 

Lead 5.18E-07 B2 26 

Sodium 

Chloroform 3.24E-06 3.05E-02 B2 24 9.89E-08 

bis(2-Ethylhexyl)phthalate 4.23E-06 7.37E-02 B2 I5 3.12E-07 

Gross Alpha 

Gross Beta 

Uranium-238 

' Pathway ~otal 

7.76E-07 

S WMU Total 

1.32E-04 



Arsenic 6.81E-07 3.66E+00 A 8 2.49E-06 


Cobalt 1.27E-06 26 

Lead 3.45E-06 B2 26 

Sodium 

1.33E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


WAG 1, SWMU 38b, FSE-Future Industrial External Exposure to Sediment 

Aluminum 

h 

Arsenic A h 


Cobalt 

b 

Lead B2 b 

Sodium 

h 

Gross Alpha 1.47E+O 1 b 


Uranium-238 3.07E+00 5.25E-08 b 1.61E-07 

Pathway Total 

1.61E-07 


Aluminum 

5.04E-04 

Arsenic 2.04E-07 1.50E+00 A a 3.07E-07 


Cobalt 

3.80E-07 

Lead 1.03E-06 B2 

Sodium 


Gross Alpha 

1 .O IE+03 

Gross Beta 

2.13E+03 

Uranium-238 2.10E+02 6.20E-11 1.30E-08 

Pathway Total 


WAG 1. SWMU 38h, FSE-Future Industrial Inhalation of Sediment 

Alummum 


Arsenic 1.91E-11 5.OOE+01 A b 9.54E-10 


Cobalt 

3.55E-11 

Lead 9.65E-11 B2 


Gross Alpha 

9.39E-02 

Page 55 of 64





Uranium-238 1.96E-02 1.24E-08 2.43E-10 

~~ 

Pathway Total 

1.22E-09 

WAG 1, SWMU 38b, FSW-Future Industrial Dermal Contact with Surfacewater 


Sodium 

Gross Alpha 

Gross Beta 

Neptunium-237 

Plutonium-238 

Uranium-234 

Uranium-238 

Pathway Total 

S WMU Total 


WAG 1. SWMU 38c. FGW-Future Industrial Dermal Contact with Groundwater 



Gross Beta 

Pathway Total 

WAG 1, SWMU 38c, FGW-Future Industrial Ingestion of Groundwater 

Banum 1.02E-03 NA 


Methylene Chloride 4.54E-04 7.50E-03 B2 a 3.41E-06 

Gross Beta 

2.41E+04 

Pathway Total 

WAG 1, SWMU 38c, FGW-Future Industrial Inhalation of Groundwater 

Barium 

NA 

Manganese 

D 

Methylene Chloride 4.73E-05 E2 

Gross Beta 

Pathway Total 

WAG 1, SWMU 38c, FSO-Future Industrial Dermal Contact with Soil 


Arsenic 

3.14E-06 3.66Ei-00 A 8 1.15E-05 

Beryllium 


Cobalt 

5.04E-06 

26 

Lead 

7.39E-06 

B2 26 

Sodium 

1.06E-04 

llallium 

6.35E-08 

NA 52 

2-Hexanone 

2.68E-08 

36 

Aroclor- 1260 

4.27E-08 8.56E+00 B2 46 3.65E-07 

Benzo( a)anthracene 1.6 IE-07 2.35E+00 B2 2 3.79E-07 


1.39E-07 2.35E+01 B2 2 3.28E-06 

Benzo(b)fluoranthene 2.04E-07 2.35E+00 B2 2 4.79E-07 

Phenanthrene 

2.71E-07 

D 2 

Gross Alpha 

Gross Beta 

Neptunium-237 

llorium-228 

Uranium-235 

Uranium-238 

Pathwav Total 

WAG 1. SWMU 38c. FSO-Future Industrial External Exoosure to Soil 

9.40E-08 

3.41E-06 

1.41E-04 

Arsenic 

A b 

Beryllium 

Cobalt 

B2 b 

b 

Lead 

B2 b 

Sodium 

b 

Thallium NA b 

2-Hexanone 

b 

Aroclor- 1260 B2 b 

Benzo( a)anthracene B2 h 

Page 56 of 64


WERiH'I. ANAL- IdTAL- 




Benzo(bfflu0ranthene B2 h 


Gross Alpha 6.34E+01 h 

Gross Beta 8.75E+01 h 

Neptunium-237 5.56E+00 4.62E-07 h 2.57E-06 

Thorium-228 4.67E+00 9.94E-07 h 4.64E-06 

Uranium-235 1.02E+00 2.65E-07 h 2.69E-07 

Uranium-238 1.80E+01 5.25E-08 h 9.43E-07 

Pathway Total 

8.42E-06 

WAG 1, SWMU 38c, FSO-Future Industrial Ingestion of Soil 

Alummum 

1.46E-03 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Thallium 

2-Hexanone 

Aroclor-1260 




Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-23 5 

Uranium-238 

9.41E-07 

8.75E-08 

1.5 1E-06 

2.22E-06 

3.19E-05 

1.91E-08 

1.61E-09 

6.41E-09 

2.41E-08 

2.09E-08 

3.05E-08 



5.99E+03 

3.80E+02 

3.20E+02 

6.95E+01 

1.23E+03 

1.50E+00 

4.3 OE+OO 

7.70E+00 

7.30E-01 

7.30E+00 

7.30E-01 

3.00E-10 

2.31E- 10 


6.20E-11 

A 

B2 

B2 

NA 

B2 

B2 

B2 

B2 

D 

Pathway Total 

WAG 1. SWMU 38c, FSO-Future Industrial Inhalation of Soil 

Aluminum 

1.37E-07 

Arsenic 

8.79E-11 5.00E+01 

Beryllium 

8.17E-12 8.40E+00 

Cobalt 

1.41E-10 

Lead 

2.07E- 10 

B2 

Sodium 

2.98E-09 

Thallium 

1.78E-12 

NA 

2-Hexanone 

1.50E- 13 

Aroclor-1260 

5.98E-13 

B2 

Benzo(a)anthracene 2.25E-12 

B2 


1.9SE-12 

B2 

Benzo(b)fluoranthene 2.8SE-12 

B2 

Phenanthrene 

3.80E-12 

D 

Gross Alpha 

4.OSE-01 

Gross Beta 

5.59E-01 

Neptunium-237 

3.5SE-02 3.45E-08 

Thorium-228 

2.98E-02 9.68E-08 

Uranium-23 5 

6.49E-03 1.30E-08 

Uranium-23 8 

1.15E-01 1.24E-08 

Pathway Total 

a 

a 

a 

1.41E-06 

3.76E-07 


1.76E-08 

1.53E-07 

2.23E-08 

1.14E-07 

7.39E-08 

3.27E-09 

7.62E-08 

A h 4.39E-09 

B2 h 6.87E-11 

1.23E-09 

2.89E-09 

8.44E-11 

1.42E-09 

s WMU ~otai 


Lead 2.19E-08 B2 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 7, SWMU 130. FSO-Future Industrial External Exposure to Soil 

Lead B2 b 

Gross Alpha 1 .OOE-01 h 

Gross Beta 2.55E-0 1 h 

Uranium-23 8 1.55E-02 5.25E-08 h 8.12E-10 

Page 57 of 64 

2.30E-06 

1.01E-08 

1.56E-04



Gross Alpha 

6.87E+00 

Gross Beta 

1.74E+01 

Uranium-238 1.06E+00 6.20E-11 6.56E-11 

Gross Alpha 

6.41E-04 

Gross Beta 

1.63E-03 

Uranium-238 9.88E-05 1.24E-08 

1.23E-12 

Pathway Total 

1.23E-12 

SWMU Total 


Lead 4.17E-09 B2 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

WAG 7, SWMU 131, FSO-Future Industrial External Exposure to Soil 

Lead B2 h 


Gross Beta 3.02E-02 h 

Uranium-238 1.91E-03 5.25E-08 h 1.00E-10 

Pathway Total 1 .OOE- 10 


Lead 1.25E-09 B2 

Gross Alpha 

1.41Ei-00 

Gross Beta 

2.07E+00 

Uranium-238 1.31E-01 6.20E-11 8.09E- 12 

Pathway Total 

8.09E-12 


Lead 1.17E- 13 B2 

Gross Alpha 

1.31E-04 

Gross Beta 

1.93E-04 

Uranium-238 1.22E-05 1.24E-08 1.51 E- 13 

Pathway Total 1.51 E- 13 

S WMU Total 

WAG 7, SWMU 132. FSO-Future Industrial Dermal Contact with Soil 

Lead 3.42E-07 B2 26 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Lead B2 h 

Gross Alpha 

2.80E-01 

h 

Gross Beta 


h 

Uranium-238 3.30E-02 5.25E-08 

h 1.73E-09 

Pathway Total 

1.73E-09 


Lead 1 .O2E-07 B2 


Gross Beta 

3.34E+01 

Uranium-238 2.26E+00 6.20E-11 1.40E- 10 

Pathway Total 

1.40E-10 

WAG 7, SWMU 132. FSO-Future Industrial Inhalation of Soil 

Lead 9.57E- 12 B2 

Gross Alpha 

1.79E-03 

Gross Beta 

3.12E-03 

Uranium-238 2.11E-04 1.24E-08 2.62E-12 


SWMU Total 

8.79E-10 

1.08E-10 

1.88E-09 

Page 58 of 64





Lead 3.96E-07 B2 26 







Dibenzo(qh)anthracene 


Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

2.87E-09 

2.15E-08 

1.62E-08 

1.74E-08 

9.59E-09 

1.45E-08 

1.19E-09 

7.95E-09 

1.94E-08 

2.35E+00 

2.35E+01 

2.35E+00 

2.35E-01 

2.35E+01 

2.35E+00 

B2 

B2 

B2 

D 

B2 

B2 

B2 

D 

2 

2 5.06E-OR 

2 3.80E-07 


2 

2 3.42E-09 

2 2.79E-08 

2 1.87E-08 

2 


Lead B2 b 


b 





Benzo(k)fluoranthene B2 b 

Dibenzo(qh)anthracene B2 b 



Gross Alpha 3.72E-0 1 b 

Gross Beta 4.36E-01 b 

Uranium-238 2.94E-02 5.25E-08 b 1.54E-09 

Pathway Total 


Lead 1.19E-07 B2 






1.90E-09 


Benzo(k)fluoranthene 2.18E-09 7.30E-02 B2 1.59E- 10 

Dibenzo(a,h)anthracene 1.78E-10 7.30E+00 B2 1.30E-09 

Indeno( 1,2,3-cd)pyrene I. 19E-09 7.30E-0 1 B2 8.71E-10 


Gross Alpha 2.55E+01 

Gross Beta 

2.98E+Ol 

Uranium-238 2.01E+00 6.20E-11 1.25E-10 

Pathway Total 


Lead 1.11E- 11 B2 

Acenaphthylene 4.01E-14 





Benzo(k)fluoranthene 2.03E-13 B2 

Dibenzo(a,h)anthracene 1.66E-34 B2 

Indeno( 1,2,3-~d)pyrene 1.llE-13 B2 


Gross Alpha 

2.38E-03 

Gross Beta 

2.79E-03 

Uranium-238 1.88E-04 1.24E-08 2.33E-12 

Pathway Total 

SWMU Total 


Lead 6.36E-08 B2 26 


Page 59 of 64 

5.22E-07 

1.54E-09 

2.44E-08 

2.33E-12 

5.48E-07






Benzo(g,h,i)perylene 3.62E- 10 D 2 


Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

2.03E-08 


Lead B2 b 





Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

2.85E-01 

3.22E-01 

2.19E-02 

5.25E-08 

BZ 

B2 

BZ 

D 

D 


Lead 1.91E-08 B2 





Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

5.43E-11 

2.47E-10 

D 

D 

b 

b 

b 

b 

b 

b 

b 

b 

1.15E-09 

l.lOE-10 7.30E-01 B2 8.04E-11 

1.03E-10 7.30E+00 B2 a 7.50E- 10 

1.53E-10 7.3OE-01 B2 1.12E- 10 

1.95E+01 

2.21E+01 

1.50E+00 6.20E-11 9.28E-11 

1.15E-09 





Phenanthrene 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

1.03E- 14 

BZ 

9.59E-15 

B2 

1.43E- 14 

B2 

5.07E-15 

D 

2.30E-14 

D 

1.82E-03 

2.06E-03 

1.40E-04 1.24E-08 1.73E- 12 

S WMU Total 


Alummum 7.61E-04 4.5 

Arsenic 1.61E-06 3.66E+00 A 8 5.89E-06 


Cobalt 2.88E-06 26 

Lead 2.16E-06 B2 26 

Sodium 

2.51E-05 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 


Aluminum 

b 

Arsenic A b 


Cobalt 

b 

Lead BZ b 

Sodium 

b 

Gross Alpha 

1.04E+O 1 

b 

Gross Beta 

1.72E+O 1 

b 

Uranium-238 

1.25E+00 5.25E-08 

b 6.57E-08 

Pathway Total 

Page 60 of 64 

1.73E-12 

7.90E-05 

6.57E-08 

2.24E-08





Aluminum 

2.28E-04 

Arsenic 

Beryllium 

Cobalt 

Lead 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-238 

Pathway Total 

4.83E-07 1.5OE+00 A a 7.25E-07 

5.10E-08 4.30E+00 BZ a 2.19E-07 

8.64E-07 

6.48E-07 

B2 

7.54E-06 

7.15E+02 

l.l8E+03 

8.56E+01 6.20E-11 5.31E-09 

~~ 

9.49E-07 


Aluminum 

2.13E-08 

Arsenic 

4.51E-11 5.00E+01 A b 2.26E-09 

Beryllium 

4.76E-12 8.40E+00 B2 b 4.00E-11 

Cobalt 

Lead 

8.07E-11 

6.OSE-11 

B2 

Sodium 

Gross Alpha 

Gross Beta 

Uranium-238 

7.04E-10 

6.67E-02 

1.lOE-01 

8.00E-03 1.24E-08 9.91E-11 

Pathway Total 

2.39E-09 


Aluminum 495 

Antimony 1.53E-06 NA 7 

Arsenic 1.08E-07 3.66E+00 A 8 3.94E-07 

Cadmium 2.16E-07 B1 16, 1 

Lead 3.09E-07 B2 26 


Silicon 

Sodium 

Sulfate 

Thallium NA 52 

Vanadium 4.58E-05 NA 58, 5 


Gross Alpha 

Gross Beta 

Pathway Total 


S WMU Total 

WAG 7, SWMU 8b, FGW-Future Industrial Dermal Contact with Groundwater 

Aluminum 

4s 


Cobalt 26 

Iron 26 


Nickel 1.34E-OS NA 44 

Silica 

Silicon 

Sulfate 

Sulfide 

1, I-Dichloroethene 1.82E-06 6.00E-0 1 C 31 1.09E-06 

1,2-Dichloroethene 3.35E-06 NA 



Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Uranium-234 

Uranium-235 

Uranium-238 

Pathwav Total 4.68E-04 

WAG 7, SWMU 8b, FGW-Future Industrial Ingestion of Groundwater 

Alummum 

1.69E-01 

Page 61 of 64 

8.04E-05





Cobalt 

Iron 

Manganese 

Nickel 

Silica 

Silicon 

Sulfate 

Sulfide 


2.98E-03 


8.73E-02 

2.29E-03 

1.75E+00 


2.78E+00 

8.39E-03 

3.39E-05 6.00E-01 

D 

NA 

C a 2.03E-05 


Phenanthrene 


5.34E-04 

3.49E-06 

1.86E-05 1.1OE-02 

NA 

D 

NA e 2.05E-07 

Gross Alpha 

Gross Beta 

Neptunium-237 

9.55E+04 


1.48E+04 3.00E-10 


Thorium-228 


1.13E-06 

Uranium-234 


3.68E-06 

Uranium-235 


3.27E-07 

Uranium-238 

1.75E+05 6.20E-11 

1.08E-05 

Pathway Total 

8.35E-04 

WAG 7, SWMU 8b, FGW-Future Industrial Inhalation of Groundwater 

Aluminum 

Beryllium 

Cobalt 

Iron 

Manganese 

Nickel 

Silica 

Silicon 

Sulfate 

Sulfide 



Phenanthrene 


Gross Alpha 

Gross Beta 

Neptunium-237 

Tkonum-228 

Uranium-234 

Uranium-235 

Uranium-238 

Pathway Total 

8.40E+00 B2 b 

D 

NA 

3.53E-06 1.20E+00 C 

NA 

D 

1.94E-06 6.00E-03 NA 

3.45E-08 

9.68E-08 

1.40E-08 

1.30E-08 

1.24E-08 

b 

e 


1.16E-08 

WAG 7, SWMU 8b, FSO-Future Industrial Dermal Contact with Soil 


Arsenic 2.36E-06 3.66E+00 A 8 8.62E-06 

Beryllium 4.05E-07 4.30E+02 B2 13, 1 1.74E-04 


Lead 5.8OE-06 B2 26 


3.32E-05 

Sodium 

6.33E-05 



Aroclor-1260 3.33E-08 8.56E+00 B2 46 2.85E-07 

Benzo( a)anthracene 2.01E-07 2.35E+00 B2 2 4.74E-07 

Benzo(a)p yrene 2.93E-07 2.35E+01 B2 2 6.89E-06 

Benzo@)fluoranthene 3.31E-07 2.35E+00 B2 2 7.79E-07 

Dibenzofuran 

2.87E-07 




Gross Alpha 

Gross Beta 

Page 62 of 64 


~~ 




Neptunium-237 

Thorium-228 

Thorium-230 

Uranium-235 

Uranium-238 

Pathway Total 

1.92E-04 

WAG 7, SWMU 8b, FSO-Future Industrial External Exposure to Soil 

Aluminum 

b 

Arsenic 

Beryllium 

Cobalt 

Lead 


Sodium 

Thallium 

2-Meth ylnaphthalene 

Aroclor-1260 




Dibenzokan 


Naphthalene 

Phenanthrene 

A 

BZ 

BZ 

NA 

BZ 

BZ 

BZ 

B2 

BZ 

D 

D 

b 

b 

b 

b 

h 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

b 

Gross Alpha 

Gross Beta 

Neptunium-237 


8.05E+O 1 


b 

h 

b 4.22E-06 

Thorium-228 

5.11E+00 9.94E-07 

b 5.08E-06 

Thorium-230 


b 1.04E-07 

Uranium-23 5 

8.81E-01 2.65E-07 

b 2.33E-07 

Uranium-238 

1.73E+01 5.25E-08 

b 9.09E-07 

Pathway Total 

1.05E-05 

XAti 7, SWMU 8b, FSO-Future Industrial Ingestion of Soil 

Aluminum 

1.90E-03 

Arsenic 

Beryllium 

Cobalt 

Lead 


Sodium 

Thallium 


Aroclor- 1260 




Dibenzofuran 


Naphthalene 

Phenanthrene 

Gross Alpha 

Gross Beta 

Neptunium-237 

Thorium-228 

Thorium-230 

Uranium-235 

Uranium-238 

7.07E-07 

1.22E-07 

1.35E-06 

1.74E-06 

9.96E-06 

1.90E-05 

2.70E-08 

2.10E-08 

5.00E-09 

3.02E-08 







3.28E+03 

5.5 1E+03 

6.25E+02 

3.5OE+02 

1.63E+05 

6.03E+01 

1.18E+03 

1.50E+00 


7.70E+00 

7.30E-01 

7.30E+00 

7.30E-01 

7.30E-01 

3.00E- 10 

2.31E-10 

3.75E-11 


6.20E-11 

A 

B2 

BZ 

NA 

BZ 

BZ 

BZ 

B2 

BZ 

D 

D 

a 

a 

a 

1.06E-06 

5.23E-07 

3.85E-08 

2.20E-08 

3.20E-07 

3.62E-08 

2.93E-08 

1.88E-07 

8.09E-OR 

6.09E-06 

2.83E-09 

7.35E-08 

8.47E-06 

Arsenic 

Beryllium 

Cobalt 

bad 

6.60E-11 5.OOE+01 A b 3.30E-09 

1.14E-11 8.40E+00 B2 b 9.54E-3 1 

1.26E- 10 

1.62E-10 

B2 

Page 63 of 64





9.30E-10 

Sodium 

1.77E-09 


2-Methylnap hthalene 1.96E-12 

Aroclor- 1260 4.66E-13 B2 


Benzo(a)pyrene 4.10E-12 B2 

Benzo(b)fluoranthene 4.63E-12 BZ 

Dibenzofuran 


Indene( 1,2,3-cd)pyrene 3.75E-12 BZ 



Gross Alpha 

3.07E-01 

Gross Beta 5.14E-0 1 

Neptunium-237 5.84E-02 3.45E-08 2.01E-09 

Thorium-228 3.27E-02 9.68E-08 3.16E-09 

Thorium-230 

1.52E+01 1.72E-08 2.61E-07 

Uranium-235 5.63E-03 1.30E-08 7.32E-11 

Uranium-238 1.llE-01 1.24E-08 1.37E-09 

Pathway Total 

2.71E-07 

S WMU Total 

1.52E-03 

Page 64 of 64

Appendix L.8 

Chemicals of Concern

mnmsuMMARyFo~ 

ANTIMONY 

DECEMBER 1992 

Prepared by 

Robert k Young, PbD., D.kB.T. 

Chemical Hazard Evaluation and Communication Group 

Biomedical and Environmental Information Analysis Section 

Health and Safety Research Division 

Oak Ridge National hboratory* 


Prepared for 

OAK RIDGE RESERVATION ENVIRONMENTAL 

RESTORATION PROGRAM 

*Managed by Martin Marietta Energy Systems, Inc., for the U.S. Department of Energy 

under Contract No. DE-ACO5-840FU1400

ntis page intentionally le/t blank

EXECUTIVESUMMARY 

Antimony (Sb) is a naturally occurring metal that is used in various manufacturing 

processes. It exists in valence states of 3 and 5 (Budavari, 1989; ATSDR. 1990). Antimony 

is a common urban air pollutant (Beliles, 1979). Exposure to antimony may be via inhalation, 

oral and dermal routes (ATSDR, 1990). 

Antimony is sparingly absorbed following ingestion or inhalation (Felicetti et al., 1974a; 

Gerber et al., 1982, ATSDR, 1990). Both gastrointestinal and pulmonary absorption are a 

function of compound solubility. Antimony is transported in the blood, its distribution varying 

among species and dependent on its valence state (Felicetti et al., 1974b). Antimony is not 

metabolized but may bind to macromolecules and react covalently with sulfhydryl and 

phosphate groups (A’ISDR, 1990). Excretion of antimony is primarily via the urine and feces, 

and is also dependent upon valence state (Cooper et aL, 1%8, Ludersdorf et aL, 1987; 

ATSDR, 1990). 

Acute oral exposure of humans and animals to high doses of antimony or antimonycontaining 

compounds (antimonials) may cause gastrointestinal disorders (vomiting, diarrhea), 

respiratory difficulties, and death at extremely high doses (Bradley and Frederick, 1941; 

Beiiles, 1979; ATSDR, 1990). Subchronic and chronic oral exposure may affect hematologic 

parameters (ATSDR, 1990). Long-term exposure to high doses of antimony or antimonials 

has been shown to adversely affect longevity in animals (Schroeder et al., 1970). Limited data 

suggest that prenatal and postnatal exposure of rats to antimony interferes with vasomotor 

responses (Marmo et aL, 1987; Rossi et aL, 1987). 

Acute inhalation exposure of humans may cause gastrointestinal disorders (probably due 

to ingestion of airborne antimony) (AISDR 1990). Exposure of animals to high 

concentrations of antimony and antimonials (especially stibine gas) may result in pulmonary 

edema and death (Price et ai., 1979). Long-term occupational exposure of humans has 

resulted in electrocardiac disorders, respiratory disorders, and possibly increased mortality 

(Renes, 1953; Breiger et ai., 1954). Antimony levels for these occupational exposure 

evaluations ranged from 2.2 to 11.98 mg Sb/m3. Based on limited data, occupational exposure 

of women to metallic antimony and several antimonials has reportedly caused alterations in 

the menstrual cycle and an increased incidence of spontaneous abortions (Belyaeva, 1967). 

Reproductive dysfunction has been demonstrated in rats exposed to antimony trioxide 

(Beiyaeva, 1967). 

No data were available indicating that dermal exposure of humans to antimony or its 

compounds results in adverse effects. However dermal application of high doses of antimony 

oxide (1,584 mg Sbkg) resulted in the death of rabbits within one day (IBTL, 1972). Eye 

irritation due to exposure to stibine gas and several antimony oxides has been reported for 

humans (Stevenson. 1965; Potkonjak and Pavlovich, 1983). 

The U. S. EPA (U.S. EPA, 1991, 1992) has calculated subchronic and chronic oral 

reference doses (RfDs) of 4E-4 mg/kg/day based on decreased longevity and alteration of 

blood chemistry in rats chronically exposed to potassium antimony tartrate in the drinking , 

water (5 ppm equivalent to 0.35 mg Sb/kg/day). An uncertainty factor of LOO0 was applied: 

10 for extrapolation from a lowest-obsented-adverse-effect-level (LOAEL) to a no-observed- 

1

adverse-effect-level (NOAEL), 10 for extrapolation from animal data, and 10 €or protection 

of sensitive populations. 

The primary target organ €or acute oral exposure to antimony appears to be the 

gastrointestinal tract (irritation, diarrhea, vomiting) and targets for long-term exposure are the 

blood (hematological disorders) and liver (mild hepatotoxicity) (ATSDR, 1990). Inhalation 

exposure to antimony affects the respiratory tract (pneumoconiosis, restrictive airway 

disorders), with secondary targets being the cardiovascular system (altered blood pressure and 

electrocardiograms) and kidneys (histological changes) (Renes, 1953; Breiger et al., 1954). 

Only limited evidence exists €or reproductive disorders due to antimony exposure (Belyaeva, 

1967). 

Although some data indicate that long-term exposure of rats to antimony trioxide and 

trisulfide increased the incidence of lung tumors (Wong et al, 1979; Watt, 1980, Groth et aL, 

1986; Bio/dynamics, lw), the U.S. EPA has not evaluated antimony or antimonials for 

carcinogenicity and a Weight*€-Evidence classification is currently unavailable. 

2

1. INTRODUCTION 

Antimony (CAS No. 7440-36-0) is a naturally occumng metalloid element (displaying 

both metallic and nonmetallic properties) existing in valence states of 3 and 5 (Budavari, 

1989, ATSDR, 1990). Metallic antimony and a few trivalent antimony compounds are the 

most significant regarding exposure potential and toxicity (ATSDR, 1990). Antimony (Sb) 

is used in metallurgical processes, paints and enamels, various textiles, rubber, and fire 

retardation (antimony trioxide). Antimony is a common urban air pollutant, occurring at an 

average concentration of 0.001 pg/m3 (Beliles, 1979). Exposure to antimony may occur via 

inhalation and by ingestion of contaminated food. Some antimonials such as potassium 

antimony tartrate have been used medicinally as parasiticides (Beliles, 1979). 

21. ABWRPTION 

Antimony is only slowly absorbed from the gastrointestinal tract. Based on animal data, 

gastrointestinal absorption of antimony was estimated to be 2 to 7% (Felicetti et al., 1974a; 

Gerber et al., 1982). The specific chemical form will determine the absorption efficiency of 

ingested antimony. Antimony has been detected in the blood of occupationally exposed 

individuals, but it is uncertain if this was due solely to pulmonary absorption or also to 

ingestion following mucociliary transport from the upper respiratory tract (ATSDR, 1990). 

Alveolar deposition and subsequent absorption of small particle-size antimony or antimony 

compounds is likely, with absorption also being a function of compound solubility. Sunagawa 

(1981) and Aimworth (1988) provided data showing a lack of a dose-response relationship 

for absorption, and that antimony levels in lungs and livers of rodents reached a plateau, 

thereby suggesting that antimony absorption by tissues may be a saturable process. Studies 

with rabbits exposed to antimony trioxide or pentoxide provided evidence for dermal 

absorption of these forms of antimony (1B"L. 1972; Myers et aL, 1978). 

Antimony is transported in the blood, its partitioning between erythrocytes and plasma 

being a function of the valence state of the element. Exposure to trivalent antimony resulted 

in higher antimony levels in erythrocytes than in the plasma while exposure to pentavalent 

antimony resulted in a reversal of this partitioning (Felicetti et al., 1974b). However, the 

distri'bution of parenterally administered antimony is highly variable among species, and can 

not be accounted for solely by valence state (Felicetti et aL, 1974b; Beliles, 1979). Antimony 

has been detected in the liver and spleen (more so for pentavalent forms), and the thyroid 

gland (trivalent forms) (Beliles, 1979). Felicetti et aL (1974a,b) also reported accumulation 

of antimony in the skeletal system and in fur. 

31. MErABoLIsM 

Like other metallic elements, antimony is not subject to catabolism. Its metabolic 

transformations are limited to binding with macromolecules, and covalent interactions with 

sulfhydryl groups and phosphates. There is no definitive data regarding the interconversion 

3

of valence states of antimony (ATSDR, 1990). 

24. EXC”I0N 

Animal and human data are available indicating both urinary and fecal excretion of 

antimony (ABDR, 1990). Workers exposed to antimony trioxide had increased urinary levels 

of antimony (Cooper et al, 1968, Ludersdorf et aL, 1987). Urinary excretion of antimony was 

documented for workers exposed to antimony fumes (Renes, 1953; Breiger et al., 1954). 

Fecal excretion of antimony following ingestion of antimonials represents primarily 

unabsorbed antimony. However, there is evidence suggesting that the valence state of 

antimony may affect the excretory mute. Parenteral administration experiments with animals 

and humans have indicated that trivalent antimony is excreted primarily in the urine while 

pentavalent antimony is excreted in the feces (Felicetti et aL, 1974b; Edel et al., 1983). 

Whole-body clearance of trivalent antimony tartrate is biphasic with 90% of the body burden 

being excreted Within 24 hours, and the slower phase having a half-life of 16 days (Felicetti 

et al., 1974b). Urinary antimony levels in a human subject remained above normal (1 pg/g 

creatinine) for one week following a single oral dose (amount unknown) of antimony 

trisulfate (Bailly et aL, 1991). This same study also documented biliary excretion and 

enterohepatic circulation of parenterally administered antimony in rats. 

3. NONCARCINOGENIC HEALTH EFFECIS 

3.1. ORAL EXPOSURES 

3.1.1. Acute Toxicity 

3.1.1.1. Human 

- 

Acute poisoning has occur re^ as the result o€ accidental or suicidal ingestion of 

antimonials (Beliles, 1979) with death ensuing Within several hours. Symptoms of severe 

antimony poisoning include vomiting, watery diarrhea, collapse, irregular respiration, and 

hypothermia. A single dose of potassium antimony tartrate (equivalent to 0.53 mg Sbkg) 

produced vomiting (Dunn, 1928). 

3.1.1.2 Animal 

Toxic effects ranging from gastrointestinal disorders to death have been documented €or 

animals following acute oral expure to antimonials. Bradley and Frederick (1941) reported 

that a single dose (300 mg Sbkg) of the organic antimonial, potassium antimony tartrate, 

induced myocardial infarction and death in rats. However, several studies using inorganic 

antimonials (metallic antimony, antimony oxide, or antimony trioxide) reported that doses as 

high as 27,410 mg Sbkg were not fatal to rats (ATSDR, 1990). 

3.12 Subdhronw: TOX~C~Q 

3.1.21. Human 

4

No information was available regarding the toxic effects of subchronic oral exposure of 

humans to antimony or antimonials. 

3.122 Animal 

Several studies have described the systemic subchronic toxicity of antimony and 

antimonials in animals and are summarized in A'ISDR (1990) and U.S. EPA (1980). 

Subchronic (24-week) exposure of rats to metallic antimony at doses of 500 to 1,OOO 

mg/kg/day decreased plasma protein levels, hemoglobin levels, and hematocrit (Sungawa, 1981; 

Hiraoka, 1986). Sungawa (1981) also reported mild hepatotoxicity in rats receiving 418 mg 

%&$day 

(as antimony trioxide) or 500 mg Sbkg/day (as metallic antimony). A decrease in 

red blood cell count was reported by Sungawa (1981) for rats given 418 mg Sbkg/day (as 

antimony trioxide) for 24 weeks, and an increase reported by Smyth and Thompson (1945) 

in rats treated with same compound at a dose of 894 mg Sb/kg/day for 30 days. Fleming 

(1982) reported that dogs receiving antimony trioxide (6,644 mg Sbkg/day) for 32 days 

exhibited severe weight loss, vomiting, and muscle weakness and dyskinesia of the hind limbs. 

A lower dose (&I mg Sbkg/day) produced severe diarrhea. Using data from Fleming (1982), 

ATSDR (1990) reported a noabserved-adverseeffect-level (NOAEL) of 501 mg Sbkg for 

rats receiving the compound for 20 days. Exposure of CD-1 mice to potassium antimony 

tartrate in the drinking water (5 ppm for 540 days) significantly reduced the lifespan of both 

des and females (Kanisawa and Schroeder, 1W). 

3.13. CbronicTaxidty 

3.13.1. Human 

No information was available regarding the chronic toxicity of antimony in humans. 

3.13.1. Animal 

Schroeder et al. (1970) showed an increase in serum cholesterol and a decrease in 

fasting glucose levels for rats receiving a lifetime exposure to potassium antimony tartrate 

(746 mg Sbkg) in drinking water. However, the biological significance of these findings is 

not certain (ATSDR, 1990). This same study also provided data showing that long-term 

exposure of rats to potassium antimony tartrate in the drinking water (0.262 mg Sbkglday 

equivalent to 2 ppm in drinking water) 

resulted in decreased lifespan. 

3.1.4. Developmental and Reproductive Toxicity 

3.1.4.1. Human 

No information was available regarding the developmental or reproductive toxicity of 

antimony in humans. 

3.1.4.1. Animal 

The effect of prenatal and postnatal exposure of rats (gestation day one to postnatal day 

5

60) to antimony trichloride indicated that drinking water levels as low as 0.1 mg% produced 

alterations in vasomotor responses (Marmo et al., 1987; Rossi et al., 1987). The same effect 

was observed for exposure throughout lactation to postnatal day 60. Although the antimony 

trichloride exposure affected vasomotor responses during the postnatal developmental period, 

the design of these studies did not allow for definitive conclusions regarding the prenatal 

developmental toxicity of the compound. 

3.15.1. Subchronic 

ORAL RfD,: 

4E-4 mg/kg/day (metallic antimony) 

9E-4 mg/kg/day (potassium antimony tartrate) 

4E-4 mg/kg/day (antimony tetroxide, antimony trioxide) 

5E-4 mg/kg/day (antimony pentoxide) 

UNCERTAINTY FACI'OR: loo0 

NO& 

None 

3.152 Chronic 

ORAL RED,: 

4E-4 mg/kg/day (metallic antimony) 

9E-4 mg/kg/day (potassium antimony tartrate) 

4E-4 mg/kg/day (antimony tetroxide, antimony trioxide) 

5E-4 mg/kg/day (antimony pentoxide) 

UNCERTAINTY FACTOR: loo0 

MODIFYING FAaOR: 1 

NO& 

None 

LO& 

035 mg/kg/day 

CONFIDENCE 

Study: 

Data base: 

RfD: 

Low 

Low 

Low 

VERIFICATION DATE: 11106185 

PRINCIPAL STUDY Schroeder et aL. 1970 

CO-: 

Based on decreased longevity and altered blood chemistry values in rats 

chronically exposed to 5 ppm potassium antimony tartrate in drinking water. An 

uncertainty factor of 1,ooO was applied to account for extrapolation from animal data 

(lo), use of a LOAEL (lo), and for protection of sensitive populstions (10). The values 

for all of the compounds were calculated based on elemental equivalent weight of 

antimony (U.S. EPA, 1991, 1992). 

6

32 INHALATIONEXPOSURES 

321. Aca~teToxicity 

321.1. Human 

Inhalation of antimony dust by factory workers pra~ced gastrointestinal irritation, 

probably the result of antimony dust transported via the mucociliary escalator (AISDR, 

1990). However, no information regarding the acute inhalation toxicity of antimony was 

available. 

3212 Animal . 

Exposure of rats and guinea pigs to stibine gas (SbH,) at a concentration of 1,395 mg 

Sbh' for 30 minutes resulted in pulmonary edema and death (Price et al., 1979). At 799 

mg Sb/m3, the guinea pigs and rats exhibited only renal tubular dilation. 

3221. Human 

Several occupational exposure studies have been conducted that evaluated the effects 

of subchronic cxposure of smelter workers to antimony fumes. Renes (1953) reported that 

c 5 month exposures to antimony fumes at concentrations ranging from 4.69 to 11.82 mg/m3 

produced various conditions (rhinitis, dermatitis, laryngitis, bronchitis, pneumonitis, 

conjunctivitis, and septal perforations) the severity of which increased with increasing duration 

of scposure. These workers, however, were also exposed to low concentrations of arsenic 

(039 to 1.10 mum3). The effects of occupational cxposure to antimony trioxide (0.58 to 55 

mg/m3) for periods of 8 months to 2 years were reported by Breiger et al. (1954). Eight of 

the employees died during this period but only one death had ocamed in the 16 years prior 

to the use of antimony. Additionally, abnormal electrocardiograms were detected in 37 of 75 

workers and some workers also exhibited elevated blood pressure. The findings of this study 

are compromised by concurrent exposure to phenol formaldehyde resin. However, the 

investigators noted that no additional deaths occurred and the incidence of electrocardiac 

anomalies decreased following cessation of antimony use. 

3.222 Animal 

Gross et al. (1952) reported that inhalation exposure of rats to antimony trioxide for up 

to 14 months resulted in lipoid pneumonia. Myocardial damage and alteration of 

electrocardiograms were observcd for rats and rabbits exposed for six weeks to antimony 

trisulfide dust at concentrations of 220 and 4.02 mg Sb/m3, respectively (Brieger et aL, 1954). 

This same study also noted similar effects in dogs exposed for 10 weeks to antimony trisulfide 

(3.98 mg Sbim3). Thirteen-week exposure of rats to antimony trioxide (0.92 mg Sb/m3) 

resulted in nonreversible proliferation of alveolar macrophages (Bio/dynamia, 1989). Sevtral 

studies reviewed in A'ISDR (1990) reported interstitial fibrosis in rats exposed for 12 to 145 

months to antimony trisulfide or antimony trioxide at concentrations ranging from 1.6 to 83.6 

mg Sbim? 

7

3-3.1. Human 

Occupational exposure to antimony trioxide and/or antimony pentoxide dust (9 to 31 

years) resulted in respiratory effects including pneumoconiosis, chronic bronchitis, chronic 

emphysema, pleural adhesions, and obstructive pulmonary effects (Cooper et aL, 1968, 

Potkonjak and Pavlovich, 1983). The pneumoconiosis was characterized by chronic coughing, 

wheezing, and upper airway irritation. Shorter-term occupational exposures (Renes, 1953; 

Brieger et aL, 1954) are described in Section 3.2.21. 

3-32 Animal 

No information regarding the chronic toxicity of antimony or antimony-wntaining 

compounds was available, although animal studies employing long-term exposures (12 to 14.5 

months) examined the effects of several antimony-containing compounds (see Section 3.22.2). 

324. Devclopmentai and Reproductive Toxicity 

In a report lacking in detail, Belyaeva (1%7) noted an increased incidence of 

spontaneous abortions and disturbances in the menstrual cycle of women occupationally 

exposed to airborne metallic antimony, antimony trioocide, and antimony pentasulfide 

3242 Animal 

Belyaeva (1967) reported a decrease in the number of ofipring for rats exposed to 

antimony trioxide (209 mg Sb/m3) prior to mating and throughout gestation. Exposure to this 

concentration prior to mating resulted in a 67% failure in conception. Metaplasia in the 

uterus and disturbances in ovum maturation were detected in the animals that did not 

conceive. 

Reference concentrations are currently unavailable. 

33. oTHERROUTESOFExpoGuRE 

33.1. AcuteTcdcity 

33.1.1. Human 

No dermatologic or systemic effects were noted for human subjects having induction 

patches containing antimony trioxide in place for 24 hours (IWZ 1972). 

. 

8

33.12 Animat 

Dermal application of antimony oxide (1,584 mg Sbkg) resulted in the death of rabbits 

within one day (ISTI.., 1972) and dermal application of antimony trioxide (6,686 Sb mag) 

was also fatal to rabbits within one day (Myers et al., 1978). 

Ocular application of antimony oxide or antimony thioantimonate (79 to 100 mg Sb) to 

rabbits resulted in eye irritation (Horton et aL, 1986, IBTL., 1972; WRL, 1979) but similar 

application of antimony trioxide (345 to 83.6 mg Sb) did not produce irritation (Gross et aL, 

1955; Myers et aL, 1978). 

Exposure of rats and guinea pigs to stibine gas (Price et ai., 1979) or antimony trioxide 

(Bio/dynamics, 1985; 1989) caused eye irritation. It is likely that this effect was due to direct 

contact to airborne compounds rather than an inhalation-mediated toxicity. 

332 subchroruc Tdty 

3321. Human 

' 

Occupational exposure to airborne antimony or antimony trioxide has resulted in 

dermatitis (epidermal cellular necrosis with inflammatory cellular reactions) and ocular 

irritation (ocular conjunctivitis), the effects being more pronounced in higher temperature 

environments (Stevenson, 1%5; Potkonjak and Pavlovich, 1983). 

3322 Animal 

Thirteen-week dermal exposure of rabbits to a 5% solution of a mixture of antimony 

trisulfide and antimony pentasulfide did not produce significant signs of toxicity (Horton et 

aL.1986). - 

No human or animal data were available regarding the chronic toxicity of antimony by 

other exposure mutes. 

33.4. hdopmentalToxkity 

NO human or animal data were available regarding the developmentalheproductive 

toxicity of antimony by other exposure routes. 

9

3.4. TARGET ORGANS/CRITICAL EFFECIS 

3.4.1. Oral Expuns 

3.4.1.1. primary Taqpt(s) 

1. Gastrointestinal tract: The gastrointestinal tract appears to be the primary target 

€or acute and long-term oral exposure to antimony and antimonials. Effects are 

characterized by imtation resulting in vomiting and diarrhea These effects have 

been documented €or both humans and animals. 

3.4.12 other Target@) 

1. 

2 

3. 

4. 

Cardiovascular system: Data arc available suggesting that oral exposure to 

antimony or antimonials may affect the cardiovascular system resulting in a 

decreased hypotensive response. 

Blood: Animal data are available showing mild hematologk effects although the 

biological significance of these effects is uncertain. 

Liver: Limited data in animals have shown mild hepatotoxkity following oral 

exposure to antimony and antimonials. 

Developmental toxicity is suggested by animal data showing that prenataupostnatal 

exposure to antimony may affect cardiovascular functions. 

3.421. Primary Target($) 

1. Respiratory tract: The respiratory tract is the primary target for toxicity of 

inhaled antimony and antimonials following acute, subchronic, and chronic 

exposure. Both human and animal data have demonstrated various forms of 

restrictive airway diseases including pneumoconiosis, bronchitis, emphysema, 

pulmonary edema, and varying degrees of imtation and inflammation. 

1. Cardiovascular system: Cardiovascular effects (alterations in blood pressure and 

electrocardiograms) have been documented in humans exposed to antimony and 

antimonials. Similar effects have also been verifed using several animals species. 

2 Kidney: Renal toxicity (histological changes) has been observed €or animals 

exposed to stibine gas and various antimony oxides and sulfides. 

3. Reproductive tract Limited data are available indicating adverse effects on the 

reproductive system of women occupationally exposed to antimony. One study 

in rats has also shown reproductive/developmental toxicity of antimony. 

10

4.1. ORAL p[posuRE 

4.1.1. Human 

4.12. Animal 

No information was available regarding the carcinogenicity of antimony in humans. 

No definitive data were available regarding the carcinogenicity of antimony in animals. 

Although evidence for an increased incidence of cancer was not observed for rats and mice 

fed potassium antimony tartrate (0.262 and 035 mg Sbkg/day, respectively), the maximum 

tolerated dose was not used (Schroeder, 1968; Kanisawa and Schroeder, 1969; Schroeder, 

1970). 

421. Human 

Evidence of increased incidence of cancer was not detected in workers exposed to 

antimony oxide for 9 to 31 years (Potkonjak and PavloVich, 1983). 

422 Animal 

Lung tumor incidence was increased for rats exposed for one year to 4.2 or 36 rng 

Sbhn' as antimony trioxide (Wong et al, 1979, Watt, 1980, Groth et al., 1986) or 17.48 mg 

Sb/m3as antimony trisulfide (Wong et aL, 1979; Groth et al, 1986). An increased incidence 

of lung tumors was also reported by Bio/dynamics (1989) for rats exposed to antimony tnioxidc 

(3.76 mg Sb/m3) and by Watt (1983) for pigs exposed to the same compound at a 

concentration of 4.2 mg Sbhn3. 

43. OTHER ROUTES OF EXPOWRE 

No data were available regarding the potential carcinogenicity of antimony and 

antimonials by other router of exposure. 

4.4. EPA mGHT-OF-EVIDRKE CXASIFICA'IION 

The U.S. EPA has not evaluated antimony regarding its potential carcinogenicity and, 

therefore, a Weightsf-Evidence classification has not been assigned (U.S. EPA, 1991). 

45. CARCINOGENICITY SLxlPE FACIORS 

None have been calculated. 

11

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12

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13

Price, N. H., W. G. Yates and S. D. Allen. 1979. Toxicity evaluation for establishing IDLH 

values. National Institute for Occupational Safety and Health, Cincinnati, OH; PB87-229498. 


Renes, L E 1953. Antimony poisoning in industry. Arch. In& Hyg. 799-108. 

Rossi, E, R Acampora, C. Vacca, et al. 1987. Prenatal and postnatal antimony exposure in 

rats: effect on vasomotor reactivity development of pups. Teratogen. Carcinogen. Mutagen. 

7:491-4%. 

Schroeder, H. A, M. Mitchener, J. J. Balassa, et al. 1968. Zirconium, niobium, antimony and 

fluorine in mice: Ef€ects on growth, survival and tissue levels. Nutr. 9595-101. 

Schroeder, H. A, M. Mitchener and A P. Nason. 1970. Zirconium, niobium, antimony, 

vanadium and lead in rats: Life-time studies. J. Nutr. 10&59-68. 

Smyth, H.F., Jr. and W. L. Thompson. 1945. The single dose and subacute-toxicity of 

antimony oxide (Sb20,). Mellon Inst. of Indust. Res, Univ. of Pittsburgh. 013206062. (Cited 


Stevenson, C. J. 1965. Antimony spots. Trans. St. John's Hospital Dermat. SOC. 51:40-42 


Sunagawa, S. 1981. Experimental studies on antimony poisoning. Igaku Kenkyu 51:129-142 


U.S. EPA 1980. Ambient water quality criteria document for antimony. EPA-440/5-8M)20, 

US. EPA 1991. Antimony. Integrated Risk Information System (IRIS). Environmental 

Criteria and Assessment Office,Ofice of Health and Environmental Assessment, Cincinnati, 

OH. 

U.S. EPA 1992. Health Effects Assessment Summary Tables, Fy-1992 AnnuaL OfTce of 

Research and Development, OfTce of Emergency and Remedial Response, Washington, D.C. 

OERR 9200.6-303(X). 

Watt, W.D. 1980. Chronic inhalation toxicity of antimony trioxide: validation for the TLV - 

,progress report-summary of results. OTS206195. (Cited in ATSDR, 1990) 

WRL (Wil Research Laboratories). 1979. Acute eye irritation study in rabbits with antimony 

oxide. PPG Indust., Inc., Pittsburgh, PA (Cited in A'ISDR, 1990) 

Wong, L C. K, J. M. Winston, J. Hagensen, et aL 1979. Study of carcinogenicity and toxicity 

of inhaled antimony trioxide, antimony ore concentrate and thallic oxide in rats. NIOSWUS. 

Dept. Health. 0130511065. (Cited in ATSDR, 1990) 

14

TOXICITYSUMMARY 

for 

INORGANIC ARSENIC 

April 1992 

Prepared by 

Dennis M. Opresko, PbD. 




Oak Ridge National Laboratory* 


Prepared for: 



+Managed by Martin Marietta Energy Systems, Inc., for the US. Department of Energy 

under Contract No. DE-AC05-840R21400

Thir page intentionaUy lefi blank

The toxicity of inorganic arsenic (As) depends on its valence state (-3, +3, or +5), and 

also on the physical and chemical properties of the compound in which it occurs. Trivalent 

(Ast3) compounds are generally more toxic than pentavalent (As”) compounds, and the 

more water soluble compounds are usually more toxic and more likely to have systemic effects 

than the less soluble compounds, which are more likely to cause chronic pulmonaxy effects 

if inhaled. One of the most toxic inorganic arsenic compounds is arsine gas (ASH,). It should 

be noted that laboratory animals are generally less sensitive than humans to the toxic effects 

of inorganic arsenic. In addition, in rodents the critical effects appear to be immunosuppression 

and hepato-renal dysfunction, whereas in humans the skin, vascular system, and 

peripheral nemus system are the primary target organs. 

Water soluble inorganic arsenic compounds are absorbed through the G.I. tract (>90%) 

and lungs; distributed primarily to the liver, kidney, lung, spleen, aorta, and skin; and excreted 

mainly in the urine at rates as high as 80% in 61 hr following oral dosing (U.S. EPA, 1984; 

ATsDR, 1989, Crecelius, 1977). Pentavalent arsenic is reduced to the trivalent form and 

then methylated in the liver to less toxic methylarsinic acids (ATSDR, 1989). 

Symptoms of acute inorganic arsenic poisoning in humans are nausea, anorexia, vomiting, 

epigastric and abdominal pain, and diarrhea. Dermatitis (edoliative erythroderma), m d e 

cramps, cardiac abnormalities, hepatotoxicity, bone marrow suppression and hematologic 

abnormalities (anemia), vascular lesions, and peripheral neuropathy (motor dysfunction, 

paresthesia) have also been reported (US. Air Force, 1990. ATSDR, 1989, Franzblau and 

Lilis, 1989; U.S. EPA 1984, Armstrong et al, 1984, Hayes, 1982; Mizuta et aL, 1956). Oral 

doaes as low as 20-60 pg/kg/day have been reported to cause toxic effects in some individuals 

(ATSDR, 1989). Severe exposures can result in acute encephalopathy, congestive heart 

failure, stupor, convulsions, paralysis, coma, and death. The acute lethal dose to humans has 

been estimated to be about 0.6 mg/kg/day (ATSDR, 1989). General symptoms of chronic 

arsenic poisoning in humans are weakness, general debility and lassitude. loss of appetite and 

energy, loss of hair, hoarseness of voice, loss of weight, and mental disorders (Hindmarsh and 

McCurdy, 1986). Primary target organs are the skin (hyperpigmentation and hyperkeramis) 

frerada et ai. 1%0, Tseng et ai, 1968; Zaldivar 1974; Cebrian et al., 1983; Huang et al, 

19851, nemus system (peripheral neuropathy) (Hindmarsh et al., 1977, 1986; Valentine et 

al., 

1% Heyman et aL, 1956, Mizuta et al, 1956: Tay and Seah, 19751, and vascular system 

pSeng et al, 1%8, Borgano and Greiber, 1972; Salcedo et aL, 1984; Wu et al., 1989, Hansen, 

19901. Anemia, leukopenia, hepatomegaly, and portal hypertension have also been reported 

(Terada et aL, 1%0, Viallet et al., 1972; Morris et aL, 1974; Datta, 1976). In addition, 

possible reproductive effects include a high male to female birth ratio (Lyster, 1977). 

In animals, acute oral exposures can cause gastrointestinal and neurological effects 

(Heymod and Sortwell. 1979). Oral LD, values range from about 10 to 300 mgikg 

(-R, 1989; US. Air Force, 1990). Low subchronic doses can result in 

immunosuppression, (Bfakely et al, 1980) and hepato-renal effects (Mahaffey et al, 1981; 

Brown et ai., 1976; Woods and Fowler, 1977,1978 Fowler and Woods, 1979; Fowler et al., 

1979). Chronic exposures have also resulted in mild hyperkeratosis and bile duct enlargement 

With hyperplasia, focal necrosis, and fibrosis (Baroni et aL, 1963; Byron et at, 1967). 

1

Reduction in litter size, high male/female birth ratios, and fetotoxicity without significant fetal 

abnormalities occur following oral exposures (Schroeder and Mitchener, 1971; Hood et aL, 

1977; Bdey et al., 1981); however, parenteral dosing has resulted in exencephaly, 

encephaloceles, skeletal defects, and urogenital system abnormalities (Ferm and Carpenter, 

1968; Hood and Bishop, 1972; Beaudoin, 1974; Burk and Beandoin, 1977). 

The Reference Dose for chronic oral exposures, 0.0003 mg/kg/day, is based on a NOAEL 

of O.OOO8 mg/kg/day and a LOAEL of 0.014 mg/kg/day for hyperpigmentation, keratosis, and 

possible vascular complications in a human population consuming arseniccontaminated 

drinking water (U.S. EPA, 1991a). Because of uncertainties in the data U.S. EPA (1991a) 

states that "strong scientific arguments can be made for various values within a factor of 2 or 

3 of the currently recommended RfD value." The subchronic Reference Dose is the same 

as the chronic IUD, 0.0003 mg/&g/day (U.S. EPA, 1992). 

Acute inhalation exposures to inorganic arsenic can damage mucous membranes, cause 

rhinitis, pharyngitis and laryngitis, and result in nasal septum perforation (U.S. PA, 1m). 

Chronic inhalation exposures, as occurring in the workplace, can lead to rhino-pharynolaryngitis, 

tracheobronchitis, (Lundgren, 1954); dermatitis, hyperpigmentation, and 

hyperkeratosis (Perry et al., 1948, Pinto and McGill, 1955); leukopenia (Kyle and Pease, 1965; 

Hine et aL, 1977); peripheral nerve dysfunction as indicated by abnormal nerve conduction 

velocities (Feldman et aL, 1979; Blom et aL, 1985; Landau et al., 1977); and peripheral 

vascular disorders as indicated by Raynaud's syndrome and increased vasospastic reactivity in 

fingers exposed to low temperatures (Lagerkvist et aL, 1986). Higher rates of cardiovascular 

disease have also been reported in some arsenic-exposed workers (Lee and Fraumeni, 1969, 

krelson et aL, 1978 Wingren and Axelson, 1985). Possible reproductive effects include a 

high frequency of spontaneous abortions and reduced birth weights (Nordstrbm et al, 

1978a,b). Arsine gas (ASH,), at concentrations as low as 3-10 ppm for several hours, can 

cause toxic effects. Hemolysis, hemoglobinuria, jaundice, hemolytic anemia, and necrosis of 

the renal tubules have been reported in exposed Workers (ACGIH, 1986, Fowler and 

Webberg, 1974). 

Animal studies have shown that inorganic arsenic, by intratracheal instillation, can cause 

pulmonary inflammation and hyperplasia (Webb et al, 1986,1987), lung lesions (Pershagen 

et al., 1982), and immunosuppression (Hatch et al. (1985). Long-term inhalation exposures 

have resulted in altered conditioned reflexes and CNS damage (Rozenshstein, 1970). 

Reductions in fetal weight and in the number of live fetuses. and increases in fetal 

abnormalities due to retarded osteogenesis have been obserred following inhalation exposures 

(Nagymajtenyi et al., 1985). 

Subchronic and chronic RfCs for inorganic arsenic have not been derived. 

Epidemiological studies have revealed an association between arsenic concentrations in 

drinking water and increased incidences of skin cancers (including squamous cell carcinomas 

and multiple basal cell carcinomas), as well as cancers of the liver, bladder, respiratory and 

gastrointestinal tracts (U.S. EPA, 1987; IARC, 1987; Sommers et aL, 1953; Reymann et aL, 

1978 Dobson et at, 1965; Chen et aL, 1985, 1986). Occupational exposure studies have 

shown a clear correlation between exposure to arsenic and lung cancer mortality (IARC, 

1987; U.S. EPA, 1991a). U.S. EPA (1991a) has placed inorganic arsenic in weight-of- 

2

evidence group A, human carcinogen. A drinking water unit risk of 5E-5(@)" has been 

proposed (U.S. EPA, 1991a); derived from drinking water unit risks for females and males 

that are equivalent to slope factors of 1.OE-3 (@g/day)" (Females) and 2.OE-3 (clgflrglday)'' 

(males) (U.S. EPA, 1987). For inhalation exposures, a unit risk of 4.3E-3 (pg/m3)-' (U.S. 

EPA, 1991a) and a slope factor of 5.0E+1 (mg/kg/day)-' have been derived (U.S. EPA, 1992). 

3

1. INTRODUCIION 

The toxicity of inorganic compounds containing arsenic depends on the valence or 

oxidation state of the arsenic (-3, +3, or +5), as well as on the physical and chemical 

properties of the compound in which it occurs. Trivalent (Ast3) compounds such as arsenic 

trioxide (As,O,), arsenic trisulfide (As&, and sodium arsenite (NaAsOJ, are generally more 

toxic than pentavalent (As”) compounds such as arsenic pentoxide (As,O,), sodium arsenate 

(NaWO,), and calcium arsenate (Ca3(ASO4)2). Trivalent arsenic interacts with sulfhydryl 

groups of proteins and enzymes; pentavalent arsenic substitutes for phosphate groups 

important in oxidative phosphorylation (Squibb and Fowler, 1983). The relative toxicity of 

the trivalent and pentavalent forms may also be affected by factors such as the water solubility 

of the compound. Although the more water soluble arsenic compounds are generally more 

toxic and more likely to have systemic effects, the less soluble compounds are more likely to 

cause chronic pulmonary effects if inhaled. One of the most toxic arsenic compounds is 

arsine gas (AH,) with arsenic in the -3 valence state. 

It should be noted that laboratory animals are generally less sensitive than humans to the 

toxic effects of inorganic arsenic. In addition, in rodents the critical effects appear to be immunosuppression 

and hepato-renal dysfunction, whereas in humans the skin. vascular system, 

and peripheral nervous system are the primary target organs. 

Z METABOLISM AND DISPOSITION 

21. ABSORPTION 

Absorption of water soluble inorganic arsenic compounds through the G.I. tract is very 

high. In humans, absorption rates of %.5% for trivalent sodium arsenite and 94% for 

soluble pentavalent arsenic have been reported (Bettley and OShea, 1975; Pomroy et aL, 

1980). In contrast, G.I. absorption of the less soluble arsenic trisulfide and lead arsenate was 

reported to be only 20-30% in hamsters (Marafante and Vahter, 1987). In tests on humans, 

absorption of the insoluble arsenic selenide appeared to be neglible as indicated by the 

absence of an increase in urinary arsenic excretion (Mappes, 1977). 

Absorption of arsenic in the lungs is dependant on particle size as well as water solubility; 

respirable particles (0.1-1 p) are carried further into the lungs and are therefore more likely 

to be absorbed (ATSDR 1989). Estimates of pulmonary absorption may be complicated by 

the fact that some of the particles may be cleared from the lungs, then swallowed and 

absorbed through the G.I. tract. In studies on smelter workers exposed to arsenic dusts of 

about 5 p particle size, Lagerkvist et al. (1986) estimated that 75% of the dust would be 

deposited in the respiratory tract and MO of this would be absorbed directly or through the 

stomach after mucocillary clearance. 

4

22 DISX'RIBUTION 

Following absorption of trivalent or pentavalent arsenic compounds, arsenic is initially 

accumulated in the liver, kidney, lung, spleen, aorta, and skin. With the exception of the skin, 

clearance from these organs is rapid. Arsenic is also extensively deposited in the hair and 

nails (U.S. EPA, 1984). 

Arsenic compounds are subject to metabolic transformation. In both humans and animals, 

pentavalent arsenic compounds are reduced to trivalent forms and then methylated in the 

liver to less toxic methylarsinic acids (ATSDR, 1989). 

24. EXCREIION 

Arsenic is cleared from the body relatively rapidly and primarily in the urine. Urinary 

excretion rates of 80% in 61 hr following oral doses and 30430% in 4-5 days following 

parenteral doses have been measured in humans (Crecelius. 1977; Hunter et al., 1942). 

Arsenic is also lost from the body in the hair and nails, since this represents a non-biologically 

available arsenic pool. 




- 

3.1.1.1. Human 

Common symptoms of inorganic arsenic poisoning are nausea, anorexia, vomiting, 

epigastric and abdominal pain, and diarrhea. Dermatitis (exfoliative erythroderma), muscle 

cramps, cardiac abnormalities, hepatotoxicity, bone m a w suppression and hematologic 

abnormalities (anemia and leukopenia), vascular lesions, and peripheral neuropathy (motor 

dysfunction, long axon Wallerian degeneration) have also been reported (U.S. Air Force, 

1990, A'TSDR, 1989, Franzblau and Lilis, 1989, U.S. EPA, 1984; Armstrong et A, 1984, 

Hayes, 1982; Mizuta et al., 1956). 

Oral doses as low as 20-60 pg/kg/day have been reported to cause toxic effects in some 

individuals (ATSDR, 1989). Severe exposures can result in acute encephalopathy, congestive 

heart failure, stupor, convulsions, paralysis, coma, and death. The acute lethal dose to 

humans has been estimated to be about 0.6 mg/kg/day (ATSDR, 1989). A dose estimated at 

3 muday for a 1-2 month period was fatal to 1% of a group of infants receiving amniccontaminated 

milk (Hamamoto, 1955).


Monkeys exposed to acutely toxic doses of inorganic arsenic exhibit gastrointestinal 

distress and neurological effects. Adolescent and infant Rhesus monkeys receiving 5 daily oral 

doses of a complex inorganic arsenic compound containing the equivalent of 7.5 mgkg of 

arsenic trioxide exhibited loss of condition, vomiting, diarrhea, salivation and uncontrolled 

shaking of the head (Heywood and Sortwell, 1979). 

LD, values for inorganic arsenic compounds in laboratory animals range from about 10 

to 300 mgkg (ASTDR, 1989, U.S. Air Force, 1990). 

3.1.21. Human 

Depending on the dose and duration, subchronic exposures to inorganic arsenic can cause 

toxic effects similar to those caused by acute and/or chronic exposures. Skin and vascular 

disorders, neuropathy, gastroenteritis, hepatotoxicity, and hematological abnormalities (anemia 

and leukopenia) have been reported in individuals exposed for time periods ranging from less 

than 6 months to 13 years (ATSDR 1989, Huang et aL, 1985). 

Borgono and Greikr (1972) reported a 12% incidence of skin abnormalities in children 

whose drinking water contained 0.6-0.8 mg As/L. The earliest cases occurred about 4-5 years 

after the initial exposure. Cardiovascular effects, including Raynaud’s syndrome, acrocyanosis, 

angina pectoris, hypertension, myocardial infarction, mesenteric thrombosis, systemic occlusive 

a*rial disease, bronchiectasis, and recurrent broncho-pneumonia were also observed in this 

group of subjects (Zaldivar, 1980). The bronchiectasis and recurrent broncho-pneumonia 

were attributed to an immunosuppressive action of arsenic in the lungs. A significant 

decrease in the incidence of skin abnormalities was observed following a reduction in drinking 

water concentration to about 0.04 mg/L After 4 years at the lower exposure, effects were 

rarely Seen in children younger than 12 years old (Borgono et al., 1977). 

Central nemus system deficits (hearing loss, eye damage, abnormal EEGs, mental 

retardation, epilepsy), electrocardiographic changes (elevated ST wave and extended QT 

interval), and skin abnormalities (melanosis, desquamation, rashes, and hyperkeratosis) 

occurred in infants who had been fed arsenicoontaminated milk for 1-2 months (Hamamoto, 

1955). It was estimated that the daily arsenic intake was about 3 mg/day (U.S. EPA, 1984). 

Immunosuppression and hepato-renal toxicity have been identified as toxic effects in 

rodents. Immunosuppression, as measured by hemagglutination, radial immunodiffusion, and 

Cunningham plaque assays, was observed in mice exposed for 3 week to sodium arsenite 

levels of 05 ppm in drinking water (Blakely et aL, 1980). Reported hepato-renal effects 

include: (1) mild swelling of renal tubular cell mitochondria and decreases in liverderived 

serum enzymes (aspartate aminotransferase [ASTI and alkaline phosphatase) in rats following 

10 weeks exposure to 50 ppm dietary arsenate (Mahaffey et aL, 1981); (2) functional and 

ultrastructural changes in the kidneys of rats exposed for 6 weeks to arsenate concentrations 

6

of 85 and 125 ppm in drinking water (Brown et al., 1976); (3) disruption of liver biosynthesis 

of heme and 8-aminolevulinic (ALA) synthetase activity in mice and rats exposed for 6 wk 

to 40 and 85 ppm arsenic in drinking water (Woods and Fowler, 1977, 1978); (4) alteration 

of hepatocyte mitochondrial structure and liver enzyme activity (monoamine oxidase, 

cytochrome oxidase) in rats and mice exposed for 6 week to 20-85 ppm sodium arsenate in 

drinking water (Fowler and Woods, 1979; Fowler et al., 1979); and (5) increases in serum 

AST and alanine aminotransferase (UT) levels due to hepatocyte plasma membrane 

dysfunction in beagle dogs fed dietary levels of sodium arsenite equivalent to 4 mgkg for 58 

days followed by 8 mg/kg/day for an additional 125 days (Neiger and Osweiler, 1989). 

In a six-month study in which rats were fed 250 ppm pentavalent or trivalent arsenic, 

Douglas and Blendermann (1961) found that trivalent arsenic caused bile duct lesions and a 

significant depression in growth. 

Although arsenic-induced skin disorders are not commonly seen in rodents, eaerna, 

hyperplasia, and hyperkeratosis were reported in two-week-old rats dosed for 40 days by 

stomach intubation with 2 mg/kg/day or 10 mg/kg/day of arsenic trioxide (Ishinishi et at, 

1976). Avoidance conditioning responses were also impaired by these dose levels (Osato, 

!9n>* 

3.13. Chronic Toxicity 

3.13.1. Human 

General symptoms of chronic arsenic poisoning are weakness, general debility and 

lassitude, loss of appetite and energy, loss of hair, hoarseness of the voice, loss of weight, and 

mental abnormalities (Hindmarsh and McCurdy, 1986). Skin, neurological, and vascular 

disorders are the most common effects seen following long-term exposures. 

Skin abnormalities, particularly hyperpigmentation and hyperkeratosis have been observed 

in populations exposed to arsenic in drinking water (Terada et al. 1%0, Tseng et al., 1968, 

Zaldivar 1974; Cebrian et al., 1983; Huang et al., 1985). Tseng et al. (1968) reported an 

incidence rate of 18% for hyperpigmentation and 7% for hyperkeratosis in a Taiwanese 

population whose drinking water contained an average arsenic concentration of 0.4-0.6 ppm 

Skin abnormalities were also reported in 40% of patients consuming Fowler’s solution for 6- 

26 years (Hen, 1965). 

Arsenic-induced neurotoxicity is manifested as a peripheral neuropathy involving both 

sensory and motor nerves, and resulting in numbness and paresthesia, diminished sensations 

of touch, pain, heat, and cold, and muscle weakness (Hindmarsh et aL, 1977; Hindmarsh and 

McCurdy, 1986, Valentine et al., 1982, Heyman et al., 1956, Mizuta et al., 1956; Tay and 

Seah, 1975). 

Peripheral vascular disorders have been reported in several populations whose drinking 

water contained high arsenic levels (Tseng et aL, 1%8* Salcedo et al., 1984; Chen et al, 

1988). Blackfoot disease (a condition cawed by arteriosclerosis and thromboangiitis 

obliterans), which can result in gangrene of the lower extremities, occurred in 0.9% of one 

such population (Tseng et al., 1%8, 1977). Epidemiological studies and mechanistic 

7

considerations have implicated arsenic as a possible causative factor in arteriosclerotic plaque 

formation and cardiovascular disease (Wu et ai., 1989, Hansen, 1990; Penn, 1990). 

Chronic oral exposures to arsenic reportedly have also resulted in anemia, leukopenia, 

liver swelling, and noncirrhotic portal hypertension (Terada et al., 1960; Viallet et al., 1972; 

Morris et al., 1974; Datta, 1976 Nevens et al., 1990). 

3.132 Animal 

Studies in rats have demonstrated no-adverseeffect levels of 1.4 (males) and 1.6 mg 

Askglday (females) for sodium arsenite and 28 (males) and 3.25 mg As/kg/day (females) for 

sodium arsenate (Byron et al., 1%7). Similar studies on dogs revealed a no-adverseeffect 

level at 1.1 mg As/kg/day. A drinking water concentration of 5 ppm produced no toxic effects 

in rats when administered over an entire lifetime (Schroeder et al., 1968). 

Mild hyperkeratosis has been reported in mice exposed for a lifetime to arsenic oxide in 

drinking water at a concentration of 0.01% (Baroni et al., 1963). 

Bile duct enlargement with hyperplasia of the glandular elements, focal necrosis, and 

fibrosis was Seen in rats receiving dietary arsenic levels of 125 and 250 ppm as sodium arsenite 

and 250 and 400 ppm as sodium arsenate for up to two years (Byron et aL, 1967). Lifetime 

(29 mo) exposure to lead arsenate at a dietary level of 1850 pprn also caused bile duct lesions 

in rats (Kroes et aL, 1974). 

3.1.4. DRlelopmental and Reproductive Tolddty 

3-1.4.1. Human 

A high male-to-female birth ratio (157 to 10) was reported for a population that may 

have been exposed to elevated arsenic levels in their drinking water 10 to 11 months earlier 

(Lyster, 1977). 

3.1.42 Animal 

Chronic exposure of pregnant mice to 5 ppm sodium arsenite in drinking water resulted 

in a slight reduction in litter size and a higher male/female ratio (increased from 0.93 to 1.71), 

but no adverse effects on fetal development (Schder and Mitchner, 1971). Oral doses as 

high as 120 mgAcg/day of sodium arsenate were reported to be fetotoxic but not teratogenic 

to rats (Hood et aL, 1977). Oral doses of 25-40 mgkg of sodium arsenite caused prenatal 

mortality and a low, but non-significant, incidence of fetal malformations (exencephaly) in 

mice (Baxley et aL, 1981). 


ORAL RfD. 0.0003 mg/kg/day (U.S. EPA. 1992) 

UNCERTAINTYFACIOR: 3 

8

NOAEL: O.OOO8 mgAcg/day, epidemiological study. 

COMMENT: The same study applies to the subchronic and chronic RfD (see Section 

3.1.5.2). 

3.152 chronic 

ORAL RfD: 0.0003 mg/kg/day (U.S. EPA, 1991a) 

UNCERTAINTYFACTOR: 3 

MODlFYINGFACTOR 1 

NOAEL: 0.0008 mg/kg/day, epidemiological study 

CONFIDENCE: 

StndF Medium 

Data Base:Medium 

=.Medium 

VERIFICATION DATE: 11/15/90 

PRINCIPAL STUDIES: Tseng, W.P. 1977; Tseng et al., 1968 

COMMENT: The NOAEL was based on an arithmetic mean of 0.009 mg/L in drinking 

water (range 0.001-0.17 mg/L), a daily water consumption of 4.5 L, and an arsenic intake 

in food of 0.002 muday. A LOAEL of 0.014 mg/kg/day for hyperpigmentation, keratosis, 

and possible vascular complications. was based on an arithmetic mean of 0.14 mg/L in 

drinking water (4.5 Uday), and 0.002 mg/kg in food. The UF of 3 is to account for both 

the lack of data to preclude reproductive toxicity as a critical effect and to account for 

some uncertainty in whether the NOAEL of the Critical study accounts for all sensithe 

individuals. 

NOTE: U.S. EPA (1991a) states that "strong scientific arguments can be made for various 

values within a factor of 2 or 3 of the currently recommended RfD value, i.c, 0.1-0.8 

)rg/kg/day"; therefore, considerable flexibility is allowed in formulating regulatory decisions. 

3.21. Acute Toxicity 

321.1. Human 

Inorganic arsenic dusts can cause respiratory irritation and mucous membrane damage 

leading to rhinitis, pharyngitis or laryngitis. Several weeks exposure to high concentrations 

can result in nasal septum perforation (U.S. EPA, 1984). Although inhalation exposures to 

most inorganic arsenic compounds are not usually associated with acute lethality (ATSDR, 

1989); exposure to 250 ppm of arsine gas is instantly fatal and several hours exposure to 

concentrations as low as 10 ppm can produce toxic symptoms and may also be fatal (Fowler 

and Webberg, 1974; NOSH, 1979). Arsine causes severe hemolysis, hernoglobmuria, 

9

jaundice, hemolytic anemia, and necrosis of the renal tubules (ACGIH, 1986; Fowler and 

Weissberg, 1974). 

3.21.2 Animal 

Intratracheal instillation studies indicate that inorganic arsenic can have direct toxic effects 

on respiratory tissue. Trivalent arsenic oxide and gallium arsenide were shown to cause 

pulmonary inflammation and hyperplasia in rats (Webb et aL, 1986, 1987), and calcium 

arsenate caused lung lesions in hamsters; however, arsenic trioxide and arsenic trisulfide did 

not have such an effect (Pershagen et aL, 1982). 

The pulmonary immune response can be affected by inorganic arsenic compounds. Hatch 

et al. (1985) reported significant increases in mortality of mice due to infectious streptococcal 

challenge following intratracheal injection of sodium arsenite, and Aranyi et aL (1985) 

reported similar increases in mortality as well as decreases in pulmonary bactericidal activity 

to MebsielZa pneumonia following single and multiple inhalation exposures to arsenic trioxide. 

Exposure of mice to arsine concentrations as low as 25 ppm caused significant decreases 

in red blood cells, hematocrit and hemoglobin, as well as significant increases in white blood 

cell counts, and mean corpuscular volume of RBC. Erythropoiesis in bone marrow cells was 

impaired and erythropoiesis in the spleen was increased (Hong et al., 1989). 

3221. Human 

Subchronic inhalation exposures to inorganic arsenic are expected to cause toxic effects 

similar to those resulting from chronic exposures (see Section 3.2.3). 

Rats exposed for 3 months to 46 )rum3 of arsenic trioxide aerosol exhibited altered 

conditioned reflexes and CNS damage as evidenced by pericellular edema and neuronal 

cytolysis in the brain (Rozenshstein. 1970). 

Rats exposed to 0.025 ppm arsine gas for 90 days developed anemia (Blair et al., 1990). 

Higher exposure levels (primarily 2.5 ppm) resulted in bone marrow hypcrplasia, increased 

splenic hemosiderosis and extramedullary hematopoiesis, decreased packed cell volume, 

increased delta-aminolevulinic acid dehydratase activity, and increased relative spleen weight. 

Similar effects were seen in mice and hamsters. 

3a.1. Human 

Information on the inhalation toxicity of inorganic arsenic is derived primarily from 

occupational expotsure studies, particularly those involving smelter workers. Early studies 

identified chronic respiratory diseases (rhinitis, pharyngitis, laryngitis, tracheobronchitis, and 

10

pulmonary insufficiency) and blood disorders (leukopenia) in exposed workers (Lundgren, 

1954; Kyle and Pease, 1%5). In one study, a 23% incidence of relative neutropenia occurred 

in 130 smelter workers exposed to arsenic air concentrations averaging less than 0.5 mum3 

(Hine et aL, 1977). 

Neurological disorders (peripheral newe dysfunction indicated by abnormal nerve 

conduction velocities) have been documented in smelter workers exposed to arsenic 

concentrations of sO.5 mum3 (Feldman et al., 1979 Blom et al., 1985; Landau et al., 1977). 

Chronic encephalopathy, evidenced by cognitive impairment and psychological symptoms was 

reported in two workers exposed to arsenic fumes for 14-18 months (Morton and Caron, 

1989). Abnormal electromyograms were reported for populations living near an arsenic mine 

and smelter (Takahashi, 1974). Hearing losses have been reported in children living near a 

coal-fired power plant burning high-arsenic content coal (U.S. EPA, 1984). 

Chronic exposure of smelter workers to low levels of atmospheric arsenic (so5 mg/m3) 

caused subtle changes in the peripheral vascular system, as indicated by an increased incidence 

of Raynaud’s syndrome (white fingers) and increased vasospastic reactivity in fingers exposed 

to low temperatures (Lagerhist et al., 1986). Higher rates of cardiovascular disease have also 

been reported in some arsenicexposed workers (Lee and Fraumeni, 1%9 Axelson et aL, 

1978; Wingren and Axelson, 1985). 

Dermatitis, hyperpigmentation, and hyperkeratosis were observed in early studies of 

workers exposed to inorganic arsenic (Perry et al., 1948, Pinto and McGill, 1953); howevcr, 

it is not known to what degree the reported effects were due to direct skin contact and 

accidental ingestion of the arsenic dust. 

Chronic exposure to very low levels of arsine gas may have a cumulative effect in causing 

anemia (FowIer and Weissberg, 1974). 

Glaser et al. (1986) exposed male Wistar rats to aerosols (~0.3 pm MMAD) of arsenic 

trioxide for 18 months at concentrations of 0.60, and 200 pg/m3. The animals were observed 

for one year after the termination of the exposures and no adverse effects on body weight, 

hematology, clinical chemistry, or macro- or microscopic structure of internal organs were 

reported. 

324.1. Human 

A significantly higher frequency of spontaneous abortions (1 1% vs 7.6%) and significantly 

reduced birth weights were recorded for a population living near a copper smelter when 

compared with control populations (Nordstrbm et al., 1978a.b). 

3242 Animal 

11

Nagymajtenyi et al. (1985) exposed mice for 4 hr/day to an aerosol of arsenic trioxide 

(285 mum3) on days 9-12 of gestation, and found a significant reduction in fetal weight and 

in the number of live fetuses. In addition, there was a significant increase in the number of 

fetuses with retarded osteogenesis and an increase in the frequency of chromosomal 

aberrations (chromosome breaks and chromatid exchanges). Concentrations of 2.9 mg/m' and 

0.26 mg/m3 caused no significant changes, except a slight decrease in fetal weight. 

Subchronic and chronic FUCs for inorganic arsenic have not been derived. 

33. oTHERRO~OFExpomTRE 

33.1. Acute Taddty 

33.1.1. Human 

Information on the acute toxicity of inorganic arsenic to humans by other routes of 

exposure was not available. 

33.12 Animal 

Intraperitoneal LDw, values of 4-20 mgkg for various inorganic arsenic compounds have 

been reported (A'ISDR, 1989). 

332 SubcbFWw: * Toxicity 

3321. Human 

- 

Information on the subchronic toxicity of inorganic arsenic to humans by other routes of 


3322 Animal I 

Intraperitoneal injections of sodium arsenate solution at a dose level of 0.2 m&g for two 

months, resulted in inner ear damage and hearing loss in guinea pigs (Aly et aL, 1975). 

333. Chronic Taxicity 

333.1. Humau 

Skin contact with inorganic arsenic dusts in occupationally exposed workers has been 

associated with direct dermatitis, allergenic hypersensitivity, and conjunctivitis (U.S. EP4 

1984, Pinto and McGI11, 1953; Holmqvist, 1951). 

12

333.2 Animal 

Weekly injections of up to 10 mg/kg/day, for 18 months did not produce signs of 

neuropathy in rats (Schaumburg, 1980). 

33.4. Developmental and Reproductive Toxicity 

33.4.1. Human 

Information on the developmental and reproductive toxicity of inorganic arsenic to 

humans by other routes of exposure was not available. 

33.42 Animal 

Some inorganic arsenic compounds cause teratogenic effects when administered 

parenterally. Intravenous injections of sodium arsenate into hamsters on day 8 of gestation 

at dose levels of 15, 17.5, or 20 mgkglday resulted in exencephaly, encephaloceles, skeletal 

defects, and urogenital system abnormalities in fetuses (Ferm and Carpenter, 1968). 

Intraperitoneal injections of sodium arsenate, at doses levels of 30 mg/kg/day or higher, 

resulted in similar terata in rats and mice (Hood and Bishop, 1972; Beaudoin, 1974; Burk and 

Beaudoin, 1!377). 

3.4. TARGEI' ORGAN/C€UTIICAL EFFEcIs 

3.4.1.1. Primary Target Organs 

1. Skk Hyperpigmentation ana hyperkeratosis in humans. 

2 Newus System: Peripheral neuropathy and CNS effects in humans. 

3. Cardiovascular System: Peripheral and cardiovascular disorders in humans. 

1. Blood. Hematological changes (anemia, leukopenia). 

2 Liver: Liver swelling in humans; cirrhosis and portal hypertension in animals. 

3. G.I. System: Gastroenteritis in humans and monkeys at high doses. 

4. Reproductive Effects: Increased male to female birth ratio in animals and possibly in 

humans. 

13

3.42 Inhalam * nbpxwres 

3.421. Primary Target Organs 

1. Skin: Dermatitis and possibly hyperpigmentation and hyperkeratosis in humans. 

2. Nervous System: Peripheral neuropathy and CNS effects in humans. 

3. Cardiovascular System: Peripheral vascular disorders in humans. 

3.4.2.2 other Target Organs 

1. Respiratory system: Rhinitis, laryngitis, tracheobronchitis, pulmonary insufficiency, and 

nasal septum perforation. 

2 Blood: Hematological changes (anemia, leukopenia). 

3. Developmental Effects: Increase in spontaneous abortions, reduction in birth weight 

observed in animals and humans. 

4.1. ORAL EXPOSURES 


Epidemiological studies have revealed a close association between arsenic concentrations 

in drinking water and increased incidences of skin cancers, including squamous cell carcinomas 

and multiple basal cell carcinomas (U.S. EPA, 1987). Tseng et al. (1968) reported skin cancer 

rates of 26, 10.1 and 21.4 per lo00 in Taiwancse populations whose drinking water contained 

~0.30, 030-059, and 20.6 ppm As. respectively. No cases of skin cancer were seen in a 

control population of 7500 whose drinking water contained 0.001-0.017 ppm As. Cebrian et 

aL (1983) reported a 3.6-fold increase in skin lesions thought to be associated with epidermoid 

or basal cell carcinomas, in residents of a Mexican town whose drinking water contained 0.4 

PPm As- 

Chronic oral exposure to arsenic has aiso been linked to various types of internal cancers, 

including those of the liver, bladder, and respiratory and gastrointestinal tracts (U.S. EPA, 

198% IARC, 1987, Sommers and McManus, 1953; Reymann et d, 1978 Dobson et aL, 1%5; 

Chen et aL, 1985,1986). 

4-12 Animal 

OF the many studies conducted on laboratory animals, only a few have been able to show 

a positive association between oral exposure to arsenic and increased tumor incidence. both 

(1966/67) reported increased incidences of adenocarcinomas of the skin, lung, peritoneum, 

14

and lymph nodes in NMRI mice dosed with arsenic trioxide or Fowler’s solution once per 

week for 5 months (estimated total dose 7 mganimal). Katsnelson et al. (1986) reported that 

arsenic trioxide induced a low incidence of adenocarcinomas at the site of its implantation in 

the stomach of rats. In addition, Shirachi et al. (1983) reported that sodium arsenite 

enhanced the incidence of renal tumors induced in rats by intraperitoneal injection of the 

carcinogen N-nitrosodiethylamine. 

421. Human 

Occupational exposure studies of smelter and pesticide workers have shown a close 

association between exposure to arsenic and lung cancer mortality (IARC, 1987; U.S. EPA, 

1991a). A dose- and durationdependent increased frequency of respiratory tract cancers was 

found in copper smelter workers exposed to air-borne arsenic concentrations averaging up 

to 62 mum3 (arithmetic mean) (Lee and Fraumeni, 1%9; Lee-Feldstein, 1983,1986,1989). 

Standardized mortality ratios (SMR) as high as 981 and a maximum relative risk of 6 were 

reported (Lee-Feldstein, 1986, 1989). At another smelter, lung cancer mortality rates were 

correlated with cumulative arsenic exposure as measured by urinary arsenic excretion values, 

and arsenic concentrations of 10 mum3 were linked to a SMR greater than 200 (Enterline 

and Marsh, 1982, Enteriine et al., 1987). Similarly, in a study of Swedish smelter workers, a 

clear positive dose-response relationship was found between cumulative arsenic exposure and 

lung cancer mortality and the overall SMR was 372 (Jirup et al., 1989). Both proportionate 

mortality and cohort studies of pesticide workers have also shown an increased incidence of 

lung cancer deaths (Ott et al., 1974; Mabuchi et al., 1979). 

An increased risk of lung cancer may also occur in non-occupationally exposed populations 

living in areas with high atmospheric levels of arsenic resulting from industrial emissions. 

Higher lung cancer rates have been reported in residents living near smelters (Brown et aL, 

1984; Pershagen 1985) and near an arsenic pesticide manufacturing plant (Matanoski et aL, 

1981). 

Several animal studies have shown an association between tumor induction and exposure 

to arsenic by inhalation or intratracheal instillation. Ivankovic et al. (1979) reported that lung 

tumors developed in 9 of 15 BD IX rats given a single intratracheal instillation of Bordeaux 

mixture (4% calcium arsenate containing 0.07 mg As). In another study, calcium arsenate 

induced a borderline increase in lung adenomas following intratracheal instillation, but arsenic 

trisulfide had no effect on tumor incidence. Perinatal treatment of mice with arsenic trioxide 

resulted in the induction of lung adenomas (Rudnay and BarzSanyi 1981), and intratracheal 

instillation of the same compound in hamsters resulted in respiratory tract carcinomas, 

adenomas, papillomas and adenomatoid lesions (Ishinishi et al., 1983; Pershagen et aL, 

1 Ma, 

b). 

43. OTHERROUTESOF- 

15

Osswald and Goerttle (1971) reported a high incidence (11/19) of lymphocytic leukemia 

or lymphomas in female Swiss mice injected intravenously with 0.5 mg Askg (as sodium 

arsenate) once per week for 20 weeks. In a second study with pregnant mice injected 

subcutaneously with 0.5 m@g, once per day for 20 days during pregnancy, 1 1 of 24 developed 

the same types of tumors. 

DiPaolo and Cast0 (1979) reported that sodium arsenate induced cell transformations bz 

vim in Syrian hamster embryo cells, and Cast0 et al. (199) reported that sodium arsenite 

enhanced virus-induced cell transformation. 

4.4. EPA WEXGHT-OF-EVIDENCE 

4.4.1. Oral 

Classification - A; human carcinogen (U.S. EPA, 1991b) 

Basis - Increased skin cancer incidence in several populations consuming drinking water 

with high arsenic concentrations. 

4-42 Inhalation 

Classification - A; human carcinogen (U.S. EPA, 1991a) 

Basis - Increased lung cancer mortality in populations exposed primarily through 

inhalation. 

45. SIXlPEFACLORS 

45.1. Oral 

SLOPE FACTOR: 1.OE-3 (pg/kg/dayyl (females) and 20E-3 (Ccgflrgday)" (males) (U.S. 

EPA, 1987). These slop factors were based on unit risks of 3E-5 (females) and 7E-5 

(&)*I (males) that were used to derive a single drinking water unit risk as shown below. 

DRINKING WATER UNIT RISK: 5E-5 (@)-I 

(U.S. EPA, 1991a). 

PRINCIPAL STUDIES: Tseng et al.. 1968; Tseng, 1977 

VERIFICATION DATE: Not given. 

COMMENT: The final unit risk is the arithmetic mean of the unit risks derived for 

females and males in a population in Taiwan exposed to arsenic in drinking water. 

Uncertainties associated with this unit risk involve the dose-response relationship, 

particularly in regard to (1) differential mortality due to other arsenic-induced diseases, 

(2) the possibility that ingestion of arseniccontaminated foods contributed to the effects, 

and (3) the shape of the dose-response cum at low doses. A memorandum from the 

EPA administrator noted that the "uncertainties associated with ingested inorganic arsenic 

are such that estimates could be modified downwards as much as an order of magnitude, 

relative to risk estimates associated with most other carcinogens." 

16

452 Inhalation 

SLOPE FAmOR 5.OE+1 (mg/kg/day)-’ (U.S. EPA, 1992) 

INHALATION UNIT RISK: 4.3E-3 (pg/m3)” (U.S. EPA, 1991a) 

PRINCIPAL STUDIES: Brown and Chu, 1983a-c. Lee-Feldstein, 1983; Higgins, 1982, 

Enterline and Marsh, 1982 


COMMENT: The final unit risk is the geometric mean of the geometric means for 

distinct exposed populations of workers at two different copper smelters. It was assumed 

that the increase in age-specific mortality was a function only of cumulative exposure. 

The unit risk should not be used if the air concentration exceeds 2 @m3 (U.S. EPA, 

1992). 

17

5. REFERENCES 

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ATSDR (Agency for Toxic Substances and Disease Registry). 1989. Toxicological Profile 

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Axelson, 0.; Dahlgren, E; Jason, C.-D.; Rehnlund, S.O. 1978. Arsenic exposure and 

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Baroni, C van Esch, GJ.; Saffiotti. U. 1%3. Carcinogenesis tests of two inorganic arsenicals. 

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Baxley, M.N; Hood, RD.; Vedel, G.C; Harrison, W.P.; Szczech, G.M. 1981. Prenatal 

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Beaudoin, AR. 1974. Teratogenicity of sodium arsenate in rats. Teratology 10153-158. 

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Bettley, F.R; O’Shea, J.A 1975. The absorption of arsenic and its relation to carcinoma. 

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Blair, P.C.; Thompson, M.B.; Morrissey, RE.; et al. 1990. Comparative toxicity of arsine gas 

in B6C3F1 mice, Fischer 344 rats, and Syrian golden hamsters: system organ studies and 

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Blakely, B. R; Sisodia, C.S.; Mukkur, T.K. 1980. The effect of methylmercury, tetraethyl 

lead, and sodium arsenite on the humoral immune response in mice. 

Pharmawl. 52245-254. 

TaXicol. AppL 

18

Blom, S.; Lagerkvist, B.; Linderholm, H. 1985. Arsenic exposure to smelter workers: clinical 

and neurophysiological studies. Scand. J. Work Environ. Health 11:265-270. 

Borgono, J.M.; Greiber, R 1972 Epidemiological study of arsenism in the city of 

Antofagasta In: Trace Substances in Environmental Health, vol. 5. D.C. Hemphill, ed. 

University of Missouri, Columbia, MS. pp. 13-24. 

Borgono, J.M.; Vincent, P.; Venturino, H.; Infante, A 1977. Arsenic in the drinking water 

of the city of Antofagast; epidemiological and clinical study before and after the installation 

of the treatment plant. Environ. Health Perspect. 19103-106. 

Brown, CC; Chu, KC. 1983a Approaches to epidemiologic analysis of prospective and 

retrospective studies: Example of lung cancer and exposure to arsenic. In: Risk Assesment 

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EPA, 1992). 

Brown, C.C; Chu, KC. 1983b. Implication of the multistage theory of carcinogenesis 

applied to occupational arsenic exposure. J. Natl. Cancer Inst. 70455-463. (Cited in U.S. 

EPA, 1992). 

Brown, C.C; Chu, KC 1983c. A new methoid for the analysis of cohort studies, 

implications of the multistage theory of carcinogenesis applied to occupational arsenic 

exposure. Environ. Health Perspect. 50293-308. (Cited in U.S. EPA, 1W). 

Brown, M.M.; Rhyne, B.C; Goyer, RA; Fowler, B.A 1976. Intracellular effects of chronic 

arsenic administration on renal proximal tubule cells. J. Torticol. Environ. Health 1505-514. 

Brown, LU; Pottem, LM.; Blot. WJ. 1984. Lung cancer in relation to environmental 

pollutants emitted from industrial sources. Environ. Res. 34250-261. 

Burk D.; Beaudoin, AR 1977. Arsenate-induced renal agenesis in rats. 

16247-260. 

Teratology 

Byron, W.R.; Bierbower, G.W.; Brouwer, J.B.; Hansen, W.H. 1%7. Pathologic changes in 

rats and dogs from two-year feeding of sodium arsenite or sodium arsenate. ToximL AppL 

Pharmacol. 10132-147. 

Casto, B.Q Meyers, J.; DiPaolo, J A 1979. Enhancement of viral transformation for 

evaluation of the carcinogenic or mutagenic potential of inorganic metal salts. Cancer Res. 

39193-198. 

Cebrian, M.E; Albores, A; Aguiiar, M.: Blakely, E 1983. Chronic arsenic poisoning in the 

north of Mexico. Hum. Toximl. 2121-133. 

men, CJ.; Chuang, Y.C; Lin,T.M.; Wu, H.Y. 1985. Malignant neoplasms among residents 

of a Blackfoot disease-endemic area in Taiwan: High-arsenic artesian well water and cancers. 

Cancer Res. 455895-5899. 

19

Chen, CJ.; Chuang, Y.C.; You, S.L; Lin, T.M.; Wu, H.Y. 1986. A retrospective study on 

malignant neoplasms of bladder, lung, and liver in a Blackfoot disease-endemic area in 

Taiwan. Br. J. Cancer 53399-405. 

Chen, CJ.; Wu, S.; Lee, J.; et al. 1986. Atherogenicity and carcinogenicity of high-arsenic 

artesian well water: Multiple risk factors andf related malignant neoplasms of blackfoot 

disease. Arteriosclerosis 8452-460. (Cited in Hansen, 1990). 

Crecelius, EA 1977. Changes in the chemical speciation of arsenic following ingestion by 

man. Environ. Health Perspect. 19147-150. (Cited in U.S. EPA, 1984). 

Datta, D.V. 1976. Arsenic and noncirrhotic portal hypertension. Lancet 1:433. 

DiPaolo, J .4 Casto, B.C. 1979. Quantitative studies of in vitro morphological transformation 

of Syrian hamster cells by inorganic metal salts. Cancer Res. 391008-1013. 

Dobson, R.L; Young, M.R; Pinto, J.S. 1%. 

9233-556. 

Palmar keratoses and cancer. Arch. Dermatol. 

Douglas, C.D.;Blendermann, EM. 1961. Obsemtions on the influence of some arsenic 

compounds on pyruvic oxidase activity in vitro and in vivo. In: Pa. 5th Inter. Congr. 

Biochem., vol. 9, p. 582 (Intern. Union Biochem. Symp. Ser., d. 29, 1963). Macmillan, New 

York. (Cited in Byron et al., 1967). 

Enterline, P.E.; Henderson, V.L; Marsh, G.M. 1987. E5posure to arsenic and respiratoty 

cancer. A reanalysis. Am. J. Epidemiol. 125(6):929-938. 

Enterline, P.E.; Marsh, G.M. 1982. Mortality among workers exposed to arsenic and other 

substances in a copper smelter. Am. J. Epidemiol. 116:895-910. 

Feldman, R.G.; Niles, CA; Keiiy-Heyes, M.: Sax, D.S.; Dixon, WJ.; Thompson, DJ.; Landau, 

E. 1979. Peripheral neuropathy in arsenic smelter workers. Neurology 29939-944. 

Ferm, V.H.; Carpenter, SJ. 1968. Malformations induced by sodium arsenate. J. Reprod. 

Fert. 12199-201. 

Fien, U. 1965. Katamnestische Untersuchungen Uber die Nebenwirkungen der Therapie 

mit anorganischen Arsen bei Hautkrankheiten. Dennatologica 131:41-58 (Cited in U.S. 

=A, 1984) 

Fowler, B.A.; Weissberg, J.B. 1974. Arsine poisoning. New Eng. J. Med. 291:1171-1174. 

Fowler, B.A.; Woods, J.S. 1979. The effects of prolonged oral arsenate exposure on liver 

mitochondria of mice: morphometric and biochemical studies. Toxicol. Appl. Pharmacal. 

50: 177-187.

Fowler, B.A; Woods, J.S.; Schiller, CM. 1979. Studies of hepatic mitochondria structure and 

function: Morphometric and biochemical evaluation of in vivo perturbation by arsenate. Lab. 

Invest. 42313-320. 

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exposure. Arch. Environ. Health 44(6):385-390. 

Glaser, U.; Hochrainer, D.; Oldiges, H.; Takenaka, S. 1986. Long-term inhalation studies 

with nickel oxide and arsenic trioxide aerosols in Wistar rats. Excerpta Med. 676325-328. 

Hamamoto, E 1955. Infant arsenic poisoning by powdered milk. Jap. Med. J. 16492-12 

(Cited in U.S. EPA, 1984). 

Hansen, ES. 1990. Shared risk factors for cancer and artherosclerosis - a review of the 

epidemiological evidence. Mutat. Res. 239163-179. 

Hatch, G.E; Boykin, E.; Graham, J.A.; Lewtas, J.; Pott, F.; bud, K; Mumford, J.L 1985. 

Inhalable particles and pulmonary host defense: in vivo and in virr0 effects of ambient air and 

combustion particles. Environ. Res. 3667-80. 

Hayes, WJ., Jr. 1982 Pesticide Studies in Man. Williams and Eilkins, Baltimore, MD. pp. 

41-50. 

Hcyman, A; Pfeiffer, J.B.; Willett, RW.; Taylor, H.M. 19%. Peripheral neuropathy caused 

by arsenical intoxication. New England J. Med. 254(9): 401-409. 

Heywood. R, Sortwell, RJ. 1979. Arsenic intoxication in the rhesus monkey. ToxicoL Lett. 

3:137-144. 

Higgins, I. 1982 Arsenic and respiratory cancer among a sample of Anaconda smelter 

workers. Report submitted to the Occupational Safety and Health Administration in the 

comments of the Kennecott Minerals Company report on the inorganic arsenic rulemaking. 

(Exhiiit 203-5). 

Hindmarsh, J.T.;McCurdy, RF. 1986. Clinical and environmental aspects of arsenic toxicity. 

CRC Crit. Rev. Clh. Lab. Sci 23315-347. 

Hindmarsh, J.T.; McLetchie, 0.R; Heffernan, LP.; Haynie, O.A.; Ellenberger, H& 

McCurdy, RE; Thiebaux, HJ. 1977. Electromyographic abnormalities in chronic 

environmental arsenicalism. J. And Toxicol. 1270-276. 

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exposure. J. Occup. Med. 19(6)391-3%. 

Holmqvist, I. 1951. Occupational arsenical dermatitis. A study among emplayees at a copper 

ore smelting work, including investigations of skin reactions to contact with arsenic 

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21

Hong, H.L; Fowler, B.A; Boorman, G.A. 1989. Hematopoietic effects in mice exposed to 

arsine gas. ToRcol. Appl. Phannacol. 97:173-182 

Hood, R.D.; Bishop, S.L 1972 Teratogenic effects of sodium arsenate in mice. Arch. 

Environ. Health 2462-65. 

Hood, R.D.; Harrison, W.P. 1982. Effects of prenatal arsenite exposure in hamsters. Bull. 

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Hood, R.D.; Thacker, G.T.;Patterson, B.L. 1977. Effects in the mouse and rat of prenatal 

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RJ.; Zhang, E 1985. Endemic chronic arsenism in Xinjiang. 

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Chin. Med. J. (Eng). 

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after single intratracheal instillation of an arseniccontaining pesticide mixture formerly used 

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Ji!rup, L; Pershagen, G.; Wall, S. 1989. Cumulative arsenic exposure and lung cancer in 

smelter workers: a dose-response study. Am. J. Ind. Med. 1531-42 

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mc, 1980) 

22

TOXICITYSUMMARY FOR 

BARIUM 

DECEMBER 1W 

Prepared by 

A.A. Francis, M.S., D.A.B.T. 




Oak Ridge National Laboratory 


Repared for 

OAK RIDGE REsERvAnoN ENVIRONMENTAL 

REsLoRAnON PROGRAM 

*Managed by Martin Marietta Energy Systems, Inc. for the U.S. Department of Energy 


This page intentionally lefi blank.

The soluble salts of barium, an alkaline earth metal, are toxic in mammalian systems. They 

are absorbed rapidly from the gastrointestinal tract and are deposited in the muscles, lung 

and bone. Barium is excreted primarily in the feces. 

At low doses, barium acts as a muscle stimulant and at higher doses affects the newus 

system eventually leading to paralysis. Acute and subchronic oral doses of barium cause 

vomiting and diarrhea, followed by decreased heart rate and elevated blood pressure. Higher 

doses result in cardiac irregularities, weakness, tremors, anxiety and dyspnea. A drop in serum 

potassium may account for some of the symptoms. Death can occur from cardiac and 

respiratory failure. Acute doses around 0.8 grams can be fatal to humans. 

Subchronic and chronic oral or inhalation exposure primarily affects the cardiovascular 

system resulting in elevated blood pressure. A LOAEL of 0.51 mg bariudkglday based on 

increased blood pressure was observed in chronic oral rat studies (Perry et al., 1983), whereas 

human studies identified a NOAJX of 0.21 mg barium/kg/day (Wones et al., 1990; Brenniman 

and Levy, 1984). The human data were used by the EPA to calculate a chronic and 

subchronic oral reference dose (RfD) of 0.07 mg/kg/day (U.S. EPA, 1991, 1992). In the 

Wones et aL study, human volunteers were given barium up to 10 mg/L in drinking water for 

10 weeks. No clinically significant effects were observed, An epidemiological study was 

conducted by Brenniman and Levy in which human populations ingesting 2 to 10 mg/L of 

barium in drinking water were compared to a population ingesting 0 to 0.2 m@L 

No 

significant individual differences were seen; however, a significantly higher mortality rate from 

all combined cardiovascular diseases was observed with the higher barium level in the 65+ 

age group. The average barium concentration was 73 mg/L, which corresponds to a dose of 

0.20 mgkg/day. Confidence in the oral RfD is rated medium by the 

- 

EPA 

Subchronic and chronic inhalation exposure of human populations to bariumcontaining dust 

can result in a benign pneumoconiosis called ”baritosis”. This condition is often accompanied 

by an elevated blood pressure but does not result in a change in pulmonary function. 

Exposure to an air concentration of 5.2 mum3 for 4 hours/day for 6 months has been 

reported to result in elevated blood pressure and decreased body weight gain in rats 

(Tarasenko et al., 1977). 

Reproduction and developmental effects were also observed. 

Increased fetal mortality was seen after untreated females were mated with males treated with 

5.2 mg/m3 of barium. Similar results were obtained with female rats treated with 13.4 mg/m3. 

The NOAEL for developmental effects was 1.15 mg/m3. An inhalation reference concentration 

(RfC) of 0.005 mglm’ for subchronic and O.ooO5 m@m3 for chronic expure was calculated 

by the EPA based on the NOAEL for developmental effects (U.S. EP& 1992). 

These effects have not been substantiated in humans or other animal systems. 

Barium has not been evaluated by the U.S. EPA for evidence of human carcinogenic 

potential (U.S. EPA, 1991). 

1

1. INTRODUCI'XON 

Barium (CAS registry number 7440-39-3) is a divalent alkaline-earth metal found only in 

combination with other elements in nature. The most important of these combinations are 

the peroxide, chloride, sulfate, carbonate, nitrate, and chlorate. The pure metal oxidizes 

readily and reacts with water emitting hydrogen; it is chemically similar to calcium (Weast, 

R.C. 1987). The most likely source of barium in the atmosphere is from industrial emissions. 

Since it is usually present as a particulate form, it can be removed from the atmosphere by 

wet precipitation and deposition. Due to the element's tendency to form salts with limited 

solubility in soil and water, it is expected to have a residence time of hundreds of years and 

is not expected to be very mobile. Acidic conditions, however, will increase the solubility of 

some barium compounds facilitating their movement from the soil to the groundwater (U.S. 

EA, 1984). Trace amounts of barium were found in over 99% of the surface waters and 

finished drinking water samples (average values of43 pg/L, and 286 pgL, respectiveb) across 

the United States (National Academy of Sciences, 1977). 

2 MEI'ABOLISMANDDIspomnoN 

21. Aborption 

The soluble forms of barium salts are rapidly absorbed into the blood from the intestinal 

tract. The rates of absorption of a number of barium salts have been measured in rats 

following oral exposure to small quantities (30 m a body weight). The relative absorption 

rates were found to be. barium chloride > barium sulfate > barium carbonate. Large doses 

of barium sulfate do not increase the uptake of this salt because of its low solubility 

(McCauley and Washington, 1983; U.S. EPA, 1984). 

Systemic toxic effects have been observed following both oral and inhalation exposure. No 

absorption kinetics are available following inhalation exposure, although it is obvious that 

absorption does occur (US. EPA, 1984). 

Barium absorbed into the bloodstream disappears in about 24 hours, however, it is deposited 

in the muscles, lungs and bone. Very little is stored in the kidneys, k r , spleen, brain, heart 

or hair. It remains in.the muscles about 30 hours after which the concentration decreases 

slowly. The deposition of barium into bone is similar to calcium but occurs at a faster rate 

(Stokinger, 1981). "he half life of barium in bone is estimated to be about 50 days (Machata, 

1988). 

3. Metabolism 

About 54% of the barium dose is protein bound. Barium is known to activate the secretion 

of catecholamines from the adrenal medulla without prior calcium deprivation. It may 

displace calcium from the cell membranes, thereby increasing permeability and p'ovidhg 

2

stimulation to muscles. Eventual paralysis of the central nervous system can occur (Stokinger, 

1981). 

A tracer study in rats utilizing ''%a demonstrated that 7% and 20% of the barium dose was 

excreted in 24 hours in the urine and feces respectively. In contrast, calcium is primarily 

excreted in the urine. The clearance of barium is enhanced with saline infusion. (Stokinger, 

1981). 


3.1. Oral Expuns 

3.1.1. Acute T- 

3.1.1.1. Human 

A number of accidental barium poisonings have OCCUK& following the ingestion of barium 

salts. The estimated fatal dose of barium carbonate, a rodenticide, is about 5 grams for a 70 

kg human (Arena, 1979). The LDS for barium chloride is estimated at about 1 gram for a 

70 kg human (Machata, l-), and the LD, (lowest published lethal dose) is reported to be 

about 0.8 grams (Lewis and Sweet, 1984). The acute symptoms include: excess salivation, 

vomiting, diarrhea, increased blood pressure, muscular tremors, weakness, paresis, anxiety, 

dyspnea, and cardiac irregularities. A severe loss of potassium can account for some of the 

symptoms. Convulsions and death from cardiac and respiratory failure can occur. Magnesium 

and sodium sulfate are antidotal if taken soon after ingestion since either salt will result in 

the formation of insoluble barium sulfate and prevent further absorption. Survival for more 

than 24 hours is usually followed by complete recovery (Arena, 1979). 


Similar acute symptoms occur in animals, however higher daws are usually involved. The 

LDu, for rats is listed as 630 mgkg for barium carbonate; 118 mgkg for barium chloride, and 

921 mgkg for barium acetate (Lewis and Sweet, 1984). 

3.12 SubchronicToxicity 

3.121. Human 

An experiment testing the subchronic toxicity of barium chloride on human volunteers was 

conducted by Wones et aL (1990). The diets of 11 male subjects were controlled. They wcrc 

given 15 Uday of distilled and charcoal-filtered drinking water that contained 0 mg/I barium 

for weeks 1 and 2,5 mg/L for weeks 3 to 6, and 10 mg/L for weeks 7 to 10. NO clinically 

significant effects were observed in blood pressures, serum chemistry, urhalysk. or 

electrocardiograms. The 10 mg/L (021 mgkg/day) dose was identified as a NOAEL 

3

3.122 Animal 

Groups of 30 male and 30 female Charles River rats were exposed to barium chloride at 0, 

10, 50 or 250 ppm in drinking water for 90 days (Tardiff et al., 1980). The highest average 

dose in this study was calculated to be 45.7 mg/kg/day for female rats. No significant clinical 

signs of toxicity were observed. Blood pressure was not measured. 

McCauley et aL (1%) conducted drinking water studies in which six male Sprague-Dawley 

rats/group were given water containing 0, 10,100 or 250 mg/L barium for 36 weeb, or 1.10, 

100 or lo00 mg/L barium for 16 weeks. Female rats were given 0 or 250 mg/L for 46 weeb. 

Animals receiving the lo00 mg/L dose developed ultrastructural changes in the kidney 

glomeruli. No other effects were reported. 

Tardiff et aL (1980) exposed groups of 30 male and 30 female Charles River rats to 0, 10, 

SO, or 250 ppm barium (given as barium chloride) in drinking water for 90 days. A slight 

reduction in adrenal weights was seen in female rats with the 250 pprn (45.7 mg/kg/day) dose 

at 13 weeks and in male rats with the 50 ppm (8.1 mg/kg/day) and the 250 ppm (38.1 

mg/kg/day) doses at 8 weeb, no other adverse effects were observed. No clear dose effect 

or dose duration effect was seen with the adrenal weight decrease: therefore, the clinical 

significance is uncertain. 

3.13. CbOnicTadeity 

3.13.1. Human 

An epidemiology study conducted by Brenniman and Levy (1984) compared a human 

population ingesting barium levcis of 2 to 10 mg/L in their drinking water to a population 

ingesting 0 to 0.2 mg/L Although significantly higher mortality rates from all cardiovascular 

diseases were observed with the higher barium level in the 65 and over age group, there were 

no significant individual differences in blood pressures, strokes, or heart and renal diseases 

within the two groups. The average barium concentration for the mortality study was 7.3 

mg/L, which corresponds to a dose of 0.20 mg/kg/day assuming drinking water consumption 

of 2 Uday for a 70 kg human. 

3.132 Animal 

A series of experiments were performed in which groups of 52 male and female Long-Evans 

rats and 42 male and female Swiss mice were exposed to 5 mg barium/L (given as barium 

acetate) in drinking water for their lifetime (Schroeder and Mitchener, 1975a,b). The barium 

doses were about 023 and 0.825 mg/kg/day for rats and mice, respectively. No adverse clinical 

effects were observed, however, blood pressure was not measured. There was a slight but 

significant reduction in longevity of treated male mice when measured as the mean age at 

death of the last surviving 10% of animals. The overall average life span of the group, 

however, was about the same as the control group (U.S. EPA 1984, US. EPA, 1989) 

Perry et at (1983) exposed 12-13 female weanling rats/pup to 0,1,10 or 100 pprn barium 

(given as barium chloride) for up to 16 months. Average doses were calculated to be 0,0.051, 

051 and 5.1 mg/kg/day (US. EPA, 1985). A clinically significant increase in average blood 

4

pressure was observed in the highest dose group; a slight but statistically significant increase 

was seen in the 10 ppm (0.51 mgAcg/day) dose group. The controlled diet, which restricted 

the intake of trace metals, calcium and potassium, may have contributed to the effect. 

3.1.4. Developmental and Reproductive Taxicity 

information on developmental and reproductive toxicity in humans or animals following oral 

exposure was unavailable. 

3.15. Dcse 


ORAL RfD,: 

0.07 mg/kg/day (U.S. EPA, 1992) 

UNCERTAINTYFACI'OR 3 

NOAEL: 

021 mgkg/&y 

PRINCIPAL STUDIES: 

The same studies and comments apply to both the subchronic and chronic RfD derivations. 

See Section 3.152 

3.152 cbonic 

ORAL IUD; 

0.07 mgAcg/day (U.S. EPA, 1991) 

UNCERTAINTYFACI'OR 3 

MODIFYINGFAOR 1 

NOAEL: 

021 mgkg/day 

CONFIDENCE: 

Study: 

Medium 

Data Base 

Medium 

RfD: 

Medium 


PRINCIPAL STUDIES. Wones et aL (1990); Brenniman and Levy (1984). 

coMMEN?s: The RED values are based on a weight-ofevidence approach ushg 

subchronic to chronic human drinking water studies. Tbe uncertainty factor 

accounts for protecting sensitive individuals and is reduced from the usual factor 

of 10 because the selected studies examined the population judged most at risk. 

321. AcuteToxicity 

Barium carbonate dust has been reported to be a bronchial irritant. Barium oxide dust is 

considered a dermal and nasal irritant (Stokinger, 1981). 

. 

5

3.2.2 SubchronicToxicity 

3.2.21. Human 

Industrial workers exposed to barium dust., usually in the form of barium sulfate or 

carbonate, often develop a benign pneumoconiosis referred to as ”baritosis”. Because of the 

radiopacity of barium compounds, this condition can be specifically diagnosed radiologically. 

After removal from the sources of exposure, baritosis is reversible in most cases. Baritosis 

results in a significantly higher incidence of hypertension, but no changes are usually seen in 

pulmonary function (Stokinger, 1981; U.S. EPA, 1991). 

Male rats were exposed to 1.15 and 5.2 mghn’ of barium carbonate dust for 4 houdday for 

6 montbs. The high dose animals developed increased arterial pressure; decreased body 

weight gain; decreased blood levels of hemoglobin, sugar, protein, cholinesterase and 

thrombocytts; increased blood levels of leukocytes, phosphorous and alkaline phosphatase; 

increased urine calcium; and perivascular and peribronchial sclerosis in the lungs. (U.S. EPA, 

1984; Tanqenko et aL, 1977). 

323. ChronicToxicity 

323.1. Human 

Baritah also occurs in workers chronically exposed to barium containing dust. Hypertension 

is the only reported adverse clinical effect (US. EPA, 1991). 

Information on the chronic inhalation toxicity of barium in animals was unavailable. 

3.24. -tal and Reproductive Toxicity 

Tarasenko et al. (1977) performed a series of experiments designed to test for possible 

reproductive and developmental effects. Increased fetal mortality was observed following the 

mating of males exposed to barium carbonate (52 mg/m3 air) with untreated females. 

Decreased sperm motility was observed in males treated with 226 mg/m’ the mating of 

females exposed to 13.4 mg/m3 for 4 months also resulted in inmasad fetal mortality and a 

general underdewelopment of the newborn pups. Ovarian follicle atresia was seen in female 

rats exposed to 3.1 mg/m3. There were no significant adverse effects with the 1.15 mg/m3 

concentration (U.S. EPA, 1984). 

33.1. Subchroaic 

INHALATION RfC,: 0.005 mg/m3; 0.001 mg/kg/day (US. EPA, 1992) 

UNCERTAINTYFACTOR 100 

6

NOAEL: 

PRINCIPAL STUDY 

1.15 mg BaCOJm3 given 4 hdday (U.S. EPA, 1992) 

The same study and comments apply to the subchronic 

and chronic RfC. The study is described in section 

324. 

3-32 

cbmnic 

INHALATION RfC,: 0.0005 mg/m3; O.OOO1 mg/kg/day; (U.S. EPA, 1992) 

UNCERTAINTY FACTOR. loo0 

NOAEk 

1.15 mg BaCOJm’ @en 4 hdday (U.S. EPA, 1992) 

PRINCIPAL STUDY Tarasenko et aL, 1977. 

COMMENTS: The 1.15 mg/m3 dose was a NOAEL,, however the 5.2 mum3 dose, 

which resulted in developmental effects, was used as the basis €or the RfC 

calculations. 

33. 

33.1. 

33.1.1. 

other Routes of Expure 

hte Toxicity 

HUman 

Barium oxide dust is considered to be a dermal and nasal irritant (Stokinger, 1981). 

33.12 

Animal 

A number of experiments have utilized intravenous and subcutaneous injections to measure 

lethal levels of soluble barium compounds. LD, values €or barium chloride, nitrate and 

acetate were determined in two strains of mice by intravenous injection (Syed and Hosain, 

1972). The affected animals either died within one hour or survived the treatment. The LD, 

values obtained were: 8.128.49 and 1132 mg bariumkg for the chloride, nitrate and acetate, 

respectively, in Swiss-Webster mice; 19.20, 20.10 and 2331 mg barium/kg for the chloride, 

nitrate and acetate, respectively, in ICR mice. Although the relative toxicity of the barium 

salts remained the same, there was an unexplained two-fold difference in the LD, values 

between the two mice strains. 

Tbe LD, has been determined by subcutaneous injection in mice to be 10 mgkg €or the 

barium nitrate and chloride salts. The LDb in rabbits was 55 mgkg €or the chloride and 96 

mg/kg for the acetate salts. The LDb values vary widely with the route and test animal. For 

example, with barium chloride the LDb value €or oral administration to rabbits is 170 mgkg, 

whereas the value for subcutaneous injection is 55 mgkg. Subcutaneous injection in mice 

results in a value of 10 mgkg, which is higher than the LD, value for intravenous injection 

in the Swiss-Webster strain (Lewis and Sweet, 1984). 

332 subchronicTaxicity 

Information on the subchronic toxicity in humans and animals is unavailable. 

7

333. CbrOnicToxkity 

Information on the chronic toxicity in humans and animals is unavailable. 

33.4. Dmhpmental and Reproductive Toxicity 

Information on the developmental and reproductive toxicity in humans and animals is 

unavailable. 

3.4. 

3.4.1. 

3.4.1.1. 

Target-tiCalEEeCtS 

-m-K== 

mTa%w) 

1. Cardiovascular system: Subchronic to chronic symptoms include increased blood 

pressure and increased incidence of cardiovascular disease in humans. An acute 

overdose can result in cardiac irregularities. Convulsions and death from cardiac 

and respiratory failure can occur. 

2 Nervous system: Acute to subchronic symptoms include weakness, tremors, 

anxiety, and dyspnea. An acute overdose can result in convulsions and death from 

cardiac and respiratory failure. 

3.4.12 

-Targc& 

1. Gastrointestinal system: Acute to subchronic symptoms include excess salivation, 

vomiting and diarrhea in humans. 

3.42 

3.421. 

-ET== 

primaryT=Sw 

1. Cardiovascular system: Symptoms inciude increased blood pressure in humans. 

2 Reproduction and development: Subchronic exposure of rats resulted in 

decreased sperm motility and ovarian follicle atresia. Increased fetal mortality and 

underdevelopment of newborn pups were also reported. 

3.4a 

-TargCt(r) 

1. Lungs: Subchronic to chronic exposure in humans results in a pneumoconiosis 

known as "baritosis" that usually does not adversely affect pulmonary function. 

8

4.1. 


Information on the carcinogenicity of barium in humans is unavailable. 

4-12 Animal 

No significant differences in tumor incidence were found in either rats or mice in the 

lifetime exposure experiments of Schroeder and Mitchener (1975a,b), described in Section 

3.13.2. 

Information on the carcinogenicity of barium in humans and animals is unavailable. 

Information on the Carcinogenicity of barium in humans and animals is unavailable. 

4.4. EPA W&htd-EvidcDoc 

Barium has not been evaluated by the US. EPA for evidence of human carcinogenic 

potential (U.S. EPA, 1991). 

Data are insufficient to calculate a slope factor for barium. 

9

Arena, J.M. 

Publisher, Springfield, Ill. pp. 173-179. 

5. REFERENCES 

1W9. Poisoning - Toximlogy - Symptoms - Treatments. Charles C. Thomas, 

Brenniman, G.R and P.S. Levy. 1984. High barium levels in public drinking water and its 

association with elevated blood pressure. 

Calabrese, Ed. Princeton Scientific Publications, Princeton NJ. pp. 231-249. 

In: Advances in Modem Toxicology IX, EJ. 

Lewis, RJ. and D.V. Sweet, eds. 1984. Registry of Toxic Effects of Chemical Substances, 

Vol. 1. US. Department of Health and Human Senrices, Public Health Service, Centers for 

Dkase Control, Nationai Institute for Occupational Safety and Health, Cincinnati, OH. 

Machata, G. 1988. Barium. In Handbook on Toxicity of Inorganic Compounds, eds. H.G. 

Seiler and H. Sigel, Marcel Dekker, Inc. pp. 97-101. 

McCauley, P.T. and LS. Washington. 1983. Barium bioavailability as the chloride, sulfate or 

carbonate salt in the rat. Drug Chem. Toxicol. 6(2): 209-217. 

McCauley, P.T., B.H. Douglas, RD. Laurie and RJ. BuU 1985. Investigations into the 

effect of drinking water barium on rats. Environ. Health Perspect. Vol. IX, EJ. Calabrese, 

Ed. Princeton Scientific Publications, Princeton, NJ. pp.197-210. 

Perry, H.M., SJ. Kopp, M.W. Erlanger and EF. Perry. 1983. Cardiovascular effects of 

chronic barium ingestion. In: Trace Substances in Environmental Health, ?MI, D.D. 

Hempha Ed. Proc. Univ. Missouri’s 17th Ann. Conf. on Trace Substances in Environmental 

Health. University of Missouri Press, Columbia, MO. pp. 155-164. 

Scluoeder, H. and M. Mitchener. 197%. Life-term studies in rats: Effects of aluminum, 

barium, beryllium and tungsten. J. Nutr. 105: 421-427. 

Schroeder, H. and M. Mitchener. 197%. Life-term effects of mercury, methyl mercury and 

nine other trace metals on mice. J. Nutr. 105: 452-458 

Stokinger, H.E 1981. The Metals. In Patty’s Industrial Hygiene and Toxicology, Vol2A, eds. 

G.D. Clayton and EE Clayton, John Wiley & Sons, New Yort pp. 1531-1537. 

Syed, I.B. and F.Hosain. 1972 Determination of ID50 of Barium Chloride and Allied 

Agents. Toxicol. AppL Pharm. U: 150.152 

Tarasenko, M, 0. Promin and A Silayev. 1977. Barium compounds as industrial poisons (an 

experimental study). J. Hyg. Epidem. Microbiol. Immunol. 21: 361-373. 

Tardiff, RG., M. Robinson and N.S. Ulmer. 1980. Subchronic oral toxicity of barium 

chloride in rats. J. Environ. PathoL Toxic01 4(5-6): 267-276. 

10

U.S.EPA 1984. Health Effects Assessment for Barium. Prepared by the Office of Health 

and Environmental Assessment, Environmental Criteria and M ment Ofice, Cincinnati, 

OH for the Office of Emergency and Remedial Response, Washington, D.C. 

U.S.EPA 1985. Drinking Water Health Effects Criteria Document on Barium. Prepared 

by the Office of Health and Environmental Assessment, Environmental Criteria And 

Assessment Office,Cincinnati, OH for the Office of Drinking Water, Washington, DC. NTIS 

PB &118031. 

U.S.EPA 1989. Reportable Quantity Document for Barium and Compounds. Prepared by 

the Office of Health and Environmental Assessment, Environmental Criteria and Assessment 

Office,Cincinnati, OH for the Office of Solid Waste and Emergency Response, Washington, 

Dc 

US. EPA 1991. Integrated Risk Information System (IRIS). Health Risk Assessment for 

Barium. On line. (Verification date 6/21/90.) Office of Health and Environmental Assessment, 

Environmental Criteria and Assessment Office,Cincinnati, OH. 

U.S.EPA 1992. Health Effects Assessment Summary Tables. Annual FY-92 Prepared by 


Office, Cincinnati, OH for the Office of Emergency and Remedial Response, Washington 

DC. OHEA ECAO-cIN-821. 

US. National Academy of Sciences. 1977. Drinking Water and Health. Safe Drinking 

Water Committee, Advisory Center on Toxicology, Assembly of Life Sciences, National 

Research Council. Washington, D.C. pp 211-212 

Weast, RC, J.A Melvin and W.H. Beyer (4). 1987. CRC Handbook of Chemistry and 

Physics. CRC Press, Inc, Boca Raton, Florida, pp B-9. 

Wones, RG., B.L Stadler and L.A. Frohman. 1990. Lack of effect of drinking water barium 

on cardiovascular risk factor. Environ. Health Perspect. 85: 1-13. 

11

September 1992 

Prepared By 

Andrew Francis 

Chemical Hazard Evaluation Group 

Biomedical Environmental Information Analysis Section 

Health and Safety Restarch Division 

Oak Ridge National Laboratmy* 

Oak Ridge, Tern- 

Prepared for 

OAK RIDGE RESERVATION ENVm0-a 


*Managed by Martin Marietta Energy Systems. Inc, for the US. m a t 

Contract No. DE-Aa)5840R21400 

of &q

Thfr page mtcntionally lefi blank 

2

Benz[aanthracenc, along with a number of other polycyclic aromatic hydrocarbons, arc 

natural products produced by the incomplete combustion of organic materiai. The arrangement 

of the aromatic rings in the benz[gJanthracenc molecule gives it a "bay region" often correlated 

with carcinogenic properties. In general, the bay-region polycyclic aromatic hydrocarbons and 

some of their metabolites arc bmam to react with ceiiular macromolecules, including DNA, which 

may account for both their toxicity and carcinogenicity. The inducible mixed-function oxidase 

enzymes oxidiz benz(@&acme 

to form metabolites with increased water solubility that can be 

efficiently excreted in the urine. A minor product of this axidation, a bay-region diol epoxide, 

reacts readily With DNA and has been shown to be highly cardnogenic (us. EA, 1980, 1984; 

Jerina, et aL, 1977). 

The toxic efftcts of benz(glanthracene and simiiar potycyClic aromatic hydrocarbons arc 

primarily directed toward tissues that contain proliferating cells. Animal studies indicate that 

exposure to bay-region polycyclic aromatic hydrombons can damage the hematopoietic system 

leading to progressive anemia as well as agranulocytosis (Robinson, et aL, 1975; Cawein and 

Sydnor, 1968). The lymphoid system can also be affected resulting in lymphopenia. Toxic effects 

have been OM in the rapidly dividing cells of the intestinal epithelium, spermatogonia and 

resting spermatocytes in the testis and primary ooc$e of the ovary (Philips et al, 1973; 

Mackinzic and Angevine, 1981; Kraup, 1970; Ford and Huggins, 1963; Mattison and ThorgeirsJon, 

19n, US. EPA, 19&0* 1984). Most of these effects have occuffcd following both oral and 

parcntcral exposure. Epithelial proliferation and cell hyperplasia in the respiratory tract have 

bew reported following subchronic inhalation exposure (RemikSchuller and Moht, 1974; 

Saffiotti et & 1968). However, because of the lack of quantitative data, neither a reference dose 

nor 8 reference concentration have been derived (VS E9k 191). 

The primary conccrii with beaanthraccne exposure is its potential carcinogenicity. There 

is no unequivocal dircct evidence of the carcinogenicity of the compound to humans, however, 

bem&Janthraccne and other known carcinogenic polycyclic aromatic hydmaubons arc 

components of cod tar, soot, coke oven emissions and tobacco smoke. There is adequate 

evidence of its carcinogenic properties in animais. Oral exposures of mice to benz[aanthraccne 

have resulted in hepatomas, pulmonary adenomas and forestomach papillomas (Klein, 1%3; Bock 

and King, 1959; US. EPA, 1991). The EPA ueight-ofcvidenct classification is: B2, probable 

human Carcinogen, for both oral and inhalation cxposure based on adequate animal evidence and 

no human evidence (US. EPA, 1991). A slope factor has not been derived specifically for 

benz(&Janthracme by the EPA (US. EPA, 1991). Howlcvtr, an oral slope factor of 73 

(mg/kg/dayr' has becn calculated for benzDwpyrcne based on the incidence of stomach tumors in 

mice treated with bcnzo(&yrcne (Neal and Rigdon, 1967; US. EPA, l-, 19&$1992a). A 

drinking water unit risk of 21E-4 (pg/Lrl has also been calculated for bep;oo(&yene (US. EPA, 

1992a). An inhalation slope factor oE 6.1 (mg/kg/day)" (US. EPA, 1992b) was calculated for 

benu>[@yrene based on the incidence of respiratory tumors in golden hamsters treated with 

benzo a pyrene crriyssen et aL, 1981; US. EPA, 1980; 1984). An inhalation unit risk of 1.E-3 

(p@'$ has also been calculated for benm~pyrcne (US. EPA, 1992b).

1. KNTRODUCXION 

-- 

Bcnz[aanthraccne (CAS registry number 56-55-3) is a poiycycfic aromatic hydrocarbon 

containing four aromatic rings two of which share carbons with only one other ring. It is soluble in 

alcohol, ether and benzene but practically insoluble in water (9.4 pgh @ 25°C) (us. =A, 1984; 

Weast, 1987). There is no commercial application for be@@mthraccne, however, it is a ubiquitous 

contaminant formed during the incomplete combustion of organic material. kaz(Jantbraccne.iS - 

found in various kinds of smoke and flue gases, tobacco smoke, tobacco smokc condcnsatc, 

automobile exhaust, roasted coffee and in charcoal broiled, barbccutd or smoked meats. It is ako 

found in creosote, coal tar, petroleum asphalt, and a variety of foob, bduding vcgetablc oils and. 

baker's ycas~ It is an atmospheric con taminnnt near pomr plants and busy highways, and tends to 

bind to particulate matter in the atmosphere. The p- removal mcchaojsm from the atmosphae 

is thought to be ozonolysis reactions, where the arpected half-life is less than 1 day to scvcral weeks 

dependent on the nature of the particuiatc matter to which it is adsorbed. Benz[ganthtaceac is also 

adsorbed to soil particulates where it undergoes degradation by microor@ms. It can persist in the 

soil from days to yean depending on the adsorbent and the mlcrootganisms prcscrJt 'Ihe water 

insolubility of benz[aanthraccnc limits its movement through the soil (Sittig, 1985; Sax, 1981; US. 

EPA 1984). 

2l. ABSORFITON 

Animal studies have shown that polycyclic aromatic hydrocarbons in genCrai and 

bcx@&uithraccnt in particular are absorbed from the gastrointestinal tract (Ree~ et & 1971) 

Specifsc inhalation studies on b@&nthraccne were not available, but poiyammatic hydrocartKrmr 

as a class are cotlsidcred capable of crossing epithelial membranes. Studies with benzoMpyrcne ad 

pyrcne have shown rapid pulmonary absorption by rats (Kotin et aL, 19&9; Vainio et aL,.l976 

Mitchell and Tu, 1979). Quantitative data on bcnzjdanthraccne absorption arc not available for 

either the oral or inhaiation routes. 

Specific studies on the dutriiution of bez@danthracene in humans were not available. 

Howcvcr, animaI studies using related porycvclic aromatic h#mcarbons, chiefly beazo[alm-- 

indicate that these compounds arc distriiuted in a wide variety of body tissues, cventuaIly becamiDg 

localized primarily in fatty tissues. Appmxhatdy 80 to 90% of the adminijtered b enzom 

disappeared from the blood within 6 minutes following 8 single intravenous 10 pg injection. A m@ - 

equiliiriumwasrcachcdbctwecnthebioudandliver. Tliehalftime€orbamj;lllpyrcnerundfromthe 

liver was about 10 minutcs; huwmer, the disappearance was bip&sic with a rapid initial p b - 

followed by a slower phase lasting 6 hours or longer. Removal from thc brain was slower than hrom 

the liver with bcnzo~pyrenconcentration increasing in fat tissucS for over 6 hours (schlede, et 

1970a). The disappearance of bcnzo[&yrcne fr~m aU tissues is acetltrattd by pretreatment with 

benzo[&yrcne ?his pretreatment indm microsod enzyme activities that arc h h d h the

oxidation and detoxification of polycyclic aromatic hydrocarbons (Schlede, et aL, 1970b; US. EPA, 

-- 

1980). 

The arrangement of the aromatic rings in the molecule creates what has been termed a "bay 

region" imparting certain properties to the polycyciic aromatic hydrocarbons. Benz[aanthracene and 

other bay-region polycyciic aromatic hydroahom undergo oxidation by microsomal enzymes 

(cytochrome f-450 miroed-function oxidase system) to excretabie metabolites. Unfortunately, some 

intermediary metabolites, chiefly the bay-region diol epoxides, can reaay react with DNA and ptiy 

increase carcinogenic activity. The bcnz[aJanthracene 3,4diolepoxide is a very minor metabolite of 

benz[danthracene oxidation, which may account for its weak tumorigenic properties when compared 

to some other bay region polycyciic aromatic hydrocarbons (m et aL, 1984, Jerina, et at, 1977). 

24 EXCREI'ION 

The oxidized products produced by the cytochrome P-450 mixed-function oxidase systcm exhibit 

increased reactivity and wig undergo conjugation With intracellular mOlecuies such as glutathione 

resulting in compounds that have inrrtased solubility in water and can be cxcretcd efficiently in the 

urine. Less soluble metabolites and the parent compound can be excreted through the hepatobiliary 

system in the feces. prior exposure to a polyqdic aromatic hydrocarbon results in the induction of 

the mixed-function oxidase enzymes and greatly in- the rate of excretion by increasing the 

formation of water soluble metabolites (US. EPA, 1980). 

3.1. ORAL- 

3.1.1.1. Human 

Direct evidence of acute toxicity resulting from oral expure of humans to bcwmthracene - 

is unavailable. 

Specific studies on the acute oral toxicity of benzfalanthracene in animah were not available,. 

howtver, several effects arc common to the.poiycyclic aromatic hydrocahn class of compounck. 

Genedy thcse compounds and their metabolites are moJt toxic to targets that contain rapidly 

proliferating cck They arc known to bind to proteins and nucleic acids and may interfere with the. 

processes involved in ccll growth and division (US. EPA, 1980). The hematopoietic and lymphoid - 

system arc common targets, as well as the intestinal cpitheiium and the testis. 

shgle feedings of 112 or 133 mg dimethyl be@danthraccnentg body weight of female rats. 

re~dted in severe depression of hematopoietic and lymphoid precursors. Since only the more rapidly

proliferating cells wcfc affccttd by benzwanthracenc, the authors suggested inhibition of DNA 

replication was involved in the toxicologic response (Cawin and Sydnor, 1%8, US. EPA, 1980). In 

another experiment, female rats given 300 mg dimethyl benzfdanthracenekg by gavage displayed 

injury to the intestinal epithelium and developed a progressive anemia. Mortality of rats was about 

65% at this dose (Philip et aL, 1973). 

3.12 Subcl~~nicTdaicity 

No relevant reports of human subchronic oral exposure to benz[aanthracene weft available. 

Specific data on the toaic effects of subchronic exposure of animals to benzjdanthracene were -- 

not available. Experiments with other polycyclic aromatic hydrocarbons indicate that subchronic and 

acute exposures result in similar effects. Oml exposure of mice to 120 mg benm[&yrcne/kg body 

weight/day for 6 months resulted in sevccc aplastic anemia. The inducibility of the microsomal mkifunction 

oxidase enzymes was shown to influence survival Poorly inducible mice (AKWN mice, 

Ahd/Ahd type) died within 4 weeks. whereas the inducrile mice survivcd for the 6 month period. This 

acpCriment demonstrate the detox,&ation of a polycyciic aromatic hydrocarbon by the mixed- . 

function oxidase system (Robinson et aL, 1975; US. EPA 1984). 

3.l3.1. 

Human 

No r eht 

3.132 Animal 

reports of human chronic oral exposure to bc@&mthraccne were available. 

-. 

Chronic experiments designed to demonstrate the carcinogenic nature of polycyclic aromatic 

hydrocarbons were inadequate to determine noncarcinogenic effects (U.S. EPA 1984). 

3.L4.L Hualall 

Studies dcscrr'bing developmental and reproductive effects in humans following oral exposure to 

-anthracene were not available. 

Specifid data on dcveiopmental and reproductive toxicity resuiting from exposure of animah to 

~anthra#newercunavailable. H~,studiesusingsimilarpo~caromatic hydrocarbonr 

indicate that exposure to theseannpouads muyresultin rcproductiveefkts. Rigdon and Rands 

(1964) fed frrnalr rats SO mg beruxr~pyrcnc/kg/day for 35, months induding the gestation period 

IncrtaJed feral mortality was reen in all 7 trcated females. The treated dams did not show gn#s sip

of toxicity, although failure to lactate resulted in the death of the only surviving offspring Within 3 

days of birth. 

Decreased fertility and gonadal weights in both sexes were seen in the offspring of mice treated 

orally with 10 mg/kg/day benzo[g]:lpyrene during gestation. A dose of 40 mg/kgday resulted in almost 

compiete sterility. No effect on fetal body weight or survival of the pups was reported (Mackendt 

and Angevinc, 1981). 

Kraup (1970) reported the destruction of small oocytes and the reduction of the numbers of 

growing and large OOCytCS following oral administration of dimethyl benz[danthracene to mice (US. 

EPA, 1980). 

A reference dose for chronic or subchronic oral exposure to k@danthracene is not available. 

32 INHAIATIONEXPOSURES 

321. AatttToxicity 

321.1. Human 

Information on the acute toxicity resulting from the inhslation exposure of humans to 

bcnz[3l)anthraccne was unavailable 

32L2 Animal 

Information on the acute tarticity resulting from the inhalation exposure of animak to 

benz(4anthracenc was unavailablc 

3221. Human 

Information on the toxicity resulting from the subchronic inhalation cxposwc of humans to 

benzj~antbracenc was unavailable. 

Information on the toxicity resulting from the subchronic inhalation exposure of animals to 

bcnz~anthraccne was unavaiiabie. However, subcbronic inhnlation exposures of golden hamsters 

to other potycyctic aromatic hydrocarboos, including dimethyl bcnz(&nthracene, benzo~pyrenc. and 

di’benzo[~]pyrene. caused epithelial proliferation and cell hyperplasia in the respiratory tract (total 

weekly doae of benzo[&.pne was 0.63 mg). These effects lllt~ually seen without marked 

infiammation or necrwsis by the 11th wcek of exposure, and p d the dcvclopmcnt of rc~phtary 

tract tumors (Rd-SchuUet and Mob, 1974 SaottL et al, 1968; US. EPA 1980). 

.- 

7-

33. ChmicTaxicity 

323.1. Human 

- - 

Idomation on the toxicity resulting from the chronic inhalation exposure of humans to 

benzjdanthraocnc was unavailable. 

3232. Animal 

Infarmation on the toxicity resuiting from the chronic inhalation exposure of animals to 

benz[i&nthraccne was unavailable. Experiments utilizing the chronic c~rposurt of animals to 0th 

polycyclic aromatic hydtocarbons wen designed to study carcinogenesis and are not suitable for 

describing toxicity efftcts. 

324.1. Human 

No~reports were available on developmental and reproductive effects in humans following 

inhalation exposurt to bcnz(danthracenc. 

3242 Aaimal 

No reports were available on developmental and reproductive effects in a&& 

inhalation exposure to be4gJanthraCene. 

following 

A reference concentration for chronic or sukrhronic inhalation v urt to beatfaanthracare 

is not avaiiable. 

33. OTIIER ROuflEis OF EXPOSURE 

33.1, AeutcT0;xiCity 

33.1.1. Human 

Dm evidence of acute toxicity resulting from exposure of humans to bcnzManm:b 

other routes is unavaiiable 

Smglc injections ofpoiycyclic aromatic hychcabus have demonstrated the toxic effects of the 

compounds on rapidly proliferating cells. An intraperitoncai injection of 3-mcthyicholanthrwe (03 

to 1.0 mg) in 12 hour to 9 day-oid mice resulted in severe degeneration of the thymus, reduction ki 

weight of the splecn and mesenteric lymph nodes, degcncratim of bone marrow dls, and retardation 

of thyroid gland dcvc1opmcnt. Increased mortaiity was observed with newborn mice after treatmeat 

(YaSuhh 1961). 

8-

Philips et al. (1973) gave male rats a single intravenous injection of 50 mgkg of 7,12- 

dimethylbenz[g]anthracene. The targets that were affected included darriage to the intestinal 

epithelium, atrophy of the hematopoietic elements, decreased weight of lymphoid organs, 

agranulocytosis, lymphopenia, and progressive anemia A similar experiment demonstrated a 

decreased [“C]-labtlcd thymidine incorporation into the DNAin the cells of small and large intesthe, 

spleen, bone marraw, cenrical lymph nodes, thymus, and testis. This inhibition, which was as high as 

90%, was seen 6 hours after treatment and indicated a reduction in DNA synthesis b these orgm, 

which normally contain rapidly dividing cek 

3321. Human 

Subchronic or chronic dermal exposure of workers to materials such as coal tar. mineral 0% and 

petroleum waxa containing benz[&nthracene and other polycpctic aromatic h-ns rcsultcd 

in the devciopment of dermatitis and hyperkeratoses (Huepcr, 1963; NB, 1972)- 

33zL Animal 

Topical application of benz(~anthraccne and other poefic aromatic hydrocarbons to ~~OUSC 

skin results in the destruction of sebaceous glands, hypcrplssia hypcrkeratoais, and ulceration of the 

skin. The sebaceous glands arc the most sensitive stn~cturcs to polycyclrc hydrocarbolu. A. 

correlation exists between the carcinogenic activity of bcnz[&xUhractne and its t ~dv toward the 

scbactous glands (Bock 1961). 

Weeklysubcutaneous injections of diknzwanthracenc, benz(&anthracene and anthracene in 

Ilnioc resulted in dilated lymph sinuses and a decrease of lymphoid cells Within 40 week The lymph 

glands contained increased numbers of reticulum (stem) cells and an accumulation of iron. Decnased 

spleen weight was obscmd in the mice receiving dibcnz[g&]anthfacene (Hoch-Ugeti, 1941). 

Lasnit& and Woodhouse (1944) studied the effects of subcutanwus injections of 

dibenz[wanthraccne, benzo[aJpyrcne, 3-methylcholanthrcne, and anthracene on lymph nodes in rats. 

Injections were given 5 times weekly for scvcral week and, with the exception of anthracene, resulted 

in extravascular red blood cells in the lymph spaces and the presence of large pigmented cells. 

333.1. Human 

Subchronic or chronic e ~ ~ ~ of ~ uthe rskin c to polyqdk aromatic hydrocarbon-neg 

materials can caw dumatitis in humans (scc&on 3321.). 

chronic exposure experiments using various route wcre designed to examine cancer end points 

and are not generally useful as toxicity studies. The qualitative resultt, however, gcncdy reflect 

those obscnnd for the cf€ccts from single or-subchronic exposures to polycyclic aromatic 

hydmcahons (US. EP& 1980). 

9-

33.4. Dercbpmental and Reproductive Toxicity 


-- 

Information on the developmental and reproductive toxicity of beN4anthracene in humans by 

other routes of exposure was unavailable. 

33.42 Animal 

Single intravenous injections of 0.5 to 20 mg dimethyl be@danthracene in =day old rats or 

injections of 5.0 mg in 6O.day old rats resulted in degeneratk change in the testis 38 to 40 days 

after treatment These lesions included the destruction of spermatogonia and resting SpennatOcJrter 

(Ford and Huggins, 1963). In a similar acpcrimcnt, the destruction of primary in mice was 

also seen after injection of 3-mcthykholanthrcn~. The effezt in this experiment was correiated with 

the ability of the mice to induce the microsomal miroed-function oxidase enqmes following treatment 

(Mattison and Thorgeirson, 1977). 

3.4. TARGEI' ORG-CAL EFFECIS 

3.4-1.1. Primarjr T-r) 

1. Hematopoietic system: Animal studies have shown atrophy of the hematopoietic elements 

leading to progresshe anemia and agrarrulocytosit after exposure to polycyclic aromatk 

w==bo= 

2, Lymphoid sysw Shrinkage of lymphoid organs and rymphopeaia have been noted in - 

animals cxposcd to potyEgclic aromatic hydrocarbons. 

3. Intestinal epithelium: Damage to the rapidly growing cpithefial cells of animals has bcen 

okrved following cxposute to polycyclic aromatic hydrocarbons 

4. Testis or wary Destruction of the spermatogonia and resting spermatocytes in males and 

the primary oocytes in female, following exposure to poiycyclic aromatic hydrocarbonJ. 

3.421, RiumryTm 

1. Fbsphtory tract: Animal experiments have shown epithctial pmlEeration and-cell 

hyperplasia following rubchronic exposure topolycyclic aromatic hydrocarboas. This effect 

be a preneoplastic lesion. 

. 

10

4. CARcINoGmm 

4.1. ORALExposuREs 


Data relating human oral exposure to benz(4anthracene and subsequent cancer deveIopment 

was not available. -anthracene is a component of mixtures that have been associated with 

human C~IICCK such as coal tar, soots, coke oven emissions, automobile exhaust, and cigarette smoke 

(USEPA 1980; 1984). 

4.12 Animal 

Klein (1963) treated male mice with 3% benz[&nthraoene in Method-aerosol 0.T.by gavage 

3 timesheck for 5 weeks. Timm~ were evaluated on days 437-444 and 547 after the initiation of 

treatment. An increased incidence of pulmonary adenomas and hepatomas was noted at alI 

observation times when compared with controls. The incidence of pulmonary adenomas reached 95% 

and the incidence of hepatoma reached 100% after 547 days. Back and King (1959) administered 

8 or 16 gavage treatments of benzjgJanthracene to mice at 3-7 day intexvals over a 16.month period. 

They found forestomach papiilomas in the treated groups (un) and none in the control group (ODs). 

Treatment of Swiss mice with benzo[&yrcne, a related po&fic aromatic h m Q also 

dted in stoznach tumors. Mice were fed doses ranging between 1 and 250 ppm in the diet for 110 

days. The appearance of squamous cell papillomas and carcinomas was roughly dose dependent. The 

cancer incidences observed were for the control, 1/23 for 2.6 rng/kg/day9 1/40 for 53 mglkglday, 

4/40 for 5.S mwday, and 19i23 for 13.0 mg/kg/day (Neal and Rigdon, 1967). 

42 INHALATION- 

421. Humnn 

Data on human inhalation cxposure to benz[danthraccne and subsequent cancer development 

was not available. Be@gJanthraccne is a component of mixtures containing other polycyclic aromatic 

hydrocarborrs that have been associated with human cancers such as coaj tar, soots, coke oven 

emissions, automobile exhaust, and cigarette smoke (US. EPA, 1980; 1984). 

422 Animal 

Data on inhalation exposure of animals to ~anthnccne and substqucnt cancer 

dcvtlopment were not available. There arc studies, howevcr, !hat show tumor development following 

inhalation of related polycyciic aromatic hydmaubons Golden hamsters wcposed by inhalation to 

9.5 m&n3 benzo[j&yrcne for 45 houdday for 10 wee4 followed by 3 hodday for up to 675 d ~ , 

developed tumon of the naral cavity, largnx, trachea and pharyrm The high dose a b caused tunron 

of the upper digestive tract (Thysen et aL, 1981). 

11

43. OTRER ROUTES OF EXPOSURE 

43.1. Human 

.- 

Data relating other routes of c~rposurto benz[danthracene and subsequent cancer d-bprncat 

were not available. BenzjgJanthracene is a component of mixtures that have been d ated with 

human cancers such as coal tar, soots, cokc oven emissions, automobile exhaust, and cigarette smoke 

(U.S. EPA, 1980; 1984). 8 

432 Animal 

Intraperitoneal injections of mice with bex4&inthracene in dhethylsutfojoide on days 1,8, and 

15 of age (total dose of 638 pglmouse) resulted in liver adenomas and carcinomas in male mice (31/39 

total tumors treated, 25/39 adenomas, 2/28 total controls) and pulmonary adenomas in female mice 

(6/32 treated, ODZ coxitrob) 1 year after expo~ure (wislocki et al, 1986). 

Subcutantous injection of mice with bcnzjaanthracene resulted in sarcomaJ at the site of 

injection 9 months following treatment. Injection of 5.0 mg produccd a sarcoma incidence of 34% 

with no tumors seen in controls (Steher and Edgecomb, 1952). 

A number of studies have shown ~&nthracene to have initiating activity and to act as a 

complcte carcinogen in skin painting assays in scvcral strains of mice (IARC 1973; US. EPA, 1991b). 

Levin et ai. (1984) tested the tumor-initiating activity of bc@danthraccne and a number of its 

metabolic products in a mouse skin painting assay. A single d- of 0.4 or 2.5 pmole of 

bcnzla)anthracene followed by 25 web of promotion with 12-O-tetrad~~photboc13-aatcrte 

resulted in skin tumor incidence of 7% for the controls, 14% for 0.4 pmole, and 36% for 23 pmole. 

4.4. EPA WEIGR"!!EEVXDENCE 

CLASSIFICATION Group B2 - Probable Human Carcinogen (US. EPA, 1991b). 

BASIS: Based on no human data and suf€icient data from animal expcrimCntt 

Bcx@&mthractne has becn shown to produce tumors in mice exposed by gavage; t w 

application: and intraperitoneal, subcutancoru or intramuscular injection (US. EPA 1991). 

CLASIFICATION Group B2 - Pmbable Human Caxknogcn (US EPA, 1991b). 

BASIS: Based on no human data and suflicient data from animal 

Be@&mthraccne has been shown to produce tumon in mice exposed by gavage tow 

apptication: and intraperitoneal, subcutaneous or intramuscular injection (US. EPA 1991). A 

related bay-region polycyclic aromatic hydrocarbon, bcnm~pyrenc, has been shown to cause 

respiratory tract tumors in goiden hamsten when given by inhalation exposure frhJlssea et al, 

1S1). 

12-

45. CARCINOGENIClTY SIDPE FACXORS 

45.1. Oral 

An oral slope factor has not been calculated specifically for benzwanthracene (Us. EPA, 1991). 

Benzolalwrcne: 

SLOPE FACTOR 

73 (rng/kg/day)'' (US. EPA, 1980,1984,1992a). 

DRINKING WATER UNIT RISR 21E-4 (pgAJ' (US. EPA, 1992a) 

VERZFICATION DATE: 071011p2 

PRINCIPALSTUDY: Neal and Rigdon (1967). 

TI& slop factor was calculated by the EP& (1W) from data ob- from 

experiments using bcnzo~pyrene and was based on the incidence of stomach tumors in mi= 

This slop factor was applied to protect humans from the d o g e ~ effects c of pome 

aromatic hydrocarborn as a chemical class. It is not currently available on IRIS for specific uc 

with be~anthraccne 

45.2 Inhslation 

mfaluvrcng 

SLOPE FACXIR 

INHALATION UNIT RISK: 

VERIFICATION D AE 

PRINaPALrnX 

- 

Not verified. 

laysten et aL (1981). 

(US EPA, 1992b) 

(US EPA 199%). 

mMMEN'I3 This slope factor was calculated by the EPA (1984) from data obtained from-. 

experiments using benoo~pyrae and was bascd on the incidence of rcsphtory tumors in 

golden hamsters. This slope factor was applied to protect humans from the carcinogenic effects 

of polycyclic aromatic hydrocarbons as a chemical class. It is not currently available on IRIS for 

specific use with bcnzla)anthraccnc 

13

5. REFERENCES 

Bock, F.G. 1964. Early effects of hydmxrbons on mammalian skin. 

4 126. 

.- 

Prop. Expo Tumor Rea. 

Bock, F.G.and D.W. King. 1959. A study of the sensitivity of the mouse forestomach toward certain 

polycyclic hydrocarbans. J. NatL Cancer IIUL 23: 833-839. 

Cawein, MJ. and K.L. Sydnor. 1968 Suppression of cellular activity in the reticuloendothclial 

system of the rat by 7,12dimethyi~anthracenc Cancer Res. 28: 320. 

Ford, E and C HuggiPs. 1963. selectivt destruction in testis indd by 7J2- 

dimcthyl~anthcenc. J.Exp.Med ll&27. 

Hoch-Ligcti, C 1941. Studies on the changes in the lymphoid tissues of mice treated with 

carcinogenic and non-cardnogenic hydracarbons Cancer Res 1: 484. 

Hueper, W.C. 1963. Chemically induced skin cancers in man. NatL Cancer Inst. Monograph. 10: 

371. 

IARC (International ABency for Reruucb on Cancer). 1973. Certain Potycyciic Aromatic 

Hydrocarbons and Heterocyclic Compounds. Monographs on the Evaluation of the carcinogenic 

Risk of Chemicak to Man. Polynuclear Aromatic Compounds. VoL 3. Lyon, France. 

Jerina, D.M., R khr, M. Schaefer-Riddet, H.Yagi,J.M. Karle, D.R. -* AW. WOOQ AYE 

Lu, D. Ryan, S. West. W. M n and AH. Coany. 1977. Bay-region e- of dihydrodiok: A 

concept explaining the mutagenic and carcinogenic activity of benzrowm aad 

benzoManthraceac in: Origins of Human Cancer. cdd Spring Harbor Laboratory. pp. 639-657. 

Katin, p., et at I=. Dstriiution, retention, and elimination of 14C-39~~ne.ak 

administtation to mice and rats. J. NatL b a r Inst 23: 541. 

Lajnitzki, A and DL Woodhousc 1944. The effect of 1,2,5,6d1~t&raccne on the lpph 

nodes of the rat. J. Anat. 78: 121. 

Levin, W., RL Chang, AW. WOOQ RYagi, D.R’hakkcr, D.M. Jerinaandk H.Conmy- lB4. 

High StercwcieCtiVity among the optical isomers of the diastueomeric bay-rcgion diotcpoaider of 

anthracene in the expression of tumorigenic activity in murine tumor model. Cancer Rer 

44: 929-933. 

.

Aattisoa, D.R. and S.S. Thorgeirssoa. 1977. Ovarian metabolism of polycyclic aromatic hydrocarbons 

and associated ototoxicity in the mouse. GyntcoL Invest. 8 11. -. 

Mitchell, CE and K. W. Tu 1979. Distribution, retention and elimination of pyrene in rats after 

inhalati01~ J. ToxicOL Emriron. Health. 5: 1171-1179. 

National Academy of Sciences. 1972 Biological effects of atmospheric pollutants: Particulate 

polycyclic organic matter. Washington,D.C 

Neal, J. and RH. Rigdon. 1967. Gastric tumors in mice fed bcnzo(dpyrene: A quantitative study. 

Tex Rep. BioL Med. 25: 553. 

Rees, EO., et aL 1971. A study of the mechanism of intestid absorption of 

Biochem. Biophys. Acta. 225: 96 

ReSchuller, H. and U. Mob. 1974. Investigations on the CarcinogCnic burden by air pollution 

in man. Ix Ear@ pathological alterations of the bronchial epithelium in Syrian goldcn hamsters after 

intratracheal instillation of bu~~~pyrene. Pl.BaLt. Hyg., L Abt. Ong. R 159: 493. 

Rigdon, FLH. and EG. RCM& 1964. EIftct of feeding -e on reproduction in the rat.- 

Eqcricnth a224-226. 

Robinson, J.R., J S Felton, RC Lcvitt, S S Thotgitrsson and D.W. Nebert 1975. Relationship 

W "aromatic hydrocarbon rcqxinsivcnd and thesurvival timer in mice trurtedwithvaxious 

drugs and eavkunmental compoun&. Mol PbannaeoL 11: 850.865. 

motti, U., et aL. 1968. A method for the experimental induction of bronchogenic Catcinoma. 

Cancer Rcs. 28: 104. 

Sax, N.I. 1981. Cancer Causing Chemicals. Van Nostrand Rci~ihold, Ncw York, p. 299. 

schlede, F: et al. 19706. Stimulatory effect of benzo[dpyrene and phcnobarbital pretreatment on 

the biliary cxuetion of benoo@Jpyrcne metabolites in the rat Canccr Res. 30: 2898. 

SChlcde, E, et al. 197oa EEEcct of enzyme induction on the metaboh and tissue distniutbn of 

bcnzo@Jpe CinarRer. 30:2893. 

sitti& M. 1985. Handbook of Toxic and Hazardous Chemicals and Carcinogens, Second Edition. 

Naye~ Publications, Park Rids New Jersey, pp.109-110. 

Stcincr, P.E and J.H. Edgecomb. 1952 cardnogenicity of 13-benzarrtbraoenc. Cancer Rca 125- 

657-659. 

Taysstn, F; J. Althoff, G. Kirnmde and U. Moht. 1981. Inhslation studies with Bcnm~pyrcuc 

in Syrian golderr hamster& J. Natl Caacer Inst bbc 575-577. 

15

US. EPA 1980. Water Quaiity Criteria Document for Polynuclear Aromatic Hydrocarbons. 

Prepared by the Office of Research and Development, Environmental Criteria And Assessment 

Office, Cincinnati,OH for the Office of Water Regulations and Standards, Washington, DC 

US. EPA 1984. Hcalth Effects Assessment for Polycyclic Aromatic Hyd-ns. Prepared by 

the Office of Htalth and Environmental Assessment, Environmental Criteria and Assessment Office, 

Cincinnati, OH for the OfEcc of Emergency and Remedial Response, Washington, DC 'EP.A./540/1- 

86-013. 

US. EfA 1991. Integrated Risk Information System (nus). Health Risk Assessment for 

BenzfaJanthracene. OnLine. Office of Hcaith and Environmental Assessment, Environmental Criteria 

and Asscsslaent 0- Cincinnati, OH. 

US. EPA 1- Integrated Risk Infonaation System @us). Health Risk Asstssment for 

&nmww~. OnLiae. Office of Health and Environmental Assessment, Environmental Criteria 

and Assessmcat Ofh, Cincianati OH. 

US. EPA 1992b. Hcalth EEects Assessment Summary Tables, Prepared by the Office of Health 

and Environmental Assessment, Environmental Criteria and Assessment Office,Cincinnati, OH for 

the Office of Emcrgcncy and Remedial Response, Washington,DC 

Vainio, H.,et aL 1976. The fate of intratracheaUy installed benzo[~pyrenc in the isolated petfrrred 

rat lung of both control and 20-methylcholanthrene pretreated rats. Res. canm. chem. PathoL 

PharmacoL 13: 259. 

Wmlocki, P.G., E.S. Bagan, AYX. tu, et aL 1986. TumorigeniCity of nitrated derivatives of p~mne, 

benz(~anchraCcne, chryJerrc and berrzro[dpe in the newborn mouse assay. Carcinogenuk 7: 

1317-1322. 

Yasuhira, K 1964. Damage to the thymus and other lymphoid tissues from 3-mcthylcholanthrcnc, 

and subsequent thymoma production, in mice. Cancer Res. 24 558. 

16

TOXICITY SUMMARY FOR 

BENZO[u]PYRENE 

December 1994 

Prepared by: 

Rosmarie A. Faust, Ph.D. 






Prepared for: 



*Managed by Martin Marietta Energy Systems, Inc., for the U.S. Department of Energy under 

Contract No. DE-AC05-MOR21400

THIS PAGE INTENTIONALLY LEFT BLANK

EXECUTIVE SUMMARY 

Benzo[a]pyrene is a polycyclic aromatic hydrocarbon (PAH) that can be derived from coal tar. 

Benzo[u]pyrene occurs ubiquitously in products of incomplete combustion of fossil fuels and has been 

identified in ambient air, surface water, drinking water, waste water, and char-broiled foods (IARC, 

1983). Benzo[a]pyrene is primarily released to the air and removed from the atmosphere by 

photochemical oxidation and dry deposition to land or water. Biodegradation is the most important 

transformation process in soil or sediment (ATSDR, 1990). 

Benzo[a]pyrene is readily absorbed following inhalation, oral, and dermal routes of administration 

(ATSDR, 1990). Following inhalation exposure, benzo[u]pyrene is rapidly distributed to several tissues 

in rats (Sun et al., 1982; Weyand and Bevan, 1986). The metabolism of benzo[o]pyrene is complex and 

includes the formation of a proposed ultimate carcinogen, benzo[a]pyrene 7,8 diol-9,lO-epoxide (IARC, 

1983). The major route of excretion is hepatobiliary followed by elimination in the feces (EPA, 1991). 

No data are available on the systemic (non-carcinogenic) effects of benzo[a]pyrene in humans. In 

mice, genetic differences appear to influence the toxicity of benzo[a]pyrene. Subchronic dietary 

administration of 120 mg/kg benzo[a]pyrene for up to 180 days resulted in decreased survival due to 

hematopoietic effects (bone MITOW depression) in a "nonresponsive" strain of mice (Le., a strain whose 

cytochrome P-450 mediated enzyme activity is not induced as a consequence of PAH exposure). No 

adverse effects were noted in "responsive" mice (i.e., a strain capable of inducing increased cytochrome 

P-450 mediated enzyme activity as a consequence of PAH exposure) (Robinson et al., 1975). 

Immunosuppression has been reported in mice administered daily intraperitoneal injections of 40 or 160 

mg/kg of benzo[u]pyrene for 2 weeks, with more pronounced effects apparent in "nonresponsive" mice 

(Blanton et al., 1986; White et al., 1985). In utero exposure to benzo[a]pyrene has produced adverse 

developmentaVreproductive effects in mice. Dietary administration of doses as low as 10 mg/kg during 

gestation caused reduced fertility and reproductive capacity in offspring (Mackenzie and Angevine, 1981), 

and treatment by gavage with 120 mg/kg/day during gestation caused stillbirths, resorptions, and 

malformations (Legraverend et al., 1984). Similar effects have been reported in intraperitoneal injection 

studies (ATSDR, 1990). Neither a reference dose (RfD) nor a reference concentration (RfC) has been 

derived for benzo[a]pyrene. 

Numerous epidemiologic studies have shown a clear association between exposure to various 

mixtures of PAHs containing benzo[a]pyrene (e.g., coke oven emissions, roofing tar emissions, and 

cigarette smoke) and increased risk of lung cancer and other tumors. However, each of the mixtures also 

contained other potentialIy carcinogenic PAHs; therefore, it is not possible to evaluate the contribution 

of benu>[u]pyrene to the carcinogenicity of these mixtures (IARC, 1983; EPA, 1991). An extensive data 

base is available for the carcinogenicity of benzo[u]pyrene in experimental animals. Dietary 

administration of benzo[a]pyrene has produced papillomas and carcinomas of the forestomach in mice 

(Neal and Rigdon, 1967), and treatment by gavage has produced mammary tumors in rats (McCormick 

et al., 1981) and pulmonary adenomas in mice (Wattenberg and Leong, 1970). Exposure by inhalation 

and intratracheal instillation has resulted in benign and malignant tumors of the respiratory and upper 

digestive tracts of hamsters (Ketkar et al., 1978; Thyssen et al., 1981). Numerous topical application 

studies have shown that benzo[a]pyrene induces skin tumors in several species, although mice appear to 

be the most sensitive species. Benzo[u]pyrene is a complete carcinogen and also an initiator of skin 

tumors (IARC, 1973; EPA, 1991). Benzo[u]pyrene has also been reported to induce tumors in animals 

when administered by other routes, such as intravenous, intraperitoneal, subcutaneous, intrapulmonary, 

and transplacental. 

iii

Based on United States Environmental Protection Agency (EPA) guidelines, benzo[a]pyrene was 

assigned to weight-of-evidence group B2, probable human carcinogen. For oral exposure, the slope 

factor and unit risk are 7.3E+O (mg/kg/day)-' and 2.1E-4 (pg/L)-', respectively (EPA, 1994). 

iv


Benzo[a]pyrene (CAS Reg. No. 50-32-8), also known as 1,4-benzo[u]pyrene (BaP), is a polycyclic 

aromatic hydrocarbon (PAH) with a chemical formula of C20H,2 and a molecular weight of 252.3. It 

exists as yellowish plates and needles, has a boiling point of 310-312°C at 10 mm Hg (Budavari et al., 

1989), a melting point of 178"C, and a density of 1.35 (EPA, 1991). Benzo[u]pyrene is practically 

insoluble in water but is soluble in benzene, toluene, xylene and sparingly soluble in alcohol and methanol 

(Budavari et ai., 1989). It has a vapor pressure of 5.0 x 1-' torr and a log octanol/water coefficient of 

6.04 (EPA, 1991). 

No current commercial production or use of benzo[a]pyrene is known. It occurs ubiquitously in 

products of incomplete combustion and in fossil fuels. It has been identified in surface water, tap water, 

rain water, groundwater, waste water, and sewage sludge (EPA, 1991). Benzo[u]pyrene is primarily 

released to the air and removed from the atmosphere by photochemical oxidation and dry deposition to 

land or water. Biodegradation is the primary transfonnation process in soil or sediment (ATSDR, 1990). 

The estimated half-lives for benzo[a]pyrene are less than 1-6 days in the atmosphere, less than 1-8 hours 

in water;5-10 years in sediment, and greater than 14-16 months in soil (for complete degradation) (EPA, 

1984). Benzo[u]pyrene is one of a number of PAHs on EPA's priority pollutant list (ATSDR, 1990). 

2. METABOLISM AND DISPOSITION 

2.1 ABSORPTION 

Benzo[u]pyrene is readily absorbed by the oral, inhalation, and dermal routes of exposure (ATSDR, 

1990). Rats given benzo[u]pyrene in starch solution by gavage (100 mg) or in the diet (250 mg) absorbed 

40% or 60%. respectivefy, of the administered compound (Chang, 1943). The absorption of 

benzo[a]pyrene from the gastrointestinal tract of mice and cats is enhanced when it is solubilized in 

vehicles possessing both lipophilic and hydrophilic properties (Ekwalf et al., 1951). Once benzo[a]pyrene 

has entered the small intestine, it is solubilized by bile salts and absorbed (Ermala et al., 1951). 

In rats exposed by inhalation to 1 pg/L radiolabeled benzo[u]pyrene for 30 minutes, monitoring of 

excretion over a 2-week period showed nearly complete recovery of radioactivity (predominantly in 

feces), indicating nearly complete absorption (Sun et al., 1982). 

Under in vitro conditions, 3% of an applied dose of benzo[u]pyrene permeated human skin after 

24 hours. When tested in several animal species, the permeation was highest in the mouse (10%) and 

lowest in the guinea pig (0.1%) (Kao et al., 1985). Following topical application of radiolabeled 

benzo[u]pyrene to the skin of mice, Heidelberger and Weiss (1951) recovered most of the radioactivity 

in the feces within 16 days, indicating significant absorption of benzo[u]pyrene through the skin. 

2.2 DISTRIBUTION 

According to Rees et al. (1971), 10-20% of an intragastric dose of benzo[u]pyrene (10 mg) entered 

the thoracic lymph duct in rats (levels in other tissues were not determined). Other data concerning the 

tissue distribution of benzo[u]pyrene following oral exposure were not available.

2 

In rats exposed by inhalation, distribution of absorbed benzo[u]pyrene is rapid, with highest levels 

found in the liver, esophagus, small intestine, and blood 30 minutes after exposure (Sun et al., 1982). 

Five minutes after intratracheal instillation of benzo[u]pyrene to rats, the percentages of the administered 

dose in tissues were lungs (59.5%), carcass (14.4%), liver (12.5%), blood (3.9%), and intestines (1.9%). 

At 60 minutes, the percentages were lungs (15.4%), carcass (27.1%). liver (15.8%), blood (1.6%), and 

intestines (9.9%) (Weyand and Bevan, 1986). 

Topical administration of ''C-benzo[u]pyrene in benzene to the shaved backs of mice was followed 

by a biphasic disappearance of radioactivity from the application site, with half-lives of 40 and 104 hours 

(Heidelberger and Weiss, 1951). 

Benzo[u]pyrene can readily cross the placenta following oral, intravenous, or subcutaneous 

.. 

-ion. 

This observation is consistent with the observed toxicity in the fetuses and offspring of 

maternally exposed rodents (IARC, 1983; ATSDR, 1990). 

2.3. METABOLISM 

The metabolism of benzo[u]pyrene has been extensively studied in the literature and only the most 

important pathways will be presented in this summary. As outlined in L4RC (1983), benzo[u]pyrene is 

metabolized initially by the microsomal cytochrome P-450 monooxygenase system to several arene 

oxides, which may rearrange spontaneously to phenols, undergo hydration to the corresponding transdihydrodiols, 

or react covalently with glutathione, either spontaneously or in a reaction catalyzed by 

glutathione-S-transferases. One of the phenolic metabolites, 6-hydroxybenzo[u]pyrene, is further oxidized 

to the 1,6-, 3,6-, or 6,12-quinones. The phenols, quinones, and dihydrodiols can be detoxified by 

conjugation to glucuronides and sulfate esters, and the quinones can also form glutathione conjugates. 

In addition to conjugation, the dihydrodiols undergo further oxidative metabolism. Benzo[u]pyrene 

7.8dihydrodiol is in part oxidized to 7,8diol-9,10-epoxide, a compound considered to be the ultimate 

carcinogenic metabolite of benzo[u]pyrene. 

2.4 EXCRETION 

Hepatobiliary excretion and elimination in the feces is the primary route for benu>[u]pyrene 

metabolic excretions (EPA, 1991). Two weeks following inhalation exposure to radiolabeled 

benzo[u]pyrene for 30 minutes, most of the radioactivity was recovered in the feces of rats (Sun et al., 

1982). Similarly, essentially all of the radioactivity was recovered in the feces of mice that had been 

treated topically with radiolabeled benzo[u]pyrene (Heidelberger and Weiss, 1951). Kotin et al. (1959) 

reported that approximately 75% of a subcutaneously injected dose of benzo[u]pyrene was recovered in 

the feces of mice within 6 days of injection, while only 12% was eliminated in the urine. In rats, 39% 

of an intravenous dose was found in the bile at 3 hours and as much as 96% by 14 hours. Less than 1 % 

of recovered benzo[u]pyrene in the bile was metabolized. In rats with bile duct cannulation, 3-41 of 

the dose was recovered in the urine, while intact rats had a urinary excretion of 7-14%, suggesting 

enterohepatic circulation of metabolites. No evidence suggested that benzo[u]pyrene is eliminated via 

expired air.

3 

3. NONCARCINOGENIC HEALTH EFFECTS 

3.1 ORALEXPOSURES 

3.1.1 Acute Toxicity 

Information on the acute oral toxicity of benzo[u]pyrene in humans or animals is not available. 

3.1.2 Subchronic Toxicity 

3.1.2.1 Human 

Information on the subchronic oral toxicity of benzo[u]pyrene in humans is not available. 


Genetic differences appear to influence the oral toxicity of benzo[u]pyrene in mice. Robinson et 

al. (1975) investigated the effects of oral administration of benzo[u]pyrene in several strains of mice, 

classified as "responsive" (those capable of producing increased levels of cytochrome P-450 mediated 

enzymes as a consequence of PAH exposure) or "nonresponsive" (those not highly responsive to 

producing increased levels of cytochrome P-450 mediated enzymes as a consequence of PAH exposure). 

Following dietary administration of 120 mg/kg of benzo[u]pyrene for up to 180 days, survival of all 

"nonresponsive" mice was shortened. Death appeared to be due to bone marrow depression (aplastic 

anemia, pancytopenia). The "responsive" mice remained healthy for at least 6 months. The authors 

concluded that decreased survival in "nonresponsive" mice was associated with a single gene difference 

in PAH responsiveness. 

3.1.3 Chronic Toxicity 

Information on the chronic oral toxicity of benzo[u]pyrene in humans or animals was not available. 

3.1.4 Developmental and Reproductive Toxicity 

3.1.4.1 Human 

Information on the developmental and reproductive toxicity of benzo[u]pyrene in humans following 

oral exposure is not available. 

3.1.4.2 Animal 

No reproductive or developmental toxicity was observed in male or female White Swiss mice fed 

diets containing 0, 250, 500, or lo00 mgkg benzo[u]pyrene over various time periods during mating, 

gestation, and lactation (Rigdon and Neal, 1965). However, Mackenzie and Angevine (1981) reported 

that administration of 10 mg/kg to CD-1 mice by gavage during gestation produced decreased gonadal 

weights and reduced fertility and reproductive capacity in the offspring. Higher doses (40 mg/kg) caused 

almost complete sterility in both sexes of offspring. 

Legraverend et al. (1984) investigated the effect of genetic differences in benzo[u]pyrene metabolism 

on the reproductive or developmental toxicity in "responsive" and "nanresponsive" mice (benzo[u]pyrene

4 

metabolism occurs more readily in the "responsive" genotypes). Pregnant mice were fed 120 mg/kg/day 

on days 2-10 of gestation. Treatment with benzo[u]pyrene resulted in stillbirths, resorptions, and 

malformations in both genotypes of mice; however, the incidence of these effects was higher among 

"nonresponsive" embryos than among "responsive" embryos. The study suggests that it is benzo[a]pyrene 

and not a metabolite which is responsible for the noted adverse effects. 

3.1.5 Reference Dose 

An oral reference dose (RfD) for benzo[u]pyrene has not been derived. 

3.2 INHALATION EXPOSURES 


Information on the acute toxicity of benzo[u]pyrene in humans or animals following inhalation 

exposure is not available. 


Information on the subchronic toxicity of benzo[u]pyrene in humans or animals following inhalation 



Information on the chronic toxicity of benzo[u]pyrene in humans or animals following inhalation 



Information on the developmental and reproductive toxicity of benzo[u]pyrene in humans or animals 

following inhalation exposure is not available. 

3.2.5 Reference Concentration 

An inhalation reference concentration (RfC) for benzo[u]pyrene has not been derived. 

3.3 OTHER ROUTES OF EXPOSURE 


3.3.1.1 Human 

Information on the acute toxicity of benzo[u]pyrene in humans by other routes of exposure was not 

available. 

3.3.1.2 Animal

5 

The intraperitoneal (i.p.) LDSo for the mouse is 232 mg/kg (Salamone, 1981), and the subcutaneous 

(s.c.) LDSo for the rat is 50 mgkg (RTECS, 1994). Reduced survival was reported in "responsive" mice 

administered a single i.p. injection of 500 mg/kg benzo[u]pyrene (Robinson et al., 1975). Subcutaneous 

injections of benzo[u]pyrene (5, 20, or 40 mg/kg) caused a dose-related suppression of both T-cell 

independent and T-cell dependent antigens in mice (White and Holsapple, 1984). Wojdani et al. (1984) 

injected two strains of mice with tumor target cells; this treatment was followed by i.p. injections of 0, 

0.5, 5, or 50 mgkg of benzo[u]pyrene. At the two higher doses, significant decreases were reported in 

lymphocytes binding to target cells or killing target cells. The investigators indicated that lymphocytemediated 

immunity may be inhibited by benzo[u]pyrene and that this immunosuppresive effect may 

contribute to its carcinogenicity. 


3.3.2.1 Human 

Information on the subchronic toxicity of benzo[u]pyrene by other routes of exposure in humans 

is not available. 


Immunotoxic effects as a consequence of benzo[u]pyrene have been studied by a number of 

investigators. For example, a 60% suppression of antibody response was reported in B6C3Fl mice (a 

highly "responsive" strain) administered 14 daily S.C. injections of 160 pmol/kg benzo[u]pyrene. In 

DBN2 mice (a strain not highly "responsive") subjected to the same dosing protocol, immunosuppression 

was more pronounced (White et al., 1985). Daily S.C. injections of 40 mg/kg benzo[u]pyrene for 14 days 

resulted in a 98% depression of the T-celldependent antibody response in B6C3Fl mice. Polyclonal 

antibody responses were reduced 50 to 66% following benzo[u]pyrene (Blanton et al., 1986). 


Information on the chronic toxicity of benzo[u]pyrene by other routes of exposure in humans or 

animals is not available. 



Information on the developmental or reproductive toxicity of benzo[u]pyrene by other routes of 

exposure in humans was not available. 


Adverse developmental/reproductive effects were observed in several injection studies with 

benzo[u]pyrene. These studies are reviewed in an ATSDR report (1990). but experimental details were 

not provided. Intraperitoneal administration of benzo[u]pyrene to mice has resulted in stillbirths, 

resorptions, and malformations; decreases in follicular growth and corpora lutea; and testicular changes. 

Subcutaneous injections of benzo[u]pyrene produced increased resorptions in rats and direct embryonal 

injection led to decreased fetal survival in mice.

3.4 TARGET ORGANS/CRITICAL EFFECTS 

3.4.1 Oral Exposures 

3.4.1.1 Primary target organs 

6 

1. Hematopoietic system: Subchronic oral exposure produced bone marrow depression 

(aplastic anemia and pancytopenia) and ultimately death in "nonresponsive" mice. 

2. Reproductioddeveloprnent : Exposure during gestation of mice produced decreased 

gonadal weights, reduced fertility, and sterility in offspring. Stillbirths, resorptions, and 

malformations were seen in "responsive" and "nonresponsive" mice; however, the 

incidence of these effects was higher in "nonresponsive" mice. 

3.4.1.2 Other target organs 

Other target organs for oral exposure have not been identified. 

3.4.2 Inhalation Exposures 

Target organs for inhalation exposure to benzo[u]pyrene have not been identified. 

3.4.3 Other Routes of Exposure 

3.4.3.1 Primary target Organs 

1. Immune system: Subcutaneous injections of benzo[a]pyrene administered over a 2-week period 

caused depressed antibody responses in mice. 

2. Reproductioddevelopment : Intraperitoneal injections of benzo[a]pyrene have resulted in 

stillbirths, resorptions, malformations, decreased follicular growth and corpora lutes, and 

testicular changes in mice. Subcutaneous injections produced increased resorptions in rats. 

3.4.3.2 Other target organs 

Other target organs for other routes of exposure have not been identified. 

4. CARCINOGENICITY 

4.1 ORALEXPOSURES 

4.1.1 Human 

Information on the carcinogenicity of benzo[u]pyrene in humans following oral exposure is not 

available.

7 

4.1.2 Animal 

In a study by Brune et al. (1981), male and female Sprague-Dawley rats were fed 0.15 mg/kg every 

9th day or 5 timedweek for life. The incidence of tumors of the forestomach, esophagus, and larynx 

(combined) was 5% for controls and for rats fed benzo[u]pyrene every 9th day and 16% for rats fed 

benzo[u]pyrene 5 times/week. Administration of a single 50-mg dose of benzo[u]pyrene or of 8 weekly 

doses of 6.25 mg by gavage induced mammary tumors in LEWMai rats (McCormick et al., 1981). The 

incidence of mammary carcinomas after 90 weeks was 77% for the single exposure and 67% for the 

multiple exposures. Mammary tumors were observed in 30% of controls. Huggins and Yang (1962) 

reported that a single oral dose of 100 mg benzo[u]pyrene administered by gavage induced mammary 

tumors in 8/9 female Sprague-Dawley rats. 

Neal and Rigdon (1967) fed male and female CFW-Swiss mice a diet containing 1 to 250 ppm 

benzo[u]pyrene for up to 197 days. No tumors were found in the control group and in groups treated 

with 1, 10, or 30 ppm. However, forestomach papillomas and carcinomas developed at dietary 

concentrations of greater than or equal to 40 ppm. The authors indicated that the tumor incidence was 

related to both the concentration and the number of doses administered. Female mice administered 200 

or 300 ppm benzo[u]pyrene in the diet for a relatively short time (12 weeks) developed tumors of the 

forestomach (Triolo et al., 1977). Pulmonary adenomas developed in A/HeJ mice treated by gavage with 

two daily doses of 3 mg benzo[u]pyrene at 2-week intervals (Wattenberg and Leong, 1970). The 

pulmonary tumor count increased from 0.3 tumordmouse in controls to 16.6 tumors/mouse in the treated 

group at 30 weeks of age. 

4.2 INHALATION EXPOSURES 


Numerous epidemiologic studies have shown a clear association between inhalation exposure to 

various mixtures containing PAHs (e.g., coke oven emissions, roofing tar emissions, and cigarette smoke) 

and increased risk of lung cancer and other cancers. Each of these mixtures contained benzo[u]pyrene 

as well as other carcinogenic PAHs and other potentially carcinogenic chemicals; therefore, it is not 

possible to evaluate the contribution of benzo[u]pyrene to the carcinogenicity of these mixtures (IARC, 

1983; EPA, 1991). 


Thyssen et al. (1981) exposed Syrian hamsters to benzo[u]pyrene at concentrations of 0, 2.2, 9.5, 

or 46.5 mg/m3, 4.5 hours/day for 10 days and then 3 hours/day for up to 675 days. No treatment-related 

tumors were observed in hamsters exposed to 2.2 mg/m3 or in controls. Hamsters exposed to 9.5 mg/d 

developed papillomas and squamous cell carcinomas located primarily in the nasal cavity, larynx, trachea, 

and pharynx. In addition to respiratory tract tumors, hamsters exposed to the highest concentration also 

developed tumors of the upper digestive tract. 

Intratracheal administration of benzo[u]pyrene also induced neoplasms of the respiratory tract in 

male and female Syrian hamsters. Weekly intratracheal administration of benzo[u]pyrene (total doses 

18.2 or 36.4 mg/animal) for 52 weeks produced a doserelated increase of tracheal papillomadcarcinomas 

and lung adenomas. Similar effects were reported following weekly intratracheal administration of doses 

ranging from 0.1 to 1 mg up to 40 weeks, but the response was not clearly dose-related (Ketkar et al., 

1978).

8 

4.3 OTHER ROUTES OF EXPOSURE 


Human tumorigenicity has been reported in a number of studies as a result of dermal exposure to 

complex mixtures of PAHs containing benzo[a]pyrene. An early report (Pott, 1775) described scrotal 

cancer in chimney sweeps. More recently, skin cancer has occurred in workers exposed to shale oil 

(Purde and Etlin, 1980) and creosote (Lenson, 1956). However, the contribution of benzo[u]pyrene to 

the carcinogenicity of these PAH mixtures is uncertain. 

In an experimental study, epidermal changes (erythema, pigmentation, and desquamation) were 

reported following daily applications of a 1 % solution of benzo[a]pyrene to the skin of humans over a 

4-month period. Although reversible and benign, these changes were thought to represent early stages 

of neoplastic proliferation (Cottini and Mazzone, 1939). It should be noted that benzo[a]pyrene was 

applied as a solution in benzene, and no benzene control was evaluated. Similar epithelial changes were 

reported in humans accidentally exposed to benzo[u]pyrene (EPA, 1984). 


Benzo[a]pyrene is among the most potent and best documented skin carcinogens and is commonly 

used as a positive control in skin application assays of other chemicals. Benzo[a]pyrene has been shown 

to cause skin tumors in mice, rats, rabbits, and guinea pigs, although mice appear to be the most sensitive 

species. It is both an initiator and complete carcinogen in mouse skin (IARC, 1973; EPA, 1991). 

Wynder and Hoffmann (1959) applied 0.001, 0.005, or 0.01% benzo[a]pyrene in acetone to the 

backs of female Swiss mice three times weekly for life. For the three dose groups, the incidence of skin 

papillomas was 95, 100, or 85%. respectively, and the incidence of skin carcinomas was 4, 86, or 95%. 

respectively. Data for a solvent control group were not provided. In initiatiordpromotion experiments, 

Hoffmann and Wynder (1966) applied 10 doses of benzo[u]pyrene in dioxane (total dose 0.25 mg) every 

2 days to the skin of mice. This treatment was followed by application of 2.5% croton oil in acetone. 

Skin papillomas developed in 80% of treated animals and% 7% of controls (receiving croton oil alone). 

The modifying effects of solvents on the carcinogenicity of benzo[a]pyrene have been demonstrated 

in several studies. For example, Bingham and Falk (1969) treated C3H/He mice topically with different 

concentrations of benzo[alpyrene in either ndodecane or a ndodecaneldecalin mixture three times weekly 

for 50 weeks. When ndodecaneldecalin was used as a solvent, malignant skin tumors appeared in 5/24 

mice treated with 0.00002% benzo[u]pyrene, and the tumor incidence increased at higher concentrations. 

With decalin alone as a solvent, malignant skin tumors developed in 5/12 mice treated with 0.02%, but 

none were seen at lower concentrations. Other topical application studies with mice demonstrated 

synergistic effects of cigarette smoke condensates on skin tumor induction (IARC, 1973). 

Benzo[u]pyrene has been shown to produce tumors at various sites by other modes of 

administration. A 94% incidence of lung adenomas was reported in newborn mice injected i.p. with 280 

pg/mouse of benzo[a]pyrene (Busby et al., 1984). Newborn rats treated with a single i.p. injection of 

0.59 -01 benzo[u)pyrene/kg and observed for life developed hepatic tumors. The tumor incidence was 

37% for males and 57% for females (Peraino et al., 1984). Several studies reported injection site tumors 

in mice, rats, guinea pigs, hamsters, and some primates administered S.C. injections of benzo[a]pyrene 

@PA, 1994). In addition to injection site sarcomas, newborn mice administered benzo[u]pyrene by S.C. 

injection developed hepatomas or lung adenomas (EPA, 1991; IARC, 1973). Benzo[u]pyrene has also

9 

been reported to induce tumors when administered by the intravenous and transplacental route; by 

implantation in the stomach wall, renal parenchyma, and brain; by injection in the renal pelvis; and by 

vaginal painting ( EPA, 1994). 

4.4 EPA WEIGHT-OF-EVIDENCE 

Classification: B2, probable human carcinogen (EPA, 1994). 

Basis: Human data specifically linking benzo[a]pyrene to a carcinogenic effect are lacking, 

However, multiple animal studies in many species demonstrating benzo[a]pyrene to be 

carcinogenic by numerous routes exist (EPA, 1994). 

Note: The carcinogenicity risk assessment for benzo[a]pyrene may change in the future 

pending further review by EPA. 

4.5 CARCINOGENICITY SLOPE FACTORS 

4.5.1 Oral 

SLOPE FACTOR: 7.3E+O (mg/kg/day)-' (EPA, 1994) 

UNIT RISK: 2.1E4 (pg/L)-' 

PRINCIPAL STUDIES: Brune et al., 1981; Neal and Rigdon, 1967; 

Rabstein et al., 1973 (historical control data) 

COMMENT: The slope factor, the geometric mean of four calculated slope factors [range 

4.5E+O to 11.7E+O (mg/kg/day)-'I, was derived using multiple data sets from different studies 

employing more than one sex, strain, and species. EPA considered the data less than optimal but 

acceptable. 

4.5.2 Inhalation 

An inhalation slope factor has not been calculated. 

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24

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25

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26

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. 

27

11 

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12 

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polycyclic hydrocarbons. Cancer 12: 1079-1086.


BENZO[b]FLUORANTHENE 

May 1994 

Prepared by 







Prepared for 



*Managed by Martin Marietta Energy System, Inc., for the US. Department of Energy under 

Contract No. DE-AC05-840R21400



Benzo[b]fluoranthene, a crystalline solid with a chemical formula of C&H,* and a molecular weight 

of 252.32 (Lide, 1991), is a polycyclic aromatic hydrocarbon (PAH) with one five-membered ring and 

four six-membered rings. There is no commercial production or known use of this compound 

(IARC, 1983). Benzo[b]fluoranthene is found in fossil fuels and occurs ubiquitously in products of 

incomplete combustion. It has been detected in mainstream cigarette smoke; urban air; gasoline engine 

exhaust; emissions from burning coal and from oil-fired heating; broiled and smoked food; oils and 

margarine (IARC, 1983); and in soils, groundwater, and surface waters at hazardous waste sites 

(ATSDR, 1990). 

No absorption data were available for benzo[b]fluoranthene; however, by analogy to structurallyrelated 

PAHs, primarily benzo[u]pyrene, it would be expected to be absorbed from the gastrointestinal 

tract, lungs, and skin (EPA, 1991). Major metabolites of benzo[b]fluoranthene formed in vitro in rat 

liver include dihydrodiols and monohydroxy derivatives (Amin et al., 1982) and monohydroxy derivatives 

in mouse epidermis (Geddie et al., 1987). 

No' data were found concerning the acute, subchronic, chronic, developmental, or reproductive 

toxicity of benzo[b]fluoranthene. No data were available for the derivation of an oral reference dose 

(RfJ3) or inhalation reference concentration (RfC) (EPA, 1994). 

No long-term oral or inhalation bioassays were available to assess the carcinogenicity of 

benzo[b]fluoranthene. Benzo[b]fluoranthene was tested for carcinogenicity in dermal application, lung 

implantation, subcutaneous (s.c.) injection, and intraperitoneal (i.p.) injection studies. Dermal 

applications of 0.01-0.5% solutions of benzo[b]fluoranthene for life produced a high incidence of skin 

papillomas and carcinomas in mice (Wynder and Hoffmann, 1959). In initiation-promotion assays, the 

compound was active as an initiator of skin carcinogenesis in mice (LaVoie et al., 1982; Amin 

et al., 1985). Sarcomas and carcinomas of the lungs and thorax were seen in rats receiving single lung 

implants of 0.1-1 mg benzo[b]fluoranthene (Deutsch-Wenzel et al., 1983). Newborn mice receiving 

0.5 pmol bem[b]fluoranthene via i.p. injection developed liver and lung tumors (LaVoie et al., 1987). 

and mice administered three S.C. injections of 0.6 mg benzo[b]fluoranthene developed injection site 

sarcomas (IARC, 1993). 

Based on no human data and sufficient evidence for Carcinogenicity in animals, EPA has assigned 

a weight-of-evidence classification of B2, probable human carcinogen, to benzo[b]fluoranthene 

(EPA, 1994). 

iii



Benzo[b]fluoranthene (CAS Reg. No. 205-99-2), also known as benz(e)acephenanthrylene, 

3,4-benz(e)acephenanthrylene, 2,3-benzofluoranthene, 3,4-benzofluoranthene, and benzo(e)fluoranthene 

(IARC, 1983) is a polycyclic aromatic hydrocarbon (PAH) with one five-membered ring and four sixmembered 

rings. It is a crystalline solid with a chemical formula of t&H12, a molecular weight of 

252.32, and a melting point of 168°C (Lide, 1991). Benzo[b]fluoranthene is virtually insoluble in water 

and is slightly soluble in benzene and acetone (IARC, 1983). It has a vapor pressure of lo-'' to 106 torr 

at 20"C, an octanol/water partition coefficient of 1.1x106, and a Henry's Law constant of 1.22~10 

(ATSDR, 1990). There is no commercial production or known use of this compound (IARC, 1983). 

Benzo[b]fluoranthene is found in fossil fuels and occurs ubiquitously in products of incomplete 

combustion. It has been detected in mainstream cigarette smoke; urban air; gasoline engine exhaust; 

emissions from burning coal and from oil-fired heating; broiled and smoked food; oils and margarine 

(IARC, 1973); and in soils, groundwater, and surface waters at hazardous waste sites (ATSDR, 1990). 

Benzo[b]fluoranthene is one of a number of PAHs on the United States Environmental Protection 

Agency's (EPA's) priority pollutant list (ATSDR, 1990). 



Data regarding the gastrointestinal or pulmonary absorption of benzo[b]fluoranthene in humans or 

animals were not available. However, data from structurally-related PAHs, primarily benzo[a]pyrene, 

suggest that benzo[b]fluoranthene would be absorbed from the gastrointestinal tract, lungs, and skin 

(EPA, 1991). 


No human or animal data were available concerning the tissue distribution of benzo[b]fluoranthene. 

2.3 METABOLISM 

Amin et al. (1982) investigated the in vitro metabolism of benzo[b]fluoranthene by rat liver 

microsomes and identified 5- and 6-hydroxybenzo[b]fluoranthene and 4- or 

7-hydroxybem[b]fluoranthene as major metabolites. The principal dihydrodiol metabolite formed was 

trm-1 1,12dihydro-l1,12dihydroxybenzo[b]fluoranthene. Geddie et al. (1987) investigated the 

metabolism of benzo[b]fluoranthene in mouse epidermis. Following dermal application of 

benzo[b]fluoranthene, 4-, 5-, and 6-hydroxybenzo[b]fluoranthene were identified as major metabolites. 

Sulfate and glucuronide conjugates of these hydroxy compounds were also detected. 

1

2 

2.4 EXCRETION 

No human or animal data were available concerning the excretion of benzo[b]fluoranthene. 



Information on the acute, subchronic, chronic, developmental, or reproductive oral toxicity of 

benzo[b]fluoranthene in humans or animals was not available. Because of a lack of toxicity data, an oral 

reference dose (RfD) for benzo[b]fluoranthene has not been derived (EPA, 1994). 


Information on the acute, subchronic, chronic, developmental, or reproductive toxicity of 

benzo[b]fluoranthene in humans or animals following inhalation exposure was not available. Because of 

a lack of toxicity data, an inhalation reference concentration (RfC) for benzo[b]fluoranthene has not been 

derived (EPA, 1994). 



benzo[b]fluoranthene in humans or animals by other routes of exposure was not available. 


No data were available to determine target organs/critical effects for oral, inhalation, or other routes 

of exposure to benzo[b]fluoranthene. 



Information on the carcinogenicity of benzo[b]fluoranthene in humans or animals following oral 

exposure was not available.

3 



Although there are no human data that specifically link exposure to benzo[b]fluoranthene to human 

cancers, benzo[b]fluoranthene is a component of mixtures that have been associated with human cancer. 

These mixtures include coal tar, soots, coke oven emissions, and cigarette smoke (EPA, 1994). 


Information on the carcinogenicity of benzo[b]fluoranthene in animals following inhalation exposure 

was not available. 



Infodon on the carcinogenicity of benzo[b]fluoranthene in humans by other routes of exposure 



Benzo[b]fluoranthene was tested for carcinogenicity in dermal application, lung implantation, 

subcutaneous (s.c.) injection, and intraperitoneal (i.p.) injection bioassays. 

Wynder and Hoffmann (1959) applied 0.01, 0.1, or 0.5% solutions of benzo[b]fluoranthene in 

acetone three times weekly to the skin of three groups of 20 Swiss mice for life; there were no untreated 

or vehicle controls. The highest dose produced skin papillomas in 100% and carcinomas in 90% of 

treated mice within 8 months; the intermediate dose produced papillomas in 65% and carcinomas in 85% 

of treated mice within 12 months. Of 10 surviving mice that received the lowest dose, only one animal 

developed a papilloma after 14 months. 

A single dermal application of 1 mg benzo[b]fluoranthene in acetone produced no tumors in 20 

Swiss mice during a 63-week observation period (Van Duuren et al., 1966). However, the same protocol 

followed by repeated applications of croton resin produced papillomas in 18/20 and carcinomas in 5/20 

treated mice. 

LaVoie et al. (1982) evaluated the tumor-initiating activity of benzo[b]fluoranthene by applying 

initiation doses of 0, 10, 30, or 100 pg benzo[b]fluoranthene in acetone (10 doses, every other day) to 

the skin of Cr1:CD-1 mice (20/group). This procedure was followed by treatment with 12-0- 

tetradecanoyl-phorbol-13-acetate (TPA), 3 times weekly for 20 weeks. There was a dose-related 

increased incidence of skin tumors, predominantly squamous cell papillomas. Skin tumors were seen in 

0, 45, 60, and 80% of mice treated with 0, 10, 30, or 100 pg bem[b]fluoranthene, respectively. A 

similar initiatiodprotowl by Amin et al. (1985) resulted in a comparable increased incidence of skin 

tumors in female Swiss albino mice.

4 

Sixteen male and 14 female XW nc/Z mice were given three S.C. injections of 0.6 mg 

benzo[b]fluoranthene in olive oil over a period of 2 months (IARC, 1973). Injection site sarcomas 

developed in 18/24 surviving mice, with an average latent period of 4.5 months. 

Female Osborne-Mendel rats (35/group) received single lung implants of 0.1, 0.3, or 1 mg 

benzo[b]fluoranthene in a mixture of beeswax and trioctanoin (Deutsch-Wemi et al., 1983). An 

untreated group and a group receiving the vehicle served as controls. Granulomatous inflammatory 

lesions developed at the injection sites. After a lifetime of observation, there was a dose-related increased 

incidence of epidermoid carcinomas and pleomorphic sarcomas in the lung and thorax (combined). The 

observed incidences were 1/35, 3/35, and 13/35, respectively, in the low-, mid-, and highdose groups. 

No lung tumors were reported in untreated and vehicle controls. In contrast, multiple intratracheal 

instillations of benzo[b]fluoranthene, administered as 30 weekly doses of 0.05 or 0.5 mg, did not induce 

a significant number of respiratory tract tumors in male Syrian golden hamsters (Sellakumar and Shubik, 

1974). The group receiving the higher dose had one papilloma of the trachea at week 99. 

LaVoie et al. (1987) administered i.p. injections of benzo[b]fluoranthene in dimethyl sulfoxide to 

newborn CD-1 mice (15 males and 17 females) on days 1, 8, and 15 of age at a total dose of 

0.5 pmol/mouse. The animals were sacrificed at 52 weeks of age. Treatment with benzo[b]fluoranthene 

induced hepatic tumors (adenomas and hepatomas combined) in eight male mice. One hepatoma 

developed in 1/17 male controls; no hepatic tumors were seen in female treated mice or in female 

controls. Lung adenomas were found in two male and in three female mice; no lung tumors occurred 

in controls. 

4.4 EPA WEIGHT OF EVIDENCE 

Classification-B2; probable human carcinogen (EPA, 1994) 

Basis-Based on no human data and sufficient data from animal bioassays. 

Benzo[b]fluoranthene produced tumors in mice after lung implantation, i.p. or S.C. injection, or skin 

painting. 


No carcinogenicity slope factors were calculated. 

5.- REFERENCES 

Amin, S., E.J. LaVoie, and S.S. Hecht. 1982. "Identification of metabolites of benzo[b]fluoranthene." 

Carcinogenesis 3: 171-174. 

Amin, S., K. Huie, and S.S. Hecht. 1985. "Mutagenicity and tumor initiating activity of methylated 

benzo[b]fluoranthene. " Carcinogenesis 6: 1023-1025.

5 

ATSDR (Agency for Toxic Substances and Disease Registry). 1990. Toxicological Profile for Polycyclic 

Aromatic Hydrocarbons. Acenaphthene, Acenaphthylene, Anthracene, Benzo(a)anthracene, 

Benzo (a)pyrene, Benzo(h)jluoranthene, Benzo (g, i, h)perylene, Benzo (k)jluoranthene, Chrysene, 

Dibmo (a, h)anthracene, Fluoranthene, Fluorene, Zndeno (1,2,3-c, d)pyrene, Phenanthrene, Pyrene. 

Prepared by Clement International Corporation, under Contract No. 205-88-0608. ATSDWTP-90- 

20. 

Deutsch-Wenzel, R.P., H. Brune, G. Grimmer, et al. 1983. "Experimental studies in rat lungs on the 

carcinogenicity and dose-response relationships of eight frequently occurring environmental 

polycyclic aromatic hydrocarbons. J. Natl. Cancer Znst. 71 : 539-544. 

Geddie, J.E., S. Amin, K. Hui, et al. 1987. "Formation and tumorigenicity of benzo[b]fluoranthene 

metabolites in mouse epidermis. I' Carcinogenesis 8: 1579-1584. 

IARC (International Agency for Research on Cancer). 1973. "Benzo[b]fluoranthene." In: LARC 

Monographs on the Evaluation of Carcinogenic Risk of Chemicals to Man. Certain Polycyclic 

Aromatic Hydrocarbons and Heterocyclic Compounds, Vol3. Lyon, France, pp. 69-81. 

IARC (International Agency for Research on Cancer). 1983. "Benzo[b]fluoranthene." In: LQRC 

Monographs on the Evaluation of Carcinogenic Risk of Chemicals to Humans. Polycyclic Aromatic 

Compo&, Part 1, Chemid, Environmental and Experimental Data, Vo132. Lyon, France, pp. 

33-91, 147-153. 

LaVoie, E.J., S. Amin, S.S. Hecht, et al. 1982. "Tumor initiating activity of dihydrodiols of 

benzo[b]fluoranthene, benzoljlfluoranthene, and benzo[k]fluoranthene. I' Carcinogenesis 3 : 49-52. 

LaVoie, E.J., J. Braley, J.E. Rice, et al. 1987. "Tumorigenic activity for non-alternant polynuclear 

aromatic hydrocarbons in newborn mice." Cancer Lett. 34: 15-20. 

Lide, D.R., Ed. 1991. CRC Handbook of Chemistry and Physics, 1991-1992. 72nd ed. Boca Raton, 

FL, p. 3-96. 

Sellakumar, A. and P. Shubik. 1974. "Carcinogenicity of different polycyclic hydrocarbons in the 

respiratory tract of hamsters." J. Natl. Cancer Znst. 53: 1713-1719. 

United States Environmental Protection Agency (EPA). 1991. Drinking Water Criteria Document for 

Polycyclic Aromatic Hydrocarbonr (PM). Prepared by the Environmental Criteria and Assessment 

Office, Office of Health and Environmental Assessment, U.S. Environmental Protection Agency, 

Cincinnati, OH, for the Office of Drinking Water. ECAO-CIN-DO10. 

United States Environmental Protection Agency (EPA). 1994. Integrated Risk Information System 

(IRIS). Environmental Criteria and Assessment Office, Office of Health and Environmental 

Assessment, Cincinnati, OH.

6 

Van Duuren, B.L., A. Sivak, A. Segal, et al. 1966. "The tumor-promoting agents of tobacco leaf and 

tobacco smoke condensate." J. Nutl. Cancer Inst. 37: 519 -526. 

Wynder, E.L. and D. Hoffmann. 1959. "The carcinogenicity of benzofluoranthenes." Cancer 12: 

1194-1 199.

TOXICITYSUMMARY FOR 

BERYLLIUM 

April, 1992 

Prepared by: 

Mary Lou Daugherty, M.S. 



Health and Safety Research Division* 



Prepared for: 



*Managed by Martin Marietta Energy Systems, Inc., for the U.S. Department of 

Energy under Contract No. DE-AC05-840R21400

Thir page intentionally lefi blank


Beryllium is present in the earth's crust, in emissions from coal combustion, in surface 

water and soil, and in house dust, food, drinking water, and cigarette smoke (U.S. EPA, 

1987a). However, the highest risk for exposure occurs among workers employed in beryllium 

manufacturing, fabricating, or reclamation industries (ATSDR, 1988). Workers encounter 

dusts and fumes of many different beryllium compounds; the current occupational standard 

for worker cxposure to beryllium is 2 ram3 during an 8-hour workshift (OSHA, 1989). 

Inhaled beryllium is absorbed slowly and localizes mainly in the lungs, bone, liver and 

kidneys (Stiefel et aL, 1980, Reeves et aL, 1%7; Reeves and Vorwald, 1%7; Zorn et al., 1988; 

Tepper et aL, 1961; Meehan and Smyth, 1967). Ingested beryllium undergoes limited 

absorption and localizes in liver, kidneys, lungs, stomach, spleen and the large and small 

intestines (Crowley et al., 1949 Furchner et aL, 1973; Watanabe et al., 1985). Significant 

absorption of beryllium or its compounds through intact skin is unlikely because of its 

chemical properties (U.S. EPA. 1987b). Beryllium per se is not biotransformed, but soluble 

salts may be converted to less soluble compounds in the lung (U.S. EPA, 198%). Most orally 

administered beryllium passes through the gastrointestinal tract unabsorbed and is excreted 

in the feces (Reeves, 1%5), whereas inhaled water-soluble beryllium salts are excreted mainly 

by the kidneys (Zorn et aL, 1988). 

Limited data indicate that the oral toxicity of beryllium is low. No adverse effects 

were noted in mice given 5 ppm beryllium in the drinking water in a lifetime bioassay 

(Schroeder and Mitchener, 1975a,b). The dose (converted to 0.54 mag bw/day) was the noadverseeffect 

level (NOAEL) used in the calculation of the chronic oral RfD for beryllium 

of 0.005 madday (U.S. EPA, 1991a). 

In contrast, the toxicity of inhaled beryllium is welldocumented. Humans inhaling 

"massive" doses of beryllium compounds (such as the water soluble sulfate, fluoride, chloride, 

and oxide) may develop acute berylliosis (Constantinidis, 1978). ATSDR (1988) estimated 

that, based on existing data, the disease could develop at levels ranging from approximately 

2-1000 pg Be/m3. This disease usually develops shortly after exposure and is characterizcd 

by rhinitis, pharyngitis, and/or tracheobronchitis, and may progress to severe pulmonary 

symptoms. The severity of acute beryllium toxicity correlates with exposure levels, and the 

disease is now rarely observed in the United States because of improved industrial hygiene 

(Zorn et aL, 1988, Kriebel et al., 1988b). 

Humans inhaling beryllium may also develop chronic berylliosis which, in contrast to 

acute berylliosis, is highly variable in onset, is more likely to be fatal, and can develop a few 

months to 220 years after exposure (Constantinidis, 1978 Hall et al., 1959; Kriebel et aL, 

1988b). Chronic beryllium disease is a systemic disease that primarily affects the lungs and 

is characterized by the development of noneseating granulomas. Tbe disease most likely 

results' from a hypersensitivity response to beryllium as evidenced by positive patch tests 

(Nishimura, 1966) and positive lymphocyte transformation tests (Williams and Williams (1983) 

in exposed individuals. Granulomas may also appear in the skin, liver, spleen, lymph nodes, 

myocardium, skeletal muscles, kidney, bone, and salivary glands (Kriebel et aL, 1988b; 

Freiman and Hardy, 1970). 

- 

1

Epidemiologic studies have suggested that beryllium and its compounds could be 

human carcinogens. In a study that covered 15 regions of the U.S.,Berg and Burbank (1972) 

found a significant correlation between cancers of the breast, bone and uterus and the 

concentration and detection frequency of beryllium in drinking water. However, imperfect 

analytical and sampling methods used in the study prompted the US. EPA (1986b) to 

conclude that these results are not proof of cause and effect relationships between cancer and 

beryllium in drinking water. Studies in workers exposed to beryllium, mostly via inhalation, 

have shown significant increases in observed Over expected lung cancer incidences (Bayliss 

et al., 1971; Bayliss and Lainhart, 1972, Bayliss and Wagoner, 19n, Wagoner et aL, 1980, 

Mancuso, 1970; 1979; 1980). The U.S. EPA (1986a), in evaluating the total database for the 

association of lung cancer with occupational exposure to beryllium, noted several limitations, 

but concluded that the results must be considered to be at least suggestive of a carcinogenic 

risk to humans. In laboratory studies, beryllium sulfate caused increased incidences of 

pulmonary tumors in rats and rhesus monkeys (Vonvald, 1953,1%2 1968, Vomld et aL, 

1955, 1966, Schepers et aL, 1957; Reeves and Deitch, 1969). 

Based on sufficient evidence for animals and inadequate! evidence for humans, 

beryllium has been plad in the EPA weight-ofevidence classification B2, probable human 

carcinogen (U.S. EPA, 1991a). For inhalation exposure, the unit risk value is 24E-3 ( pg/m3)' 

*, and the slope factor is 8.4 (mg/kg/day)'' (U.S. EPA, 1991b). For oral exposure, the unit risk 

value is 1.2E-4 (pg/L)" and the slope factor is 4.3 (mg/kg/day)" (U.S. EPA, 1991a). 

2


Beryllium (Be), a metallic element, belongs to Group IIA of the periodic table and 

has an atomic weight of 9.012 and an oxidation state of +2 (U.S. EPA, 1987a; Budavari et 

al., 1989). Beryllium occurs naturally in the earth's crust at concentrations ranging from 2-10 

ppm. It is also released into the atmosphere from coal combustion at concentrations of -0.01- 

0.1 ng/m3, most likely as beryllium oxide (U.S. EPA, 1987a). Beryllium occurs in house dust 

(0.05-0.1 pg/g), surface water (0.01-1.0 ng/g), and soil (034.0 pg/g) (U.S. EPA, 1987a). Total 

daily intake values for beryllium in the general population are estimated at 1.6 ng/day in air, 

120 ng in food, and 285 ng in water (U.S. EPA, 198%). In addition, a smoker of one pack 

of cigarettes/day could inhale up to 700 ng of beryllium, depending on the type of tobacco 

used (U.S. EPA, 198%). 

Currently, beryllium has many industrial uses (e.g., in brake systems of airplanes, for 

neutron monochromatization, as window material for x-ray tubes, and in radiation detectors) 

(Zorn et al., 1988). The commercially important compound, beryllium oxide, is used in the 

electronics industry as a substrate for transistors and silicon chips, coil cores, and laser tubes 

(Zorn et ai., 1988). 

Although beryllium ore is relatively nontoxic, all other commercially important 

beryllium compounds exhibit significant pulmonary toxicity (ATSDR, 1988). Individuals 

employed in beryllium manufacturing, fabricating, or reclaiming industries are at highest risk 

for exposure and may encounter dusts and fumes of many different beryllium compounds. 

The current occupational standard for worker exposure to beryllium is 2 pg/m3 Over an &hour 

workshift (OSHA, 1989). The U.S.EPA (1987b) reports that new cases of chronic beryllium 

disease are surfacing in industries where the OSHA standard is exceeded, but that few cases 

have been reported where levels do not exceed 

- 

2 pg/m3. 

2 -METABOLISM AND DISPOSITION 


The gastrointestinal absorption of beryllium and its compounds is limited; instead, 

these compounds form insoluble precipitates at about pH 7 (Zorn et al., 1988) and pass out 

of the g.i tract unabsorbed (Reeves, 1965; Furchner et aL, 1973). Two studies in which 

beryllium was given orally to animals as 'Be in single or repeated doses demonstrated that 

< 1% of the administered beryllium was absorbed (Crowley et aL, 1949; Furchner et aL, 1973). 

In another study, rats given beryllium sulfate (6.6 or 66.6 pg berylliudday) in drinking water 

for up to 24 weeks eliminated 6040% in the feces, suggesting at first that significant 

absorption had taken place; however, further analysis of the recovery data revealed that the 

metal was probably precipitated as the phosphate and was not available for absorption 

(Reeves, I=). 

The small amount of gastrointestinal absorption of beryllium that does occur depends 

on the specific compound administered. In hamsters, the absorption of soluble beryllium 

3

sulfate from the g.i. tract exceeded that of insoluble beryllium oxide and beryllium metal 

(Watanabe et aL, 1985); and in rats, the absorption of beryllium oxide exceeded that of the 

hydroxide, and the absorption of beryllium fluoride exceeded that of the chloride, sulfate, 

nitrate, and hydroxide (Bugryshev et al., 1984). Reeves (1%5) concluded from his studies 

that most of the beryllium found in the body was absorbed from the stomach at pH values 

(3.0-3.6 in the rat) that are favorable for maintaining beryllium salts in their ionized and 

soluble form. 

Beryllium is slowly absorbed and retained by the lungs (Stiefel et al., 1980, Reeves et 

al., 1967; Reeves and Vonvald, 1967; Zom et aL, 1988). In one study, rats and guinea pigs 

were exposed for 3 hours to beryllium sulfate aerosol containing 7Be added as the chloride 

(Zorn et aL, 1977). Of the

demonstrated that urinary beryllium levels for rats fed beryllium sulfate doses of 5,50, or 500 

mgkg for 2-years were proportional to intake (Morgareidge et al.; 1977). 

Inhaled water-soluble beryllium salts are excreted mainly by the kidneys, with a halflife 

of 2-8 week (Zorn et al., 1988). Stiefel et al. (1980) found increased levels of beryllium 

in the urine of cigarette smokers (2 pg/L compared with 0.9 pg/L, normal level); in animals, 

urinary elimination of beryllium peaked at 300 ng/g 10 hours after exposure ended. Stress, 

such as that brought on by pregnancy or major surgery, may mobilize beryllium in the body, 

and excretion of the metal in the urine may continue for years. Thus, urinary concentrations 

of beryllium at any point in time reflect only the amount released, and not the total body 

burden (Parka, 1984). 

Beryllium particles are cleared slowly from the lungs. Sanders et al. (1975) measured 

the clearance of beryllium oxide in rats and hamsters. Females of both species had slower 

clearance than did males. Reeves and Vorwald (1967) made similar observations in rats 

exposed to beryllium sulfate, and reported that the clearance half-time exceeded 63 days. 

Rhoads and Sanders (1985) reported that the half-time for removal of 50% of the initial lung 

burden of beryllium, foIlowing up to 3 hours of exposure to the metal, was 400 days. 

3. NONCARCINOGENIC HEALTH EFFEcrs 

3.1. ORALEXPOSURES 


3.1.1.1. Human 

Information on the acute toxicity of beryllium following oral exposure to humans was 

unavailable. 

3.1.12 Animal 

Acute oral LDso values for beryllium range from 18 mg Bekg as beryllium fluoride 

in the mouse to 200 mg Bekg as beryllium chloride in the rat (Reeves, 1986). 

3.12 SubchronicToxicity 

Information on the subchronic toxicity of beryllium following oral exposure to humans 

and animals was unavailable. 

3.13. ChronicToJdcity 

3.13.1. Human 

Information on the chronic toxicity of beryllium following oral exposure to humans 

was unavailable. 

5


In early studies, chronic feeding of large doses of beryllium carbonate (0.1-OS%, 1-5 

gkg of food) to young animals produced rickets (Guyatt et al., 1933; Jacobson, 1933; Kay and 

Skill, 1934). This effect was thought to be the result of the binding of phosphate to beryllium 

in the gut and the subsequent depletion of phosphorus in the body. In a two-year feeding 

study, rats were given dietary levels of 5, 50, or 5000 ppm beryllium (as beryllium sulfate) 

(Morgareidge et al., 1977). Animals of the 5000 ppm group (5 gkg of food) had slightly 

decreased body weights. U.S. EPA (1991a) indicates that an unpublished dietary study by Cox 

et al. (1975) provided a NOEL of 25 mgAcg/day for beryllium. 

Groups of approximately 50 male and female Long-Evans rats and Swiss mice received 

drinking water containing 5 pprn beryllium sulfate for life (Schroeder and Mitchener, 

1975a,b). Body weights were measured throughout the study, and at the time of death, the 

animals were dissected and gross pathology recorded. Blood and urine samples were taken 

from the rats only. A slight depression in growth rate was observed for male rats at 2-6 

months of age and glucose was detected in the urine of the female rats (p

COMMENTS: The NOEL was based on no effects in rats in a lifetime bioassay. 

The uncertainty factor of 100 reflects a factor of 10 each for interspecies conversion 

and for the protection of sensitive human subpopulations. The RfD is limited to 

soluble beryllium salts. 

3.2 INHALATIONEXPOSURES 

321. AcuteToxicity 

321.1. Human 

Acute beryllium diseases in humans result from the inhalation of high concentrations 

of highly dispersed forms of beryllium or its compounds (Zorn et al., 1988). Individuals 

inhaling massive doses of beryllium compounds (such as the water soluble sulfate, fluoride, 

chloride, and oxide) may develop acute berylliosis (Constantinidis, 1978). This disease usually 

develops shortly after exposure and is characterized by rhinitis, pharyngitis, and/or 

tracheobronchitis, and may progress to severe pulmonary disease. The severity of acute 

beryllium toxicity correlates with exposure levels (Zorn et al., 1988). Brief exposure to 

kncentrations of beryllium in air above 100 pg/m3, may cause acute pneumonitis 

characterized by shortness of breath, malaise, anorexia, weight loss, coughing, cyanosis, 

tachypnea and tachycardia (U.S. EPA, 1987, Eisenbud et al., 1948). Lung volumes arc 

reduced and diffuse or localized infiltrates are seen on the chest x-ray (Kriebel et aL, 1988b). 

Although some cases of acute beryllium disease are fatal, most are resolved within a few 

months (Dutra, 1948). Sprince et ai. (1983) reported that 17% of a group of patients with 

the acute disease developed chronic disease in 10 or more years. Acute beryllium diseasc is 

now rarely observed in the United States because of improved industrial hygiene (Kxiebel ct 

aL, 1988b). 

3.212 Animal 

LC, values for beryllium were not found in the available literature. In rats, the lethal 

dose for acute inhalation of beryllium sulfate was 10 mg of the salt/m3 6 hours/day for 5 days 

(Stiefel et al., 1980). 

Brief exposures to beryllium can result in long-term effects. In a pulmonary toxicity 

study, male rats were exposed for one hour in a nose only chamber to an aerosol of 4.05 )rg 

of Be& (as beryllium sulfate) and were examined for toxicity for a year after exposwe 

(Sendelbach et ai., 1989). Parameters for lung toxicity included bronchoahmlar lavage, lung 

cell kinetics, and histopathologic analysis. The activities of alkaline phosphatase (Ak Pase), 

acid phosphatase (Ac Pase), and lactate dehydrogenase (LDH) in lavage fluids were elevated 

3 web after exposure; Alk Pase and LDH levels peaked 3 months after. Microscopic 

examination revealed progressive focal interstitial pneumonitis with a prominent ahmlar 

compdnent of heteromorphic macrophages, neutrophils, and debris. 

In a similar study, higher concentrations of beryllium (800 pg Be metal/m3 for 50 

initial lung burden, 625 pg) caused severe, acute chemical pneumonitis that is followed by a 

7'

quiescent period of minimal inflammation and mild fibrosis (Haley et al., 1990). Progressive, 

chronic-active, fibrosing pneumonitis appeared later. 

3221. Human 

Information on the subchronic toxicity of beryllium following inhalation exposure to 

humans was unavailable. 

The respiratory tract is the target for the subchronic inhalation toxicity of beryllium. 

Schepers et aL (1957) exposed 115 male and female Sherman and Wistar rats to 35 pg/m3 of 

beryllium (as beryllium sulfate) 8 hours/day, 5 dap/week and 4 houdday 1 dayhek for 180 

days. During exposure, 46 exposed rats died from a bacterial infection that affected the heart 

and lungs. At the end of exposure, 17 rats were sacrificed and examined for pdmonary 

effects. Foam-cell clusters, infiltration of macrophages, lobular septalceU proliferation and 

peribronchial and alveolar-wall epithelialization were observed in the treated animals. 

Untreated controls had none of these effects. Fifty-tM, of the exposed rats were maintained 

in beryllium-free air for up to 18 months. These animals demonstrated a progressiwz increase 

in the frequency of pulmonary changes that included atrophic-vesicular emphysema and 

metaplasia of the bronchial epithelium. 

A dose-response for pulmonary effects was suggested in a study of rats exposed to 

beryllium sulfate aerosol 7 houdday for 1-560 days (Vorwald et al., 1966). The animals 

exhibited no speciEc inflammatory abnormalities at an aerosol concentration of 28 pg/m3, 

significant inflammatory changes at 21 pg/m3, chronic pneumonitis at 42 pg/m3, and acute 

berylliosis at 194 pg/m3. Durations of exposure associated with these effects were not clear. 

Tumors developed in animals in both of the above studies: these are discussed in 

Section 4. 

33.1. Human 

Humans inhaling beryllium may develop chronic berylliosis which, in contrast to acute 

berylliosis, is highly variable in onset and can develop a few months to a years after 

exposure (Constantinidis, 1978 Ktiebel et aL, 1988b). Exposure lasting for months to years 

is essential for the development of the disease (Kriebel et al., 1988b). 

The risk of disease, estimated at 1 to 10% (Eisenbud and Lisson, 1983). is probably 

related to both the’ magnitude of the exposure and the type of beryllium compound. The 

more soluble compounds apparently cause the acute disease; whereas, the less soluble 

compounds ax more likely to be associated with the chronic disease (Machle et al., 1948). 

This suggests that the risks are now much lower as a result of the increased effectiveness of 

current occupational and environmental controls (Kriebel et ai., 1988b). In at least one 

8

exception to this. five workers developed lung granulomas after working in an area where 

beryllium fume concentrations were consistently

3 3 2 Animal 

Rats exposed 7 hourslday, 5 daysheek for 72 weeks to 34 pg/m3 of beryllium (as 

beryllium sulfate) had increased lung weights and inflammatory and proliferative changes and 

clusters of macrophages in the alveolar spaces (Reeves et al., 1967). 

See also the section on subchronic exposure, inhalation effects (3-2.2.2). 

3.24. Developmental and ReprodudiveTmkity 

Information on the developmentaVreproductive toxicity of beryllium following 

inhalation exposure to humans and animals was unavailable. 

3-3. Referenoe Concentration 

A subchronic or chronic reference concentration for beryllium was not available. 

33. OTHER ROUTES OF ExposuRE 

33.1. AarteTOaidty 

33.1.1. Human 

Beryllium is a direct irritant and may cause edema and inflammation of any contacted 

tissue (Kriebel et al., 1988b). The eyes and skin are common targets of the acute imtant 

effects of beryllium (Kriebel et al., 1988b). Cutaneous injuries from beryllium metal, alloys, 

or oxide may require surgical excision of the foreign substance to promote h&g (Zorn et 

al., 1988). In addition to primary dermatitis, beryllium may sensitize the skin to subsequent 

contact with the metal. Dermatitis usually abates after exposure stops, but ulceration can 

result from particles retained in the skin (Kriebel et aL, 198%). 

33.12 Animal 

Information on the acute toxicity of beryllium following exposure to animals by other 

routes was unavailable. 

Information on the subchronic toxicity of beryllium following exposure to humans or 

animals by other routes was unavailable. 

333. (=bonicToxicity 

333.1. Human ' 

Chronic dermal contact by beryllium and its compounds may result in skin sensitization 

and contact dermatitis in predisposed persons (Zorn et al., 1988). 

10

333.2 Animal 

Information on the chronic toxicity of beryllium following exposure to animals by 

other routes was unavailable. 


Information on the developmentaUreproductive toxicity of beryllium following 

exposure to humans by other routes was unavailable. 

33.42 Animai 

Intratracheal injection of rats with 50 mg/kg of beryllium chloride or beryllium oxide 

on (one or more) days 3,5, or 8 of gestation produced increases in fetal mortality, decreases 

in fetal weight, and increases in the percentages of pups with internal abnormalities 

(Selivanova and Savinova, 1986). 

Rats, treated intratracheally with beryllium oxide (0.2 mg berylliudrat) and allowed 

to mate repeatedly over 15 months, displayed no change in reproductive performance (Clary 

et aL, 1975). 

3.4. TARGEI' ORGANSICRITICAL EFFECIS 

3.4.1.1. PrimrUy Target Organs 

Skeletal system: Rickets in young animals appeared to be the result of the binding 

of phosphate to beryllium in the gut. 

3.4.12 Other Target Organs 

None 

3.42 lnhalrtionExposures 

3.4.21. Primary Target Organs 

Lungs: Chronic beryllium disease is characterized as an immunologkdly mcdiatcd 

granulomatous lung disease in humans and appears to be the result of direct chemical 

toxicity and foreign-body-type reactions in rats. 

3.4Z Other Target Organs 

Skin, liver, spleen, lymph nodes, myocardium, skeletal muscles, kidney, bone, and 

salivary glands may &%it granulomas, similar to those of the lungs. 

11

4. CARCXNOGENICITY 

4.1. ORALEXPOSURES 


In the late 1970’s, epidemiological studies suggested that beryllium and its compounds 

could be human carcinogens. In a study that cwered 15 regions of the U.S., Berg and 

Burbank (1972) found a significant correlation between cancers of the breast, bone, and 

uterus and the concentration and detection frequency of beryllium in drinking water. 

Mortality rates in areas with beryllium in the drinking water were excessive only for nonwhite 

males. The probability of a positive association ranged from O.OO6-0.040. However, imperfect 

analytical and sampling methods used in the study prompted the US. EPA (1986b) to 

conclude that these results were not proof of cause and effect relationships between cancer 

and beryllium in drinking water. 


Chronic oral administration of beryllium to animals produced equivocal carcinogenicity 

results in two studies. In one study, mice and rats treated with drinking water containing 5 

ppm beryllium (as beryllium sulfate) had slightly higher incidences of leukemias and grossly 

observed tumors, but the increases were not statistically significant (Schroeder and Mitchener, 

1975a,b). In the other study, male Wistar rats fed diets containing 0, 5, 50, or 500 ppm 

beryllium as beryllium sulfate for 104 weeb had statistically significant increases in the 

incidence of reticulum cell sarcoma at the two lowest doses, but no response at the highest 

dose (Morgareidge et al., 1975). The U.S. EPA (1986b) concluded that this study is 

suggestive of a carcinogenic response to ingested beryllium, but the lack of response at the 

high dose and the lack of peer review or publication of the study limits the interpretation as 

a positive study. 

4.2 INHAIA”IONEXP0SURES 

421. Human 

Infante et al. (1980) conducted a lung cancer mortality study of white males listed in 

the BCR using a retrospective cohort method. Of the cohort consisting of 421 individuals, 

139 had died and 64 had no vital statistics; 15 of the 139 that died had no cause of death 

listed. In terms of total cancer, 19 deaths were observed vs. 1241 expected for white males. 

In term of lung cancer, 6 deaths were observed 15 or more years after exposure vs. 281 

expected (~~0.01). However, the study used the NIOSH life table program which results in 

an 11% excess in the calculated expected number of lung cancer deaths (Wagoner et aL, 

1980). When the expected lung cancer deaths were adjusted for using the NIOSH program, 

the p value was reduced to ~0.09, questionable or borderline significance. Further analysis 

of the data from this study revealed a positive correlation for increased cancer and acute (but 

not chronic) beryllium disease. However, the NIOSH life tables were used for some of the 

calculations and the results are therefore questionable (U.S. EPA, 1987). 

12

Several epidemiological studies of lung cancer were conducted among beryllium 

workers from two plants (Bayliss et al., 1971; Bayliss and Lainhart, 1972; Bayliss and 

Wagoner, 1977; Wagoner et al., 1980; Mancuso, 1970; 1979 1980). The studies, based on 

personnel records and social security quarterly earnings reports, were equivocal regarding the 

carcinogenicity of beryllium. For example, three studies revealed significant increases in 

observed over expected lung cancer cases in workers who were (a) employed from 1942-1967 

and followed for ten additional years (pc0.05) (Bayliss and Wagoner, 1977; Wagoner et al., 

1980); (b) employed from 1937-1948 and followed for 30 additional years (~~0.01) (Mancuso, 

1980); and (c) combined workers of both plants who were employed from 1942-1948 and 

followed for an additional 28 years (Pc0.01) (Mancuso, 1979). However, the studies were 

considered to be limited because of methodological constraints and deficiencies such as no 

correction for smoking (U.S. EPA, 1991a). 

The U.S.EPA (1986a) evaluated the total database for the association of lung cancer 

with occupational exposure to beryllium, and noted several limitations. However, in spite of 

the limitations of the studies, U.S. EPA (1986a.b) concluded that the results must be 

considered to be at least suggestive of a carcinogenic risk to humans. 

Inhalation studies have tested the carcinogenic potential of beryllium in various animal 

species. Table 1 shows that beryllium sulfate causes increased incidences of pulmonq 

tumors in rats and rhesus monkeys (Vonvald, 1953, 1962, 1%. Vorwald et al., 1955, 1966, 

Schepers et al., 1957; Reeves and Deitch, 1969). Rats exposed to concentrations of beryllium 

ranging from 1.8 to 180 mg/m3 exhibited increased incidences of pulmonary carcinomas that 

ranged from 20 to 100% (Vorwald 1953; 1%2). The animals were exposed 33-38 hoursheel 

for 3 to 24 months. The incidence of lung tumors exhibited a weakly positive correlation With 

exposure concentration and duration. Schepers et al. (1957) observed a 43% increase in the 

incidence of pulmonary carcinomas in rats exposed to 32-35 mg/m3 beryllium 44 hoursheel 

for 69 months followed by an l&month obsemtion period. These investigators identified 

eight histologically distinct types of tumors in the lungs of exposed rats. The tumors were 

metasticking and transplantable. Reeves and Deitch (1%9) observed an approximate 100% 

incidence in lung tumors in rats exposed to 36 mg/m3 beryllium 35 hoursheek for up to 18 

months. The studies of these investigators indicated that tumor yield in rats was dependent 

upon age at exposure rather than on duration of exposure. 

Tumor incidences were also increased in rats exposed to beryllium phosphate, 

beryllium fluoride, and beryl ore (Schepers, 1961; Wagner et al, 1969). 

43. OTHER ROUTES OF EXPOSURE 

Beryllium is carcinogenic when administered by intratracheal and intravenous 

injections and implantation into bone. Intratracheal injection o€ beryllium into rats induced 

cancer’incidences ranging from @loo%, with latency periods of at least 6 to 9 months 

(Vonvald and Reeves, 1959; Spencer et al., 1968, 1972, Ishinishi et aL, 1980, Groth et al., 

1972; 1976; 1980, Groth and MacKay* 1971). Several investigators have induced 

osteosarcomas in rabbits (Nash, 1950; Dum and Largent, 1950; Yamaguchi and Katsura, 

1963; Sissons, 1950; and others) and mice (Cloudman et al., 1949) with intravenous injection 

13

Concentration Weekly Exposure Duration of Exposure Incidence of Pulmonary Reference 

(mghn’ as Be) lime (hours) (months) Carcinoma 

Emyllium sulfate 

Rat 

Rat 

33-35 33-38 12-14 4B (females) Vmld, 1953 

33-35 33-38 13-18 17/17 Vorwald et al., 1955 

32-35 44 6-9, followed by 58/136 SCheperS et al., 1957 

18-month observation 

55 33-38 3-18 55/74 Vorwald, 1962 

Rat 

Rat 

Rat 

Rat 

Rat 

Rat 

Rat 

Rat 

180 33-38 12 11R7 Vorwald, 1962 

18 33-38 3-22 72/103 Vorwald, 1%2 

18 33-38 8-2 1 31/63 Vmld, 1962 

18 33-38 9-24 47190 Vmld, 1962 

18 33-38 11-16 9t21 Vmld. 1962 

1 a-2.0 33-38 E21 25/50 Vowald, 1962 

Rat 

Rat 

Rat 

Rat 

Rat 

Rat 

14

~ 

TABLE 1. (Continued) 

cOmpOUnd/Species 

BcqUium sulfhtc 

Rat 

Rat 

Rat 

Rhesus monkey 

Rhesus monkey 

Guinea pig 

Guinea pig 

Guinea pig 

Concentration Weekly Exposure Du~~~ion of Exposure Incidence of Pulmonary Reference 

(mglm' as Be) lime (hours) (mom hs) Carcinoma 

36 35 9 15/15 (both sexes) Reem and Deitch, 1969 

-16 35 12 21R1 (both sexes) Reeves and Deitch, 1%9 

-16 35 18 13/15 (both sexes) Reeves and Deitch, 1%9 

35-200 42 8 014 (females) Schepers, 1964 

-78.8 15 36+ 811 1 Vorwald, 1964 

35 NR' 12 0 Schepers, 1%1 

36 35 12 2/20 Schepers, 1971 

3.7-30.4 35 18-24 0158 Reeves et al., 1972 

-m- 

Rat 

Rat 

Rhesus monkey 

Rhesus monkey 

Rhesus monkey 

Bayllium Buoride 

Rat 

Rhesus monkey 

32-35 NR' 1-12 35-60/17@' Schepcn, 1%1 

227 NR' 1-12 7/4@ schepen, 1%1 

200 42 8 014 (females) 

Schepers, 1%1 

~- ~ 

1100 42 8 014 (females) Schepen, 1964 

8Mo 42 8 0/4 (females) Shepers, 1964 

9 NR' 6-15 10-20/200 Schepcrs, l%l 

180 42 8 014 (females) Schepers, 1964 

15

Y 

I 

I 

Conantration 4 

TABLE 1. (Continued) 

Reference 

ii 

'NR = Not reported 

bNumbcr of tumorsMumber of animals exposed 

16

and subperiosteal or intraosseous implantation of beryllium and several of its compounds. 

The incidence of osteosarcoma ranged from 0-100% by either route of administration, with 

a latency period of r9 months. 

4.4. EPA WEIGHT-OF-EVIDENCE 


Not assigned. 

4.42 Inhalation 

Classification - B2, probabIe human carcinogen 

Basis - Inadequate evidence for humans; sufficient evidence for animals (U.S. EPA, 

1991a). "Beryllium has been shown to induce lung cancer via inhalation in rats and 

monkeys and to induce osteosarcomas in rabbits via intravenous or intramedullary 

injection. Human epidemiology studies are considered to be inadequate." 

45. SLOPEFAClKlRS 

45.1. Oral 

SLOPE FACTOR: 4.3 (mg/kg/day)-' 

DRINKING WATER UNIT RISK: 1x4 (pg/Lr' 

VERIFICATION DATE: 02/01/89 (U.S. EPA, 1991a) 

PRINCIPAL, STUDY Schroeder and Mitchener (1975a) 


SLOPE FACTOR: 8.4 (mg/kg/day)" 

INHALATION UNIT RISK: 24E-3 ( pglm')" 

VERIFICATION DATE: OSAW88 (U.S. EPA, 1991a) 

PRINCIPAL STUDY Wagoner et al. (1980) 

17

5. REFERENCES 

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18

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19

Jacobson, S.A. 1933. Bone lesions in rats produced by the substitution of beryllium for 

calcium in the diets. Arch. Pathol. 15: 18-26. 

Kay, H.D. and D.L Skill. 1934. Prevention and cure of beryllium rickets. Biochem. J. 28: 

1222-1 229. 

Kriebel, D., N.L Sprince, E.A. Eisen, LA. Greaves, H A Feldman and R.E. Greene. 1988a. 

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Kriebel, D., J.D. Brain, N.L. Sprince and H. Kazemi. 1988b. The pulmonary toxicity of 

beryllium. Am. Rev. Respir Dis. 137: 464-473. 

Machle, W., E Beyer and E Gregorius. 1948. BeryllioaiS Occup. Med. 5: 671-683. 

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Particulate Dust and Their Extension into the Environment. Pathrotox Publishers, Inc. 


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Meehan, W.R and LE Smyth. 1967. Occurrence of beryllium as a trace element in 

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beryllium in the rat. Toxicol. Appl. Phannacol. 41: 204-205. 

Nash, P. 1950. Experimental production of malignant tumors by beryllium. Lancet 1: 519. 

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. 

20

Reeves, AL 1965. The absorption of beryllium from the gastrointestinal tract. Arch. 

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Exp. Tumor Res. 2 203-224. 

1961. Neoplasia experimentally induced by beryllium compounds. Pmg. 

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21

Selivanova, LM. and T.B. Savinova. 1986. Effects of beryllium chloride and oxide on the 

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22

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23

ToxIClTY SUMMARY FOR 

BiS( 2--)PHTHALATE 

MARCH 1993 

Prepared by 

Andrew Francis, M.S., DABT 




Oak Ridge National Laboratory' 


Prepared for 



*Managed by Martin Marietta Energy Systems, Inc., for the U.S. Department of 

Energy under Contract No. DE-A~S-840R21400

page intentionally left blank

Bk(2-ethylhexyl)phthalate is a colorless oily liquid that is extensively used as a 

plasticizer in a wide variety of industrial, domestic and medical products. It is an 

environmental contaminant and has been detected in ground water, surface water, drinking 

water, air, soil, plants, fsh and animals (Sittig, 1985; Sandmeyer and Kirwin, 1978). It is 

rapidly absorbed from the gastrointestinal tract primarily as mono(2ethylhexyl)phthalate 

(Pollack et al., 1985; Teirlynck and Belpaire, 1985). The diester can be absorbed through the 

skin and from the lungs (Elsisi et aL, 1989; Pegg, 1982). It is rapidly metabolized in the blood 

and tissues to the monoester, which can be excreted as a glucuronide conjugate or further 

hydrolyzed to phthalic acid and excreted (Kluwe, 1982; Albro et al., 1982). 

Animal studies have indicated that the primary target organs are the liver and kidneys 

(Carpenter et aL, 1953; U.S. EPA, 1987a,b); however, higher doses are reported to result in 

testicular effects and decreased hemoglobin and packed cell volume (Kluwe et al., 1982; Gray 

et ai., 1977). The primary intracellular effects of bk(2ethylhexyl)phthalate in the liver and 

kidneys are an increase in the smooth endoplasmic reticulum and a proliferation in the 

number and size of peroxisomes (Kluwe et al., 1982, Reddy and Lalwani, 1983; Tomasawski 

et aL, 1986). An epidemiological study reported no toxic effects from occupational exposure 

to air concentrations of bk(2ethylhexyl)phthalate up to 0.16 mg/m3 (Thiess et aL, 1978). 

Other studies on occupational exposures to mixtures of phthalate esters containing bir(2- 

ethylhq1)phthalate have reported polyneuritis and sensory-motor polyneuropathy with 

decreased thrombocytes, leukocytes and hemoglobin in some exposed workers (Milkov et aL, 

1973; Gilioli et al., 1978). Developmental toxicity studies with rats and mice have shown that 

bir(2ethylhexyl)phthalate is fetotoldc and teratogenic when given orally during gestation 

(Wolkowski-Tyl et aL, 1984a and b; Shiota and Mima, 1985). Oral exposure has ais0 been 

shown to result in decreased sperm count in rats (Siddipui and Srivastava, 1992) 

A Reference Dose (RfD) of 0.02 mg/kg/day for both subchronic and chronic oral 

exposure was calculated from a lowest-observed-adver-effect level (LOAEL) of 19 

mg/lcg/day based on increased relative liver weight in guinea pigs given 0, 19, or 64 mg bk(2- 

ethylhexyl) phthalat&g/day for 12 months in their diet (Carpenter et aL, 1953; U.S. EPA, 

1992 a,b). A Reference Concentration (Euc) €or inhalation exposure is not available (U.S. 

EPA, 1992b). 

bir(2ethylhexyl)phthalate is known to induce the proliferation of peroxisomes, which 

has beem associated with carcinogenesis (Rao and Reddy, 1991). Dosedependent, 

statistically-significant increases in the incidences of hepatocellular carcinomas and combined 

carcinomas and adenomas were seen in mice and rats exposed to bis(2ethylhexyl)phthalatc 

in their diet for 103 weeb (Kluwe, et al, 1982). An increased incidence of neoplastic 

nodules and hepatocellular carcinomas was also reported in rats (Rao et al., 1990). 

Based on U.S. EPA guidelines, bk(2ethylhexyl)phthalate was assigned to weight-ofevidence 

Group BZ probable human carcinogen, on the basis of an increased incidence of 

liver tumors in rats and mice. A carcinogenicity slope factor (st') of 0.014 (mgikg/day)'* for 

oral exposure was based on the combined incidence of hepatocellular carcinomas and 

1

adenomas in male mice (Kluwe, et al., 1982, U.S. EPA, 1992b). A drinking water unit risk 

- of 4.OE-7 (pg/L)” was calculated based on the q,.. A quantitative estimation of carcinogenic 

risk from inhalation exposure is not available (US EPA, 1992b). 

2


Bh(2-ethylhexyl)phthalate or di(2-ethylhexyl)phthalate (C;,H,O,, CAS registry 

number 117-81-3) is a clear oily liquid with a molecular weight of 390.54. It has a melting 

point of -50°C; a boiling point of 387°C at 760 mm Hg and 230°C at 5 mm Hg; and a vapor 

pressure of 1.2 mm Hg at 2WC It has a density of 0.9861 and is practically insoluble in 

water (0.40 mgL at 25°C). bis(2-ethylhexyl)phthalate has a flash point of 2183°C. The 

relatively high flash point, boiling point and low vapor pressure contribute to the high stability 

of this phthalic acid ester (Sittig, 1985; Sandmeyer and Kirwin, 1978; U.S. EPA. 1987a). 

Bis(2-ethylhexyl)phthalate is primarily used in the plastics industry as a plasticizer with 

such varied applications as wire insulation, food packaging and biomedical applications such 

as tubing and blood containers. Other uses include vacuum pump oil and as a dielectric fluid 

in capacitors (U.S. EPA, 1987b, Budavari, 1989). The combined annual production of dioctyl 

phthalates in the United States exceeds 300 million pounds (U.S. EPA, 198fb). The widespread 

uses of bi,s(2-ethylhexyl)phthalate have made the compound, along with other phthalic 

acid esters, ubiquitous in the environment. It has been detected in ground water, surface 

water, drinking water, air, soil, plants, fish and animals. Air concentrations in certain PVC 

manufacturing plants have been reported to range from below 0.02 to 05 mum3 (Vainiotalo 

and Pfaffti, 1990). Some exposure OCCUK from leaching of the compound from mntainers 

used in the food and medical industries (U.S. EPA, 1987b; Callahan et aL, 1979). This is of 

particular concern to patients exposed to large amounts of blood or blood products. 'Ihe 

chemical is extracted from the containers by the blood and is converted to mono(2- 

ethy1hexyl)phthalate by a plasma enzyme (Labow et al, 1988). Experiments have shown that 

33 mg bis(2ethylhexyl)phthalate/gm of bag material were extracted in five days with bovine 

calf serum, whereas bags tested with saline resulted in no soluble plasticizers (Chawla and 

Hinberg, 1991). 

In the environment, bir(2ethylhexyl)phthalate undergoes biodegradation in water and 

soil, and is predicted to react with hydroxyl radicals in the atmosphere. It is estimated to have 

a half life of about 12 hours in the air, 10 to 20 days in the soil, and days to weeks in water 

(U.S. EPA, 1987qb). Volatilization of bh(2ethylhexyl)phthalate from contaminated water 

does not contribute significantly to its removal. The half-life of the molecule due to 

evaporation alone from bodies of water has been estimated to be as long as 15 years (US. 

EPA, 1987a.b; Callahan et aL, 1979). In the marine environment bis(2-ethylhexyl)phthdatc 

has been shown to be rapidly degraded by experimental microcosms (Davey et A, 1990). It 

has been found to bind to organic acids in the soil and water resulting in an increase in its - 

solubility and its mobility in the environment (Matsuda and Schnitzer, 1971). It also adsorbs 

to both freshwater and marine sediments where it may serve as a long-term sink (U.S.EPAb, 

1987, Sullivan et al., 1982). 

Experiments have shown that fLh do not extensively bioaccumulate biS(2- 

ethylhexy1)phthalate. Rainbow trout studies indicate $hat the diester is converted to the 

monoester by the gills before absorption from the water occurs, thus limiting the absorption 

of the diester (Barron et at, 1989). 

3

2 METABOLISM AND DISPOSITION 


Bk(2ethylhexyl)phthalate can be absorbed from the gastrointestinal tract., the lungs, 

and through the skin. Over 90% of an oral dose of bk(2ethylhexyl)phthalate was absorbed 

by the gastrointestinal tract of rats as evidenced by the excretion of metabolites (Williams and 

Blanchfield, 1974). However, gastrointestinal absorption is complicated by the hydrolysis of 

the diester to the monoester derivative by pancreatic enzymes and enzymes in intestinal 

mucosal cells. The monoester is then absorbed. Gavage studies on rats by Teirlynck and 

Belpaire (1985) showed an average plasma concentration of 8.8 pg/d of the diester compared 

to 63.2 &ml of the monoester 3 hours following a single oral dose of 2.8 g/kg of bk(2- 

ethylhexy1)phthdate. Similar studies by Pollack et aL (1985) demonstrated that 80% of a 

single oral dose was absorbed as the monoester, whereas only 13% of the dose was absorbed 

as bk(2-ethylhexyl)phthalate. These observations must be taken into account when route-toroute 

extrapolations are considered (U.S. EPA 1987b). 

Although it is known that phthalic acid esters can be absorbed by inhalation, there are 

little quantitative data available for this route of exposure (U.S. EPA 1987a). Pegg (1982) 

studied the pulmonary absorption of an aerosol of 14C-6k(2-ethylhexyl)phthalate by adult male 

Sprague-Daw19 rats, The animals were exposed for 6 hours to a concentration of 100 mg/m3 

in a heads-only chamber. The radioactivity appearing in the blood at various times following 

exposure and the radioactivity tccovered from urine, feccs, skin and the carcass were 

measured 72 hours after expasurc. The disappearance of radioactivity ftom lung tissue was 

also measured leading to the conclusion that absorption was rapid and complete. 

Bk(2ethylhezyl)phthalate can also be absorbed through the skin. This is primarily 

a hazard €or workers in the plastics industry, but other exposures can occur such as contact 

with the chemical leached horn vinyl swimming pool liners (U. S. EPA 1980). Quantitative 

absorption data are not available, however, guinea pig studies have indicated a LDW of 10 

gkg for dermal exposure (Autian, 1973; US. EPA, 1980). Excretion and distribution of 

radioactive labeled [“C]-bk(2ethylhexyl)phthalate applied to the shaved backs of male F-344 

rats at concentrations of 30 to 40 mg/kg was followed Over a period of seven days 

demonstrating dermal absorption by rats (see sections 2.2 and 24) (Elski et al, 1989). 

22 DISlRIBUTION 

Bk(2-ethylhexyl)phthalate and its metabolites are distributed primarily to plasma, 

liver, kidney, the gastrointestinal tract, and fat following oral exposure. Some metabolites 

have ken found in almost all tissues especially the monoester metabolite, which has been 

found in relatively high concentration in the testes of rats. Maximum concentrations of bk(2- 

ethy1hexyl)phthalate and the monoester metabolite were reached in blood and the tissues in 

6-24 hours after a single oral dose of 9.8 gkg in corn oil (0shi.and Hiraga, 1m U.S. =A, 

198%). Elsisi et aL (1989) applied 30 to 40 mg 6k(2-ethylhexyl)phthalatekg to the shaved 

back of F-344 rats and followed the distribution of radioactive label. Most of the label was 

found in fat, skin and muscle after seven days. 

4

23. METABOLISM 

The first step in metabolism of bir(2-ethylhexyl)phthalate is hydrolysis to the 

monoester derivative, which primarily occurs in the gastrointestinal tract following oral 

exposure, but also occurs in the tissues. A glucuronide conjugate can be formed with the 

monoester or the terminal or next to last carbon in the monoester molecule can be oxidized. 

After the carboxylic acid derivative is formed, the length of the side chain can be decreased 

by B oxidation. The monoester can also be hydrolyzed to phthalic acid (Klue, 1982; Albm 

et aL, 1982; Williams and Blanchfield 1974; U.S. EPA, 198%). 

Rat studies indicate that the diester is removed faster from most tissues than the 

monoester with half-lives from 15 hours for lung tissue to 284 hours for liver and 156 hours 

for epididymal fat. bir(2ethylhexyl)phthalate is fat soluble and remains unmetabolized in fat 

tissue much longer than in other tissues. The monoester has a half-life of about 32 hours in 

liver tissue and 68 hours in epididymal fat. It also has a half-life of about 50 hours in the 

testes, compared to 8.3 hours for the diester (Oishi and Hiraga, 1982, U.S. EPA 198%). 

The mono(Zethylheq4)phthalate metabolite has been shown to accumulate in the 

testes of rats following treatment with bk(2ethylhexyl)phthalate (Oishi, 1990). In vitro 

studies have shown that testicular tissue does not further metabolize the monoester (Albm 

et al., 1989). 

24. EXCREIION 

Since bLs(2ethylhexyl)phthalate is rapidly converted to the monoester derivative, 

solubilization and -tion of the monoester becomes the primary metabolic task. Mm 

spies tested, including humans, excrete the monctester as a glucuronide conjugate in the 

urine, feces and bile. Rats, apparently, are an exception and primarily oxidize the terminal 

or next to last carbon in the monoester molecule before excretion. The monoester can also 

be further hydrolyzed to phthalic acid and excreted (Kluwe, 1982, Albm et aL, 1982). An 

average half-life of about 12 hours has been reported in humans following a single dosc of 

bk(2ethylhexyl)phthalate (Schmid and Schlaffer, 1985; U.S. EPA, 198%). Excretion of [“qbLr(2ethylhexyl)phthalate 

after dermal absorption in F-344 rats was followed over a period 

of seven days. Radioactive label was found in the urine and feces; urine was the major route 

of elimination (Elsisi et aL, 1989). 


3.1. ORALEXPOSURES 

3.1.1. Acute Tdty 

3.1.1.1. Human 

Ingestion of 5 and 10 g of bh(2ethylhexyl)phthalate by human volunteers resulted in 

mild gastrointestinal disturbances with the 10 g dose and no effects from the 5 g dose (Shaffer 

et aL, 1945). 

5’

3.1.12 ADimal 

Oral LDw values of 30 g/kg, 30.6 g/kg, and 34 gkg have been listed for mice, rats and 

rabbits respectively (Sittig, 1985; Sax and Lewis, 1989). 

3.12 SubchronkToaiCity 

3.121. Human 

Information on the subchronic oral toxicity of bir(2ethylhexyl)phthalate in humans 


3.122 Animal 

Gray et aL (1977) observed a variety of symptoms after feeding groups of 15 male and 

15 female Sprague Dawley rats 0,O.z 1.0, or 2% bis(2ethylhexyl)phthalate (0, 150, 750, or 

1500 mgkgday, respectively) in their diet for 17 weeks. Increased absolute and relative liver 

weights were observed in all treated groups. Food consumption and growth rates were 

reduced in the 1 and 2% treated groups. A dose-related reduction in testicular weight and 

an increase in testicular damage were observed. Decreased hemoglobin concentration was 

observed in male rats, and decreased packed red cell volume was also observed in both sexes 

in the two highest dose groups. An interstitial nephritis, increased SGPT and decreased 

blood gluoose were reported by Nagasaki et al. (1974) in a 48 week rat study (U.S.EPA, 

1987a). Animals in this study were fed 500 or loo0 ppm bir(2-ethylhexyl)phthalate in the diet 

(25 or 50 rng/I@lay, rcspactively). Ota et aL (1974) reported degenerative changes in the 

kidneys and l kr of mice given 05 to 5 g/kg/day in the diet for 1 to 3 months. Male albino 

ferrets fed 1% bi3(2ethylhcxyl)phthalate in the diet for 14 months exhiiited decreased body 

weight, increased liver weight with morphological and biochemical changes, and testicular 

damage (take et al., 1976 US. EPA 1987b). 

3.13. CbronicTaxicity 

3.13.1. Human 

Information on the chronic oral toxicity of bis(2ethylhcxyi)phthalate in humans was 

not available. 

3.132 Animal 

Carpenter et al. (1953) fed groups of 32 male and 32 female Sherman rats 0,0.04, 

0.13, or 0.4% bis(2-ethylhsryl)phthalate (0,20,60, or 200 mgkg/day, respectively) in the diet 

for one year during which time they were allowed to breed. After one year, groups of eight 

males and eight females were continued on the same regimen and groups of 32 male and 32 

female of€spring were fed 0, and 0.4% (200 mg/kg/day) bis(2etbylhexyl)phthalate in the diet 

Sigmfkantly increased liver and kidney weights were observed with the high dose in the male 

parental group and in both sexes of the F, group. No other treatment related effects were 

reported in the rats. The same study also included guinea pigs and dogs. Groups of 22-24 

male and 22-24 female guinea pigs were fed the equivalent of 0, 19 or 64 mg/kg/day bir(2- 

6

ethylhexy1)phthalate for one year. Groups of 4 dogs randomly selected were given the 

equivalent of 54.7 mg/kg/day for about four weeks and then 0.06 mgkg/day for about 48 

week One dog was given a TWA dose of 79.3 mg/kg/day for a total of 246 days. Increased 

relative liver weight was seen in all treated groups of female guinea pigs, however, no 

histological changes were reported, The dog that received the TWA dose of 793 mg/&g/day 

developed fatty vacuolation and congestion in the liver and cloudy swelling and congestion 

in the kidneys. No effects were reported for the other groups of dogs (U.S. EPA, 1987a). 

Two year dietaly studies have been performed on groups of 50 male and 50 female 

F344 rats and W F , mice (NTP, 1982; Kluwe et al., 1982). Rats were given 0,6OOo, or 

l2,OOO ppm in the diet (0,322,674 mg/kg/day for males; 0,394, 774 mg/’kg/day for females). 

Mice were given 0,3000, or 6OOO ppm in the diet (0, 672, 1325 mg/kg/day for males; 0, 799, 

1821 mgkglday for females). Dtcreased body weight was observed in all treated male raq 

and female rats in the high doae group, and in all treated female mice. An increased 

incidence of seminiferous tubule degeneration was observed at the highest dose in both rats 

and mice (U.S. EPA, 1987b). Renal cysts have been reported to appear in rats fed 150 mg/kg 

three timeshveek for a year, but not when the chemical is given for six months (Woodward, 

1990). 

One of the most commonly observed effects of bis(2ethylhexyl)phthalate treatment 

is an increase in liver and kidney weights. The intracellular effects that accompany or amunt 

for the in- weights arc an increase in the smooth endoplasmic reticulum and a 

proliferation in number and size of peroxisomes. Ganning et al. (1990) fed male Spraguc- 

Dawley rats a diet containing 0.02, 0.2 or 2% bis(2ethylhexyl)phthalate for 102 weeks. 

Decreased body weight was seen only in the 2% group, however enzyme changes that reflect 

the proliferation of peroxisomes occurred in a dose related manner. Peroxisomal palmitoyl- 

CoA dehydrogenase and mitochondrial carnitine acetyltransferase activities increased to a 

maximum in 20 wetb. Comparable levels were also reached in the 0.2% dose group by the 

end of the experiment. Peroxisomal catalase increased during the first year, but decreased 

to control levels during the second year of treatment. All ewe activities returned to 

control values within 2-3 weeks following cessation of treatment. Peroxbomes contain a 

number of oxidative enzymes that affect the metabolism of the bir(2ethylharyl)phthalatc and 

other intracellular molecules, especially Eats. This proliferation of peroxisomes has been 

linked with carcinogenic activity (Reddy and Lalwani, 1983; Tomaszewski et al., 1986). 

3.1.4. DeveIopmentaI and Repductivc Toxicity 


Information on deveiopmental and reproductive toxicity of bis(2-ethylhexyl)phthalak 

in humans following oral expasure was not available. 


A number of studies have reported fetotoxic and teratogenic effects in rats and mice 

following exposure to bis(2-ethylhql)phthalate. Nikonorow et al. (1973) observed incressed 

resorption of fetal implants and decreased fetal weight when 1.7 g biS(2)- 

ethylhq1)phthalateAcg body weight was given orally on days 0-21 of gestation. Bell et aL 

7

(1979) reported decreased fetal body weights, increased relative fetal liver weights, and 

reduced sterologenesis in fetal brain and liver in Sprague Dawley rats fed 05% bis(2- 

ethylhexy1)phthalate on days 5-18 of gestation. Wolkowski-Tyl et al. (1984a) fed groups of 

rats 0, 0.5, 1.0, 15, or 20% bh(2-ethylhexyl)phthalate (equivalent to 0, 356.7, 666.4, 856.5, 

or 1054,8 mg/kg/day, respectively) in their diet on days 0-20 of gestation. Some maternal 

effects were seen, including decreased body weight, increased absolute and relative liver 

weight, and increased gravid uterine weight. Dose-related increases in the number of fetal 

resorptions and in the number of dead and malformed fetuses per litter were also reported. 

There was a dose-related decrease in fetal weight that was significant in all treated groups. 

Wolkowski-Tyl et al. (1984b) also studied the effect of 0, 0.025, 0.05,0.1, or 0.15% 

bh(2-ethylhexyl)phthalate (equivalent to 0,44,91,191, or 292 mg/kg/day, respectively) in the 

diet given to mice on days 0-18 of gestation. Maternal effects observed were decreased body 

weight and increased relative k r weight, both effects significant at 0.1 and 0.15% in the diet. 

Dose-related increases in rcsorptions and in dead fetuses per litter were significant at doses 

of 0.1 and 0.15%. Significant increases in malformed fetuses per litter, with external, visceral 

and skeletal defects, were observed at doses of 20.15%. Studies utilizing higher oral doses 

(250, 500, lO(10 or ZOO0 mag) by Shiota and Mima (1985) and (0.05, 0.1, 0.2, 0.4 or 1.0% 

diet) by Shiota and Nishimura (1982) and Shiota et aL (1980) demonstrated increased 

numbers of fetuses with gross external malformations, including neural tube defects. The 

incidence of resorptions increased up to 100% in animals fed 0.4 and 1% bis(2- 

ethylhexy1)phthalate in their diets. Mice were shown to be most sensitive to the teratogenic 

effects of bis(2ethylhexyl)phthalate on days 7 and 8 of gestation. Treatment on day 7 with 

1 mvkg resulted in increased fetal mortality, resorptions, and gross external and skeletal 

anomalies Treatment on day 9 or 10 with up to 30 mUkg produced no rcsorptions, fetal 

mortality or malformed fetuses (Yagi et al, 1980). 

Mono(2ethylhcxyl)phthalate, a principle metabolite of bis(2ethylhexyl)phthalate. was 

fed to pregnant 0-1 mice on days 0 through 17 of gestation (0, 0.13, 0.26, 0.48 or 0.97 

mmoykglday). Increased maternal liver weight was observed at doses >0.48 mmovlrg and 

decreased weight gain was observed at the 0.97 mmol dose. Dose related i n d fetal 

mortality, the % of litters with malformed fetuses, and the % of malformed fetuses per litter 

were seen in all treated groups. Other metabolites including 2ethylhexanol had no effect. 

Qualitatively, the effect of the monoester was similar to the diester in oral studies (Price et 

aL, 1991). 

A dose related decrease in sperm count has been reported in rats given 500 or lo00 

mgkg/day orally bis(2ethylhsryl)phthalate for 15 days. Decreased epididymis weight was seen 

in the loo0 mg/kg/day dose group (Siddiqui and Srivastava, 1992). Decreased absolute and 

relative testicular weights were seen in rats given 2OOO mg/kg/day orally for 15 days. A 

decrease in testicular 17-betahydroxysteroid dehydrogenase activity was obsed at lo00 and 

2000 mgkg/day indicative of pible decreased steroidogenesis in treated animals (Srivastava 

and Srivastava, 1991). The monoester metabolite accumulates in the testes and has been 

shown in vitro to inhiiit testicular mitochondrial respiration (pihi, 1990). 

8

3.15. Reference Doce 


ORAL RfD,: 

UNCERTAINTY FACI'OR: 

Lorn 

0.02 mg/kg/day (U.S. EPA, 1992a) 

lo00 

19 mg/kg/day 

PRINCIPAL STUDIES: The same studies and comments apply to both the 

subchronic and chronic RfD derivations. See section 3.132. 

3.15.2 chronic 

ORAL RfD,: 

UNCERTAINTY FACI'OR: 

MODIFYING FACTOR: 

LOAEL: 

CONFIDENCE. 

Study: 

Data Base: 

RfD: 

VERIFICATION DATE: 

PRrNmALsmY 

0.02 mg/kg/day (U.S. EPA, 1992b) 

lo00 

1 

19 mg/kg/day 

Medium 

Medium 

Medium 

05120/8!5 

Carpenter et al. (1953). 

cOMMEN?s: The LOAEL was calculated from a 12 month experiment in which 

guinea pigs were given 0, 19, or 64 mg di(2ethylhayl)phthalate/kg body weight in the 

diet. The LOAEL of 19 mg/kg was based on increased relative liver weight. See 

section 3.13.2 

32 INHALATTON- 

3.21.1. Human 

Information on the acute inhalation toxicity of bis(2-ethylhexyl)phthalate in humans 


321.2 Animal 

Rats could survive a two hour exposure to a vapor mist created by bubbling air 

through heated (170°C) bh(Z-ethylhexyl)phthalate, but did after a four hour exposure 

(Sandmeyer and Kiwin, 1978). 

9

3221. Human 

A total of 101 workers in a bk(2-ethylhexy1)phthalate production plant were examined 

for adverse effects due to phthalate ester exposure. The air concentration of bis(2- 

ethylhexy1)phthalate ranged from 0.01 to 0.16 mg/m3, and the exposure was from four months 

to 35 years. Some of the chemical was found in the blood and urine of both the control and 

exposed groups, however, no compound-related effects were reported (Thiess et al., 1978). 

3222 Animal 

Information on subchronic inhalation toxicity of bis(2-ethylhexyl)phthalate in animals 


323.1. Human 

No compound related effects were observed in a study of 101 workers in a bis(2- 

ethylhexy1)phthalate production plant exposed to 0.01 to 0.16 mg/m3 for up to 35 years 

(average 12 years, see section 3.2.21) (Thiess et aL, 1978). 

Other studies have been conducted on populations chronically exposed to mixtures 

of phthalic acid esters containing blr(2ethylhexyl)phthalate; therefore, the observed effects 

may or may not be caused by the bis(2-ethylh 1)phthalate. Ambient air concentrations of 

total phthalate esters ranged from 1 to 40 mg/m OT in one study (Mill;ov et aL, lm), and from 

324.2 Animal 

Information on developmental and reproductive toxicity in animals resulting from 

inhalation exposure to bis(2ethylhexyl)phthalate was not available. 

3-3. Referenceconctntration 

3-3.1. Sthchronic 

A subchronic Reference Concentration is not available at this time. 

3252 chronic 

A chronic Reference Concentration is not available at this time. 

33. CYIRER ROUTES OF EXPOSURE 

33.1. hteTdty 

33.1.1. Human 

Bis(2ethylhexyl)phthalate is mildly irritating to the skin and irritating to the eyes and 

mucous membranes on contact (Sittig, 1985; Sax and Lewis, 1989). Humans are also 

susceptible to introduction of bir(2ethylhexyl)phthalate by intravenous route since this 

substance is known to leach from blood containers and other PVC plastic medical equipment. 

However, no reports descn'bng acute adverse effects as a result of this route of exposure arc 

available. 

33.12. Animal 

Bk(2ethylhexyI)phthalate can be absorbed through the skin and LD, values of 25 

and 10 g/kg have been listed for rabbits and guinea pigs, respectively. A dose of 500 m@4 

hours is mildly imtating to the skin and eyes of rabbits (Sax and Lewis, 1989). 

3321. Human 

Idormation on the subchronic toxicity of bk(2-ethylhexyl)phthalate by other routes 

of exposure in humans was unavailable. 

3322 Animal 

Information on the subchronic toxicity of bis(2+thyIheqI)phthalate by other routes 

of exposure in animals was unavailable. 

. 

11

333. ChukTcxicity 

333.1. Human 

Humans needing chronic transfusions of blood are susceptible to the introduction of 

bis(2-ethylhexyl)phthalate by intravenous route since this substance is known to leach from 

blood containers and other PVC plastic medical equipment (Sittig, 1985). The diester leached 

from the plastic can be metabolized to the monoester by blood enzymes. The monoester has 

been shown to inhibit platelet phospholipase A2 possibly resulting in reduced platelet 

function (Labow et ai., 1988). Long term hemodialysis patients often develop renal cysts 

similar to that reported for rats chronically exposed to bir(2ethylhexyl)phthalate, however, 

a causal relationship has not been shown with leached plasticizer (Woodward, 1990). No 

reports specifically describing adverse effects as a result of this route of exposure were 

located. 

3332 Animal 

Information on the chronic toxicity of bis(2-ethylhexyl)phthalate by other routes of 

exposure in animals was unavailable. 

33.4. Dmdopmental and Reproductive Toxicity 


Information on the developmental aad reproductive dCity of bk(2- 

ethylhexy1)phthalate by other routes of exposure in humans was unavailable. 

33.42 Animal 

Male and female mice were given subcutaneous injections of 1 to 100 ml bis(2- 

ethyheq4)phthaIate/kg on days 1,5, and 10 and evaluated on day 21 of the experiment for 

reproductive performance, biochemical parameters of the gonads and histological alterations. 

Decreased numbers of pregnancies were reported when either sex of treated mice were mated 

with untreated mice. Decreased testicular weight but not ovarian weight was reported. 

Histological damage and increased lysosomal activity was seen in both sexes. Decreased 

fertility was the most sensitive indicator for gonadotoxicity (Agarwal et aL, 1989). 

In addition to the monoester derivative of bis(2ethylhexyl)phthalate, another principal 

metabolite, 2etbylhexanoic acid, exists in two enantiomeric forms, The S enantiomer was 

found to not be embryotoxic or teratogenic. However, intraperitoneal injection of pregnant 

rats with 500 m ag twice daiiy on day 7 and 8 of gestation with the R enantiomer caused 

decreased fetal sunrival, decreased weight of surviving fetuses, and neural tube defects in 59% 

of living fetuses (Hauck et al, 1990). 

. 

12

3.4. TARGET ORGANWCRITICAL EFFECIS 

3.4.1. Oral powr re^ 

3.4.1.1. Primary Target Organ(s) 

1. Liver: Increased liver weight was observed in animals following oral treatment with 

bis(2ethylhexyl)phthalate. 

2. Kidney: Increased kidney weight was observed in animals following oral treatment 

with bir(2ethylhexyl)phthalate. 

3.4.1.2 Other Target Org8n(s) 

1. Fetus: l3posure to bis(2ethylhexyl)phthalate during gestation has resulted in 

increased fetal mortality and malformations in rats and mice, 

2 Testis: Treatment with bis(2ethylhexyl)phthalate has resulted in decreased 

testicular weight and degeneration of the seminiferous tubules in rats and mice. 

3. Blood. Decreased hemoglobin and packed cell volume was observed in rats 

exposed to bir(2ethylhexyl)phthalate. 

3.421. Primarp Target Organ@) 

1. Blood: Decreased hemoglobin and blood cell counts were observed in humans 

exposed to a mixture of phthalate esters containing bir(2ethylhexyI)phthalat.e. 

2 Nervous system: A polyneuritis and mild to moderate sensory-motor and motor 

polyneuropathy were observed in humans exposed to a mixture of phthalate eSteIs 

containing bis(2ethylhexyl)phthalate. 

3.4a Other Tar@ Organ(s) 

1. Liver: The effects on liver are likely to be independent of route of exposutc 

2 Kidnqr: The effects on kidney are likely to be independent of route of exposure. 

13

4.1. ORAL- 


Information on the oral carcinogenicity of bis(2ethylhexyl)phthalate in humans was 

unavailable. 


Groups of 50 male and 50 female FEher 344 rats were g kn 0,6oOo, or 12OOO ppm 

bk(2-ethyhexyl)phthalat.e in their diet for 103 weeks. Groups of 50 male and 50 female 

B6C3F1 mice were given 0,3000, or 6OOO ppm of the chemical in their diets for 103 weeb. 

All animals were examined when moribund or after 105 weeb from the beginning of 

treatment. No clinical signs of toxicity were obsed in any of the animals. Female rats, and 

male and female mice demonstrated a statistically significant dosedependent increased 

incidence of hepatocellular carcinomas and combined carcinomas and adenomas. A signjficant 

increase in the combined incidence of neoplastic nodules and hepatocellular carcinomas was 

seen in the highdose male rats (NTP, 1982, Kluwe, et at, 1982). 

Combined neoplastic nodules and hepatocellular carcinomas ranging from 0 to 4 per 

liver were reported in 11 of 14 F-344 rats on a diet containing 2% bif(2ethylhexyl)phthalat.e 

for 108 weeks (Rao et al, 1990). 

Bk(2ethyhexyl)phthalate is known to induce the production of peroxisOmes and the 

proliferation of pcroldsomes has been linked with carcinogenesis (Rao and Reddy, 1991) (See 

also section 3.13.2). 

42 INHALATIONEXPOSURES 

421. Human 

Information on the inhalation carcinogenicity of bir(2ethylhexyl)phthalate in humans 


422 Animal 

Information on the inhalation carcinogenicity of bis(2-ethylhexyl)phthalate in animals 


43. OTHER ROUTES OF ExpomTRE 

Information on the carcinogenicity of bir(2ethylhexyl)phthalate in animals or humans 

with other routes of expure was unavailable. 

14


4.4.1. oral 

CLASSIFICATION Group B2 - Probable Human Carcinogen (US. EPA, 1987% 

1987b, 1991% 1991b). 

BASIS: Based on an increased incidence of hepatocellular carcinomas and adenomas 

in both rats and mice treated with bir(2ethylhexyl)phthalate in the diet (NTP, 1982, 

Kluwe, et al., 1982). 

4.42 Inhnlatinn 

CLASSIFICATION Group B2 - Probable Human Carcinogen (U.S. EPA, 1987% 

1% 1992b). 

BASIS: Based on an increased incidence of hepatocellular carcinomas and adenomas 

in both rats and mice treated with bir(2ethylhexyl)phthalate in the diet (NTP, 1982, 

Kluwe, et aL, 1982). 

45. CARCINOGENICITY.sIxlPE FACIO= 

45.1. Oral 

SLOPE FACTOR 

1992b) 

DRINKING WATER UMT RISE 

I=) 


PRINCIPAL STUDY. 

1.4E-2 (mg/kg/day)" (US. EPA, 1% 

4.OE-7 (pg/L)-' (US. EPA, 19% 

mom 

NTP (1982); muwe, et ai. (1982). 

COMMENTS Based on incidence of hepatocellular carcinomas and adenomas in 

male mice exposed orally to bir(2ethylhexyl)phthalate. Both listed references discuss 

the same data set. 

Quantitative estimation of carcinogenic risk from inhalation exposure is not 

available (U.S. EPA, 1992b) 

15

5. REFERENCES 

Agaxwal, D.K, W.H. Lawrence, J.E. Turner and J. Autian 1989. Effects of parenteral di(2- 

ethylhexy1)phthalate (DEHP) on gonadal biochemistry, pathology, and reproductive 

performance of mice. J. Toxicol Environ. Health. 2f5( 1): 39-59. 

Albro, P.W., RE Chapin, J.T. Corbett, J. Schroeder and J.LPhe1p. 1989. Mono-2- 

ethylhexyl phthalate, a metabolite of di(Zethylhexyl)phthalate, causally linked to testicular 

atrophy in rats. Toxic01 Appl. Pharmacol. loO(2): 193-200. 

Albro, P.W., J.T. Corbett, J.L Schroeder, S. Jordan and H. B. Matthews. 1982 

Pharmacokinetics, interactions with macromolecules and species differences in metabolism of 

DEHP. Environ. Health Penpect. 4519-25. 

Autian, J. 1973. Toxicity and health threats of phthalate esters: Review of the literature. 

Environ Health Perspect. 4 3-26. 

Barron, M.G., LR Schultz and W.L Hayton. 1989. Presystemic branchial metabolism limits 

di(2ethylhexyl)phthalate accumulation in fsh. Toxic~l. Appl. Pharmacol. !%( 1): 49-57. 

Bell, F.P., M. Makowske, D. Schneider and CS. Patt. 1979. Inhibition of sterologentsis in 

brain and liver of fetal and suckling rats from dams fed di(2ethylhexyl)phthalate plasticizer. 

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with phthalate ester on rat Iiver. Pharmacol ToxicoL 67(5): 392-401. 

16

Gilioli, R, C Bulgheroni, T. Terrano, G. Filippini, G. Massetto and R Boeri. 1978. Studio 

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dietary di(2ethylhcxyl)phthalate (DEHP) in Faher 344 rats and B6C3Fl mice. J. ToxiwL 

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Labow, RS., E Meek, GA Adam and G. Rock. 1988. Inhibition of human platelet 

phospholipase A2 by mono(2-ethylhexyl)phthalate. Environ. Health. Perspect. 78 179-183. 

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dioctyl phthalate @OP) in male rats and mice. Nara Igaku Zasshi 25(6): 649-654 (cited in 

U.S. EPA, 1987b). 

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Oishi S. 1990. mats of phthalic acid esters on testicular mitochondrial functions in the rat. 

Arch ToxicoL 64(2): 143-147. 

17

Oishi, S and Hiraga. 1982. Distribution and elimination of di-2ethylhexyl phthalate and 

mono-2ethylhexyl phthalate after a single oral administration of di-2ethylhexyl phthalate in 

rats. Arch. Toximl. 51(2):149-156. 

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administration and repetitive dosing on the disposition kinetics of di(2ethylhql)phthalate 

and its mono deesterified metabolite in rats. Toxicol. AppL Pharmaool. 79(2): 246-256. 

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85-89. 

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18

Shiota, K. and S. Mima. 1985. Assessment of the teratogenicity of-di(2-ethylhexyl)phthalate 

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119. 

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1987a). 

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and AuLyuAryl Esters, Prepared by the Office of Health and Environmental Assessment, 

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and Emergency Response, Washington, DC 

19

U.S. EPA. 1% Health Effects Assessment Summary Tables, Prepared by the Office of 

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37 1-378. 

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diethylhexyl phthalate (CAS No. 117-81-7) in Fischer 344 rats. Gov. Rep. Announce. Index 

85(2): 70 (cited in U.S. EPA, 1987b). 

Wokowski-Tyl, R, C Jones-Price, M.C. Marr and C.A. Kimmel. 1984b. Teratologic 

evaluation of diethylhexyl phthalate (CAS No. 117-81-7) in CD-1 mice. Gov. Rep. Announce. 

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Woodward, K. N. 1990. Phthalate esters, cystic kidney disease in animals and possible effects 

on human health: a review. Human and Exp. ToxiwL 9(6): 397401. 

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of di- and mono-(2ethylhexyl)phthalate in mice. J. Emriron. PathoL Toxiwl. 4(2-3): 533-544 

(cited in us. EPh lm). 

20

ToxIclTy SUMMARY FOR 

CADMTUM 

November 1991 

Prepared by: 

Robert k Young, Ph.D., D.AB.T. 





Prepared for: 



*Managed by Martin Marietta Energy Systems, Inc, for the U.S. Department of 

Energy under Contract No. DE-AC05-840R21400

7Xs page inremhmliy left blank

ExEcuTlVESuMMARY 

Cadmium is a naturally occurring metal that is used in various chemical forms in 

metallurgical and other industrial 

and in the production of pigments. 

Environmental exposure can occur via the diet and drinking water (ATSDR, 1989). 

Cadmium is absorbed more efficiently by the lungs (30 to 60%) than by the 

gastrointestinal tract, the latter being a saturable p'ocess (Nordberg et al., 1985). Cadmium 

is transported in the blood and widely distributed in the body but accumulates primarily in the 

liver and kidneys (Goyer, 1991). Cadmium burden (especially in the kidneys and liver) tends 

to increase in a linear fashion up to about 50 or 60 years of age after which the body burdem 

remains somewhat constant. Metabolic transformations of cadmium are limited to its binding 

to protein and nonprotein sulfhydryl groups, and various macromolecules, such as 

metallothionein, which is especially important in the kidneys and liver (ATSDR, 1989). 

Cadmium is excreted primarily in the urine. 

Acute oral exposure to 20-30 g have caused fatalities in humans. Exposure to lower 

amounts may cause gastrointestinal irritation, vomiting, abdominal pain, and diarrhea 

'(ATSDR, 1989). An asymptomatic period of one-half to one hour may precede the onset of 

clinical signs. Oral LDm values in animals range from 63 to 1125 m@g, depending on the 

cadmium compound (USAF, 1990). Longer term exposure to cadmium primarily affects the 

kidneys, resulting in tubular proteinosis although other conditions such as "itai-ita? disease 

may involve the skeletal system. Cadmium involvement in hypertension is not fully 

understood (Goyer, 1991). 

Inhalation exposure to cadmium and cadmium compounds may result in effects 

including headache, chest pains, muscular weakness, pulmonary edema, and death (USAF, 

1990). The l-minute and 10-minute lethal concentration of cadmium for humans has been 

estimated to be about 2,5500 and 250 mg/m3, respectively (Barrett et al., 1947; Beton et aL, 

1966). An &hour TWA (time-weighted-average) exposure level of 5 mg/m3 has been 

estimated for lethal effects of inhalation exposure to cadmium. and exposure to 1 mg/m3 is 

considered to be immediately dangerous to human health (Friberg, 1950). Renal toxicity 

(tubular proteinosis) may also result from inhalation exposure to cadmium (Goyer, 1991). 

Chronic oral RfDs of SE-4 and 1E-3 mg/kg/day have been established for cadmium 

e;xposure via drinking water and food, respectively (U.S. EPA, 1991). Both values reflect 

incorporation of an uncertainty factor of 10. The RfDs are based on an extensive data base 

regarding toxicokinetics and toxicity in both human and animals. the critical effect being renal 

tubular proteinuria Confidence in the RfD and data base is high. 

Inhalation RfC values are currently not available. 

The target organ for cadmium toxicity via oral exposure is the kidney (Goyer, 1991). 

For inhalation exposure, both the lungs and kidneys are target organs for cadmiwn-induced 

toxicity (ATSDR, 1989; Goyer, 1991). 

1

There is limited evidence from epidemiologic studies for cadmium-related respiratory 

tract cancer (ATSDR, 1989). An inhalation unit risk of 1.8E-3 ( pg/m3)" and an inhalation 

slope factor of 6.1E+O (mg/kg/day)-' are based on respiratory tract cancer associated with 

occupational exposure (U.S. EPA, 1985). Based on limited evidence from multiple 

occupational exposure studies and adequate animal data, cadmium is placed in weight-ofevidence 

group B1 - probable human carcinogen. 

2

1. PJTRODUCIlON 

Cadmium (Cd) is a naturally occurring metallic element that is used for electroplating 

and galvanization processes, in the production of pigments, in batteries, as a chemical reagent, 

and in miscellaneous industrial processes (A'ISDR, 1989). Cadmium compounds have varying 

degrees of solubility ranging from very soluble to nearly insoluble. The solubility affects their 

absorption and toxicity. Exposure to cadmium and cadmium compounds may occur in both 

occupational and environmental settings, the latter primarily via the diet and drinking water 

(ATSDR, 1989). 


Cadmium is more efficiently absorbed from the lungs than from the gastrointestinal 

tract (ATSDR, 1989). The absorption efficiency is a function of solubility of the specific 

cadmium compound as well as its exposure concentration and route. 

Inhalation absorption usually involves cadmium in a particulate matter form with 

absorption being a function of deposition, which in turn is dependent upon the particle size 

(particles z 1Opm diameter tend to be deposited in the upper airways and particles s 0.1 Vm 

diameter are deposited in the alveolar region). Alveolar deposition efficiency in animal 

models ranges from 5 to 20% (Barrett et aL, 1947; Boisset et aL, 1978). Based on 

physiological modeling, cadmium deposition in the alveolar region of humans was estimated 

to be up to 50% for small particles (Nordberg et aL 1985). Actual cadmium absorption via 

inhalation exposure has been estimated to be 30 to 60% in humans (Fnirg et aL, 197% 

Elinder et aL, 1976). - 

Absorption of cadmium from the gastrointestinal tract appears to be a saturable 

process with the fraction absorbed decreasing at high doses (Nordberg et al., 1985). It is also 

important to distinguish true absorption from simple retention of cadmium in the rnkrodi 

of the small intestine (Foulkes et al., 1986). Shaikb and Smith (1980) reported a mean 

retention of 28% (1.1 to 7.0% range) for 12 human subjects given a single oral dost of 

radiolabeled cadmium chloride, and McLellan et aL (1978) reported 5.9% retention of 

cadmium chloride by 14 human subjects. 

Also of importance relative to cadmium absorption is that its absorption may be 

decreased by divalent and trivalent cations (Zn", Mg+2, CP3), and increased by iron and 

calcium deficiencies (Flanagan et al., 1978; Foulkes et al., 1986, Goyer, 1991). Dermal 

absorption is relatively unimportant (ATSDR, 1989). 

22 DISITUBUTION 

Cadmium is transported in the blood by red blood cells and high-molecular-weight 

proteins such as albumin (Goyer, 1991). Normal blood cadmium levels in adults arc < 

3

lpg/dL Although cadmium is widely distributed throughout the body, most (50 to 70% of 

the body burden) accumulates in the kidneys and liver (Goyer, 1991). Cadmium burden, 

especially in the kidneys, tends to increase in a linear fashion with age up to about 50 or 60 

years of age after which the kidney levels remain somewhat constant or slightly decline 

(Goyer, 1991). There is evidence that the placenta is a partial barrier to cadmium, and that 

the fetus is exposed to only small amounts of maternal cadmium (ATSDR 1989). 

As with most metallic elements, there is little or no direct metabolic conversions of 

cadmium, but rather binding to various biological components, such as protein and nonprotein 

sulfhydryl groups and anionic groups of various macromolecules (ATSDR 1989). Of special 

importance, is the binding protein, metallothionein which is very effective in binding cadmium 

and some other metals and is instrumental in determining the disposition of cadmium in the 

body (e-g. concentration of cadmium in the kidneys). 

24. EXCXZEI'ION 

The principal route of excretion is via the urine. with average daily excretion for 

humans being about 2 to 3 pg (ATSDR, 1989). Daily excretion represents on@ a small 

percentage of the total body burden, which accounts for the 17 to >30 years half-life of 

cadmium in the body (Tsuchiya et aL, 1972, Friirg et aL, 1974). Unabsorbed cadmium is 

removed from the gastrointestinal tract by fecal excretion. Typical daily cadmium excretion 

has been reported to be about 0.01% of the total body burden (ATSDR, 1989). There is 

some evidence for biliary excretion of cadmium (Klaassen et aL, 1978). 




3.1.1.1. Human 

Doses of 1,500 to 8,900 mg (20 to 30 mg/kg) of cadmium have resulted in human 

fatalities, but generally, fatal poisoning from cadmium is rare (ATSDR, 1989). High doses 

of cadmium are known to cause gastrointestinal irritation resulting in vomiting, abdominal 

pain, and diarrhea (A'ISDR, 1989). Lauwerys (1979) reported that the emetic threshold for 

cadmium in drinking water was about 15 mg/L and CEC (1978) reported that 3 mg was an 

emetic threshold. 

Following ingestion of cadmium, an asymptomatic period of 0.5 to 1.0 hour may 

precede the onset of clinical signs. Depending on the severity of exposurer clinical signs of 

cadmium poisoning following acute exposure include: nausea, vomiting, abdominal cramps, 

headache, muscle cramps, exhaustion, shock, and death (USAF, 1990). 

4-


Oral LDM values for animals range from 225 to 890 mag for elemental cadmium, 

63 to 88 mag for cadmium chloride, 72 mg/kg for cadmium oxide, and 590 to 1125 mgkg 

for cadmium stearate (USAF, 1990). 


3.121. Human 

Because the toxic effects of cadmium are a function of a critical concentration being 

attained in a target organ, similar effects will occur following long-term exposure to low 

cadmium levels and 

short-term exposure to high concentrations (Wang and Foulkes, 1984). Consequently, renal 

and hepatic toxicity may occur if toxic cadmium levels are attained in these organs even 

during subchronic exposure, A description of cadmium-induced toxicity foilowing oral 

exposure is presented in Section 3.1.3. Generally, cadmium is not as toxic via oral routes as 

via inhalation. 

3.1.22 Animal 

Exposure of rabbits to 1.5 mol cadmium chloride in drinking water (equivalent to 

13 pg/kg/day) produced histological alterations in the liver but no clinical signs of toxicity 

(Stowe et aL, 1972). In a study by Kotsonis and Klaassen (1978), rats exhibited proteinuria 

after receiving cadmium chloride in the drinking water for six weeks at 30 or 100 mg/L 

(equivalent to 3.1 and 8.0 mg Wkg/day). 

Although the effects of cadmium on the immune system of humans is unclear, 

evidence for cadmium-induced immunotoxicity in animals is available. Koller et aL (1979 

noted a decrease in the number of spleen plaque-forming cells in mice receiving cadmium 

at 0.6 mg/kg/day for 10 weeks, and Blakley (1985) reported a dosedependent suppression of 

the humoral immune system in mice receiving cadmium in drinking water at concentrations 

of 5 to 50 mg/L for three weeks. These immune system effects occurred at kidney tissue 

concentrations (0.3 to 6.0 pg/g) lower than those associated with renal toxicity. 

3.13. ChronicToxicity 

3.13.1. Humans 

The most serious chronic effect of oral exposure to cadmium is renal toxicity. This 

critical effect is characterized by tubular proteinuria resulting from renal tubular dysfunction. 

Friirg et at (1974) estimated that this critical effect will not occur in humans until the 

cadmium concentration in the renal cortex exceeds 200 pg/g. 

Dietary intake of cadmium has also been implicated in osteomalacia, wteoporosis and 

spontaneous fractures, conditions collectively termed "itai-itai" (ouch-ouch) disease and 

5

originally documented in postmenopausal women in cadmiumcontaminated areas of Japan 

(Friberg et al., 1974). 

Cadmium exposure has also been implicated in hypertensive disorders, a situation that 

is currently not thoroughly understood or verified (ATSDR, 1989). 

3.13.1. Animals 

Rats given cadmium chloride in the drinking water at a concentration of 10 mg/L (1.2 

mg Cd/kg/day) exhibited no renal effects even after 24 months, although higher exposure 

levels induced proteinuria after six weeks exposure (Kotsonis and Klaassen, 1978). 

3.1.4. Developmental and Repducthe Tdty 


Developmental and reproductive toxicity in humans have not been demonstrated for 

oral exposure to cadmium (A'ISDR. 1989). 

3-1.4.1. Animal 

Developmental toxicity data for cadmium administered orally to rats are equivocal. 

Pond and Walker (1975) reported few, if any effects, for rats exposed to cadmium chloride 

in the drinking water (15 rngkglday) during gestation. Baranski et al. (1985) reported 

teratogenic effects (fused or absent legs) in rats following gavage administration of cadmium 

chloride (40 mg/kg/day) during gestation. Neurological effects in rat pups were detected 

following gestational exposure to 0.4 or 4 mg Wkg (Baranski et aL, 1986). 

3.15. ReEereMz h 


ORAL, RfD,: 

UNCERTAINTY FACTOR: 

NOAEL 

Not available 

Not available 

Not available 

3.152 Chronic 

ORAL IUD,: 

UNCERTAIN'WFACTOR: 

MODIFYING FACTOR: 

NOAEL: 

mm 

CONFIDENCE: 

study 

5E-4 mg/ltg/day (water) (U.S. EPA, 1991) 

1E-3 mg/kg/day (food) 

10 (for both food and water) 

1 (for both food and water) 

0.005 mglkglday (water) 

0.01 mg/kg/day (food) 

Not available 

Not applicable 

6

Data base 

RfD 

High 

High 


PRINCIPAL STUDYThe data supporting the IUD have been derived from 

many animal and human studies that have provided information on cadmium toxicity 

(renal toxicity using proteinuria as the critical effect) and the calculation of 

pharmacokinetic parameters regarding calcium absorption, distribution and excretion. 

COMMENTS: Due to background cadmium in the diet, no subchronic RfD 

was calculated. 

32 IIWALA'IIONEXPOSURES 

3.21. AcuteToxiCity 

321.1. Human 

Inhalation of cadmium fumes or dust may result in a wide range of effects, including 

a metallic taste, headache, dyspnea, chest pains, cough with foamy or bloody sputum, and 

muscularwcakness. Severe exposure may result in pulmonaxy edema and death (USAF, 1990). 

If the pulmonary edema is resolved, late-occurring kidney and/or liver damage may develop. 

Peculiar to inhalation exposure to cadmium is an asymptomatic period that may precede 

clinical illness by four to eight hours (USAF, 1990). 

Based on cadmium lung burdens measured during postmortem examinations, Bamtt 

et aL (1947) estimated a 1-minute lethal concentration of 2,500 mum3. Beton et aL (1% 

conducted similar calculations and reported a 10-minute lethal concentration of 250 mghn 1 . 

This value was further extrapolated to an &hour lethal concentration of 5 mg/m3. F n i et 

aL (1974) indicated that exposure to 1 mg Wm3 for 8 hours is "immediately dangerous to 

humans" and the World Health Organization (WHO, 1980) identified 05 mg Wm3 as the 

threshold for respiratory effects resulting from an &hour exposure. 

3212 Animal 

Acute toxicity values (10-min. LG) for inhalation exposure of animals (monkeys, rats, 

mice, guinea pigs, dogs) to cadmium oxide range from 340 mg/m3 to 15 g/m3 (USAF, 1990). 

3221. Human 

8 

Both pulmonary effects (emphysema, bronchiolitis, alveolitis) and renal effects 

(proteinuria) may occur following subchronic inhalation exposure to cadmium and cadmiumcompounds 

(A'ISDR, 1989). 

7'

33.22 Animal 

Pulmonary and renal toxicity have been documented for short-term inhalation 

exposure of animals to cadmium and cadmium compounds (USAF, 1990). Dosedependent 

fibrotic lesions were observed in rats exposed to cadmium chloride aerosol at 0.3 to 1.0 mg/m3, 

6 hourslday for 12 weeks, but at a concentration of 20 mg/m3 most rats died within 45 days 

(Kutzman et aL, 1986). Friirg (1950) reported emphysema in rabbits exposed to cadmium 

chloride at 5 mg/m3, 3 hourslday, 20 daydmonth for 8 months. 

3-3.1. Human 

Several occupational exposure studies have indicated that inhalation to cadmium dust 

and cadmium compounds may result in renal and pulmonary effects. 

Bonnell (1955) reported that occupational exposure to cadmium oxide (1 to 270 

&m3) resulted in proteinuria in 16% of the workers exposed for five years or more, and an 

increased incidence of emphysema in those exposed for more than 10 years. The latter group, 

however, may have received much higher initial exposures. Kidney lesions were also reported 

for the majority of workers exposed to the compound at a concentration of 20 pg/m3 for 27 

years (Materne et aL, 1975) and tubular proteinuria detected in workers exposed to cadmium 

dust (0.05 mg/m3) for 6 to 12 years (Kjellstrom et aL 1977). 

Based on occupational exposure studies, an &hour TWA (time-weighted-average) 

concentration of 0.02 mg/m3 was established for a 20-year exposure to cadmium (OSHA, 

1989), which is equivalent to continuous exposure to 0.007 mum3 over a lifetime (AIISDR, 

1989). 

Chronic inhalation exposure studies for animals have demonstrated the carcinogenic 

potential of cadmium chloride and are discussed in Section 4.22 

324. Developmental and Reproductive Toxicity 

324.1. Huuuun 

Definitive data were not available regarding the developmental or reproductive 

toxicity of cadmium or cadmium compounds in humans. 

3242 Animal 

Decreasedletal weight (with and without decreased maternal body weight) and minor 

neurobehavioral alterations in pups have been reported for rats exposed to cadmium oxide 

(0.16 mg/m3) or cadmium sulfate (about 3 mg/m3) during gestation (AlSDR, 1989). No other 

significant effects have been documented. 

8-

3-3. ReferenceC~ncentration 

The RfC for cadmium is currently under review (US. EPA, 1991). 

33. UI'HERROUTESOF'E)s9o5uRE 

33.1. AcuteToxiUty 

No data were available regarding the acute toxicity of cadmium by other routes of 

exposure. 

No data were available regarding the subchronic toxicity of cadmium by other routes 

of exposure. 

No data were! available regarding the chronic toxicity of cadmium by other routes of 

exposure. 

33.4. DeveIopmerdToxicity 

No data were available regarding the developmental toxicity of cadmium by other 

routes of exposure. 

3.4. TARGEI' ORGANWCRITICAL EFFECLS 

3.4.1.1. Primary Target@) 

1. Kidney: Renal tubular proteinuria is the primary toxic effect of long-term cadmium 

exposure. 

2 Gastrointestinal tract: Acute exposure to high levels of cadmium and cadmium 

compounds may cause irritation, vomiting, nausea, and diarrhea. 

3.4.1.2 Other Target@) 

The liver, bones, testes, and cardiovascular system have been shown to be affected to 

various de- by cadmium. 

9

3.421, Primary Target@) 

1. Kidney: Renal tubular proteinuria may result from chronic exposure to cadmium 

and cadmium compounds. 

2 Lung: Inhalation exposure to cadmium dust, fumes, aerosols, and some cadmium 

compounds causes irritation of the respiratory tract, emphysema, and death for acute 

exposure to high cadmium concentrations. 

3.4.22 Other Target@) 

No data were available indicating additional target organs/tissues for inhalation 

exposure to cadmium and cadmium compounds. 

4.1. ORAL ExPOSURE 


Limited epidemiologic studies have indicated that exposure to cadmium in food or 

drinking water is not carcinogenic (Bernard and Lauwerys, 1986). 

4.1.2. Animal 

Chronic exposure studies using animals exposed to cadmium in the diet or drinking 

water, have all provided negative results (ATSDR, 1989). 

42 INHALATION EXPOSURE 

421. Human 

Limited evidence is available from epidemiologic studies indicating that inhalation 

exposure to cadmium may be associated with an i n d incidence of resphtory tract 

cancer (ATSDR, 1989). An exposure-related increase in mortality due to lung cancer in 

workers with cumulative exposures of 585 to >2,920 mg Wm3 (equivalent to TWA daily 

exposures of 168 to 2,522 pg/ Cd/m3) was reported by Thun et aL (1985). 

Limited evidence is available showing that inhalation exposure to cadmium dust and 

fumes may be &iated with prostate cancer, but the total number of cases in the various 

studies is small (ATSDR, 1989). 

A unit risk of 1.8 x lo3 ( pg/m3)" based on an increase in respiratory tract tumors in 

cadmium smelter workers was calculated by the U.S. EPA (1985). 

10

Chronic exposure of rats to cadmium chloride aerosols (125, 25, or 50 (rg/m3) 

produced a dose-related increase in the frequency of primary lung carcinomas (Takenaka et 

aL, 1983). 

43. OTRER ROUTES OF ExposuRE 

No data were available regarding the carcinogenic potential of cadmium by other 

routes of exposure. 

4.4. EPA WEXGHT-0F-EVI.D~~ CLASSIFICATION 


Not assigned. 

4.42 Inhalation 

Classification-B1: Probable human carcinogen 

Basis - Limited evidence from multiple occupational exposure studies showing an 

association between cadmium exposure and increased incidence of lung cancer. 

Adequate data are available showing a carcinogenic response to cadmium by rats and 

mice following inhalation exposure and parenteral administration. 

45. CARCINOGENICITY SLDPE FACIORS 

45.1. Oral 

Not assigned. 


SLOPE FACTOR 


(U.S. EPA, 1985; 1991) 

6.1 (mg/kg/day)-' 

ll/l2/Ss 

COMMENT: The inhalation unit risk is based on occupational exposure of humans 

to cadmium fumes (Thun et al, 1985). 

11

5. REFERENCES 

ATSDR (Agency for Toxic Substances and Disease Registry). 1989. Toxicological profile for 

cadmium. ATSDRKJS. Public Health Service, ATSDRKP-88/08. 

Baranski, B. 1985. Effect of exposure of pregnant rats to cadmium on prenatal and postnatal 

development of the young. J. Hyg. Epidemiol. MicrobioL Immunol. 29253-262. (Cited in 

A'ISDR, 1989) 

Baranski, B. 1986. E€€& of maternal cadmium exposure on postnatal development and tissue 

cadmium, copper, and zinc concentrations in rats. Arch. ToxicoL 58Z5-260. (Cited in 

ATSDR, 1989) 

Barrett, EM., DA 

Invin and E Semmons. 1947. Studies on the toxicity of inhaled cadmium. 

I. The acute toxicity of cadmium oxide by inhalation. J. Ing. Hyg. Toxicol. 29279. (Cited in 

ATSDR, 1989) 

Bernard, k and R. Lauwerys. 1986. Cadmium in human populations. Experimentia 4&143- 

152 (Cited in A'ISDR 1989) 

Beton, D.C, G.S. Andrew, H. J. Davies, L Howelss and G.F. Smith. 1966. Acute cadmium 

fume poisoning Frve cases with one death from renal necrosis. Br. J. Ind Med. 23292. 


Blakley, B.R 1985. The effects of cadmium chloride on the immune response in mice. Can. 

J. amp. Med. 49%)4-108 (Cited in A'ISDR, 1989) 

Boisset, U, E Girard, J. Godin and C. Boudene. 1978. Cadmium content of lung, liver, and 

kidney in rats exposed to cadmium oxide fumes. Int. Arch. Occup. Environ. Health 41:41-53. 


Bonneil, J.A 1955. Emphysema and proteinuria in men casting copper-cadmium alloys. Br. 

J. Ind Med. 12181-197. (Cited in ATSDR 1989) 

CEC (Commission of the European Communities). 1978. Criteria (ddeffect relationships) 

for cadmium. Pergamon Press, Oxford. pp. 1-1% 

Elinder, CG., T. Kjellstmn, L Friirg, B. Lind and L Linman. 1976. Cadmium in kidney 

cortex, liver, and pancreas for Swedish autopsies. Arch. Environ. Health 31292-302. 

Flanagan, P.R, J. Mckllan, J. Haist, M.G. Cherian, MJ. Chamberlain and LS. Valbar. 

1978. Increased dietary cadmium absorption in mice and human subjects with iron deficiency. 

Gastroenterology 72M1-846. 

Foulkes, EC. 1986. Absorption of cadmium. In: Foulkes, EC, ed. Handbook of 

Experimental Pharmacology. Vol. SO, Springer-Verlag, Berlin, pp. 75-100. (Cited in ATSDR 

1989) 

12

Friirg, L. 1950. Health hazards in the manufacture of alkaline accumulators with special 

reference to chronic cadmium poisoning. Acta Med. Scad. (Suppl24O) 1381-124. (Cited in 

ATSDR, 1989) 

Friirg, I,., M. Piscator, G.F. Nordberg and T. Kjellstrom. 1974. Cadmium in environment. 

2nd. Ed. CRC Press, Boca Raton, FL 

Goyer. R 1991. Toxic effects of metals. In: Amdur, M.O., J.D. Doull and C.D. Klaassen, 

Eds. Casarett and Doull's Toximlogy. 4th ed Pergamon Press, New York. pp.623-680. 

Klaassen, C. D. 1978. Effect of metallothionein on hepatic disposition of metals. Am. J. 

PhysioL 234:E47-E53. (Cited in ATSDR, 1989) 

Kjellstrom, T., P.E Evrin and B. Rahnster. 1977. Dose-response analysis of cadmium-induced 

tubular proteinuria A study of urinary Brmicroglobulin excretion among workers in a battery 

factory. Environ. Res 13303-317. (Cited in ATSDR, 1989) 

Koller, LD., J. H. Exon and J.G. Roan. 1975. Antibody suppression by cadmium. Arch. 

Environ. Health 3098. (Cited in ATSDR 1989) 

Kotsonis, F. N. and C. D. Klaassen. 1978. The relationship of metallothionein to the toxicity 

of cadmium after prolonged administration to rats. ToxicoL Appl. Pharmacol. 4639-54. 

Kutzman, RS., RT. Drew, RN. Shiotsuks and B. Y. CoCkreU 1986. Pulmonary changa 

resulting from subchronic exposure to cadmium chloride aerosoL J. Toxicol.Environ. Health 

17:175-189. (Cited in ATSDR, 1989) 

Lauwerys, R 1979. Cadmium in man. In: Webb, N. ed. %e chemistry, biochemistry, and 

biology of cadmium. Elscvier/North Holland Biomedical Press, pp. 433-453. (Cited in A mR, 

1989) 

Materne, D. R Lauwerys, J. P. Buchet, H. Roels, J. Brouwers and D. Stan- 1975. 

Investigations sur le risques resultant de I'exposition au cadmium dam deux enterprises de 

production et deux entreprises d'utilisation du cadmium. Cahiers de Medecine du Travail 

XII:l. 

McLellan, J.S. P. R Flanagan, M. J. Chamberlain and L S. Valberg. 1978. Measurement of 

dietary cadmium absorption in humans. J. ToxicoL Environ. Health 4131-138. (Cited in 

ATSDR, 1989) 

Nordberg, G. F., T. Kjellstrom and M. Nordberg. 1985. Kinetics and metabolism. In: Fnkrg, 

L, CG. Elinder, T.Kjellstrom and G.F. Nordberg, eds. Cadmium and Health A toxicological 

and epidemiological appraisal. VoL 1. Exposure, dose, and metabolism. CRC Press, Boca 

Ratori, FL.,pp. 103-178. (Cited in ATsDR, 1989) 

OSHA (Occupational Safety and Health Administration). 1989. Air contaminants: final rule. 

29CFR1910, Fed. Regist. 1/19/89,542332-2983, as corrected W.28054. 

13

Pond, W. G. and E. F.Walker. 1975. Effects of dietary Ca and Cd level of pregnant rats on 

reproduction and on dam and progeny tissue mineral concentrations. Proc. Sac. Exp. BioL 

Med. 148:655. (Cited in ATSDR, 1989) 

Shaikh, 2. A and J. C Smith. 1980. Metabolism of orally ingested cadmium in humans. In: 

Holmstead, B., et al., eds. Mechanisms of toxicity and hazard evaluation. Elsevier/North 

Holland, Amsterdam. pp. 569-574. (Cited in A'ISDR, 1989) 

Stowe, H. D., M. Wilsom and R A Gayer. 1972. Clinical and morphological effects of oral 

cadmium toxicity in rabbits. Arch. PathoL M389-405. 

Takenaka, S, H. Oldiges, H. Konig, D. Hochrainer and G. OberdOrster. 1983. 

Carcinogenicity of cadmium chloride aerosols in Wistar rats. J. NatL Cancer Inst. 70367-373. 

Thun, M. J., T. M. Schnorr, A Smith, W. E Halperin and R A Lemen. 1985. Mortality 

among a cohort of U.S. cadmium production workers - an update. J. NatL Cancer Inst. 

74:325-333. (Cited in ATSDR, 1989) 

Tsuchiya, IC, Y. Seki and M. Sugita 1972 Organ and tissue cadmium concentration of 

cadavers from accidental deaths. Proc. 17th Internat. Congress Occup. Health, Buenos Aires. 

(Cited in A'ISDR, 1989) 

USAF. 1990. Cadmium. In: Installation Restoration Program Toxicology Guide, VoL 5. Hany 

G. Armstrong Aerospace Medical Research Laboratory, Wright Patterson AFB, OH. 

U.S. EPA 1985. Integrated Risk Information System (IRIS). On-tine file, 03/31/87. 

U.S.EPA 1991. Health Ef€ezts Summary Tables, IT-1991 Annual. Off~ce of Research and 

Development, Office oflkergenq and Remedial Response, Washington, D.C OERR 

92OO.6-3O3(91-1). 

Wang, X P. and E C. Foulkes. 1984. Specificity of acute effects of cadmium on renal 

function. Toximlogy 30243-247. (Cited in ATSDR, 1989) 

WHO (World Health Organization). 1980. Recommended health-based limits in occupational 

exposure to heavy metals. Geneva. (Cited ATsDR, 1989) 

14


1,l-DICHLOROETHYLENE 


Prepared by 


Chemical Hazard Evaluation and Communication Program 

Biomdcal and Environmental Information Analysis Section 




Prepared for 



*Managed by Martin Marietta Energy Systems, Inc., for the U.S. Depariment of Energy under contract 

NO. DE-AC05-840R21400



1,l -Dichloroethylene (CAS No. 75-35-4), also known as 1 , 1 -dichloroethene and vinylidine chloride, 

is a colorless liquid that is used primarily in the production of polyvinylidine chloride (PVC) copolymers and 

as an intermebate for synthesis of organic chemicals. The major application for PVC copolymers is the 

production of flexible films for food packagmg such as Saran@ wrap (ATSDR, 1993). 

1,l-Dichloroethylene does not occuf naturally (IARC, 1986) but is found in the environment due to 

releases associated with its production and transport and with the production of its polymers. Because of its 

high volatility, releases to the atmosphere are the greatest source of ambient 1,l-dxhloroethylene. Smaller 

amounts are released to surface waters and soils (ATSDR, 1993). Loss of 1,l-dichloroethylene fiom water 

and soils is primarily due to volatilization. In the atmosphere, reaction with photochemically generated 

hydroxyl radicals is expected to be the predominant removal mechanism (EPA, 1987). Human exposure to 

1,l-dichloroethylene is potentially highest in workplace settings and in the vicinity of hazardous waste sites 

where the compound may contaminate environmental media (ATSDR, 1993). 

The primary effect of acute exposure to hgh concentrations (approximately 4000 ppm) of 

1,l-dichloroethylene vapor in humans is central nervous system (CNS) depression which may progress to 

unconsciousness (Gosselin et al., 1984). Occupational exposure has been reported to cause liver dyshction 

in workers (Tiemey et al., 1979). 1,l-Dichloroethylene is irritating when applied to the skin and prolonged 

contact can cause first degree burns (Tiemey et al., 1979). Direct contact with the eyes may cause 

conjunctivitis and transient corneal injury (IARC, 1986). 

In experimental animals, the liver and kidneys are target organs for the toxic effects of 1,ldichloroethylene. 

Subchronic oral exposure for 90 days to 1,l-dlchloroethylene in drinking water produced 

slight hepatotoxic effects at 200 ppm (Rampy et al., 1977), and chronic oral exposure to drinking water for 

2 years produced hepatocellular changes in males at 2100 ppm and in females at 250 ppm (Quast et al., 

1983). Gavage administration of 10 mg/kg/day, 5 daydweek for 2 years produced chronic inflammation of 

the kidney in male and female rats and liver necrosis in male and female mice (NTP, 1982). Exposure by 

inhalation to 55 ppm 1,l-dichloroethylene, 6 hourdday, 5 daydweek for up to 1 year produced fatty liver 

changes in rats and focal degeneration and necrosis in mice (Lee et al., 1977). 

In a three-generation study, no treatment-related effects on reproduction or neonatal development were 

seen in male and female Sprague-Dawley rats administered up to 200 ppm of 1,l-dichloroethylene in the 

drinking water (Nitschke et al., 1983). However, inhalation exposure during gestation produced increased 

resorptions and minor skeletal alterations in rodents at concentrations that caused maternal toxicity. These 

effects were reported in rats and mice at 2 15 ppm (Short et al., 1977a) and in rats and rabbits at 280 ppm and 

2 160 ppm, respectively (Murray et al., 1979). 

An oral Reference Dose (RfD) of 9E-3 mgkglday was derived for chronic exposure (EPA, 1994a) and 

subchronic exposure to 1,l-dichloroethylene @PA, 1994b), based on liver lesions seen in rats in a 2-year 

drinking water study (Quast et al., 1983). The oral RfD is currently under review and may be subject to 

change. An inhalation Reference Concentration (RE) for 1,l-dichloroethylene is under review (EPA, 

1994a). 

An epidemiology study using a small cohort found no association between the occurrence of cancer or 

cancer mortality and exposure to 1,l-dichloroethylene (Ott et al., 1976). Oral carcinogenicity bioassays 

(drinking water or gavage exposures) with experimental animals gave generally negative results (N’I”, 1982; 

... 

lll

Quast et al., 1983; Maltoni et al., 1984, 1985). In one inhalation study (Maltoni et al., 1985), statistically 

significant increases in renal adenocarcinomas were noted in male Swiss mice exposed to 25 ppm for 12 

months. Also observed were statistically significant increases in mammary gland carcinomas in females and 

lung tumors in both sexes. Results of other inhalation stuhes with rats, mice, and hamsters have been 

negative (Hong et al., 1981; Maltoni et al., 1984; Quast et al., 1986). 

Based on EPA guidelines, 1,ldichloroethylene was assigned to weight-of-evidence group C, possible 

human carcinogen. For oral exposure, the slope factor is 6E-1 (mgkg/day)’ and the unit risk is 1.7E-5 

(pa)-’ (EPA, 1994a). The mhalation slope factor and unit risk are 1.2EM (mgkbday) and 5.OE-5 

(pg/m’)’ (EPA, 1994a), respectively. 

iv


lY1-Dichloroethylene (CAS No. 75-35-4), also known as 1,l-dichloroethene and vinylidine chloride, 

is a colorless liquid with a molecular weight of 96.95 and a chemical formula of C,H,Cl,. It has a boiling 

point of 31.7"C, a melting point of -122.5"CY a density of 1.2129 g/mL (Budavari et al., 1989), and a vapor 

pressure of 600 mm Hg at 25°C (EPA, 1987). 1,l-Dichloro-ethylene is produced commercially by the 

dehydrochlorination of 1,1,2-trichloroethane by lime or sodium hydroxide (IARC, 1986). 

1,l-Dichloroethylene is used primarily in the production of poiyvinylidine chloride (PVC) copolymers 

and as an intermdate for synthesis of organic chemicals. The major application for PVC copolymers is the 

production of flexible films for food packaging such as Saran@ wrap (ATSDR, 1993). 1,l-Dichloroethylene 

is also used as an intermediate in the production of l,l,l-trichloroethane and in the manufacture of 

modacrylic fibers where it is combined with acrylonitrile. Because 1 , 1 -dichloroethylene polymerizes readily 

and can form explosive peroxides, hydroquinone monomethyl ether (MEHQ) or phenol are generally added 

as a stabilizer to prevent these reactions (Haley, 1975). 

1,l-Dichloroethylene does not occur naturally (IARC, 1986) but is found in the environment due to 

releases associated with its production and transport and with the production of its polymers. Because of its 

high volatility, releases to the atmosphere are the greatest source of ambient 1,l-dichloroethylene. Smaller 

amounts of 1,l-dichloroethylene are released to surface waters and soils (ATSDR, 1993). Estimated halflives 

in air and water are 2 days and 1-6 days, respectively. Loss of 1,l-dichloroethylene from water and soils 

is primarily due to volatilization. In the atmosphere, reaction with photochemically generated hydroq4 

radlcals is expected to be the predominant removal mechanism @PA, 1987). 

Human exposure to 1,l-dlchloroethylene is potentially highest in workplace settings and in the vicinity 

of hazardous waste sites where the compound may contaminate environmental media (ATSDR, 1993). It is 

found as a contaminant in nuclear submarines and spacecratl (Gosselin et al., 1984). The general population 

may be exposed to low levels of 1,l-dichloroethylene in ambient air, indoor air, contaminated drinking water, 

and food which has come in contact with plastic wrap containing residual monomer (HSDB, 1994). 



No human data were available regardmg the absorption of 1,l-dichloroethylene by any route of 

exposure. The rapid appearance of labeled 1,l-dichloroethylene in the urine and expired air of rats given 

intragastric doses of ["C] 1,ldichloroethylene indicates that systemic absorption following oral dosing is 

rapid (EPA, 1987). 1,l-Dichloroethylene is also readily absorbed following inhalation exposure. In rats 

exposed to 25, 75, or 150 ppm l,ldichloroethylene, equilibrium levels were reached in the blood by 45 

minutes, while at 300 ppm the blood level of 1,l-dichloroethylene tended to increase gradually for 3 hours 

(Dallas et al., 1983). 

1

2 


No data were available regarding the tissue distribution of 1,l-dichloroethylene in humans. In rats, 

1,l-dichloroethylene is rapidly hstributed to tissues following oral or dalation exposure. Following 

administration of a single oral dose of 350 or 500 ,q&g, the highest concentrations were found in the liver 

and ludneys within 30 minutes of dosing; general tissue distribution followed (Jones and Hathway, 1978b). 

After 72 hours, 3% or less of the administered dose was present, indicating that 1,l-dichloroethylene is not 

extensively stored in body tissues. Following inhalation exposure to 2000 ppm for 2 hours, rats preferentially 

accumulated 1 , 1 -dichloroethylene in the kidney and liver, with fasted rats having higher levels in these tissues 

than nonfasted rats (Jaeger et al., 1977). 


Pharmacokinetic data in animals show that metabolism is dose-dependent and saturable at inhalation 

concentrations of 150-200 ppm or approximately 50 mgkg orally (EPA, 1987). Metabolic conversion of 

1,l-hchloroethylene to an epoxide as an intermdate reactive metabolite has been proposed (IARC, 1986). 

The main biotransformation pathway in the rat most likely involves conjugation with glutathione (GHS), 

either with the epoxide or following remangement of the epoxide to chloroacetylchloride, with subsequent 

hydrolysis to mondoroacetic acid (ATSDR, 1993). Major urinary metabolites of 1 ,ldichloroethylene 

identifkd in rats are thiodihydroxyacetic acid and N-acetyl-S-cysteinylacetyl derivatives. Additional 

metabolites identified are chlmacetic acid, dithiohydroxyacetic acid (dithioglywlic acid), thiohydroxyacetic 

acid (thioglymlic acid), and methylthtoacetylamino-ethanol. Comparative studies with rodents have shown 

that mice metabolize 1,1 dchloroethylene to a greater extent than rats (IARC, 1986). 

2.4 EXCRETION 

No human data were available regarm the excretion of 1,ldichloroethylene. After oral 

administration of 5 mg radiolabeled 1,l-dichloroethylene to rats, most of the radioactivity was recovered 

within 72 hours (Reichert et al., 1979). Twenty one percent of the dose was recovered in the expired air, 

53.9% in urine, 14.5% in feces, 2.8 % in the carcass, and 7.5% was found in the cage rinse. 


3.1 ORAL EXPOSURES 


3.1.1.1 Human 

Information on the acute oral toxicity of 1 ,I dichloroethylene in humans was not available.

3 


Jones and Hathway (1978a) reported oral LD,, values of 1550 mgkg for rats and 194 and 217 mgkg, 

respectively, for male and female mice. A lethal dose of 5750 mgkg was reported for dogs (Tierney et al., 

1979). 

Increased kidney weights, increased plasma urea nitrogen and creatinine concentrations, and 

histopathological changes of the kidneys (vacuolization, tubular dilatation, and necrosis) were seen in rats 

ahstered a single oral dose of 400 mgkg of 1,l-dlchloroethylene (Jenkins and Andersen, 1978). Fastmg 

rats were more susceptible to the nephrotoxic effects of 1,l -dichloroethylene than nonfasting rats. 

Forkert et al. (1985) reported histopathological changes in Clara cells, pulmonary edema, hemorrhage, 

and focal lung collapse in mice administered a single oral dose of 200 mgkg of 1,l-dlchloroethylene. In 

contrast, Chieco et al. (1981) found no hstopathological lung changes in fasted or nonfasted rats administered 

a single oral dose of 200 mgkg of 1 , 1 -dichloroethylene. 

After oral treatment of rats with 1000 mgkg of 1,l-dichloroethylene, liver glutathione levels were 

decreased to 33% of the control values within 4 hours but returned to the control levels after 24 hours 

(Reichert et al., 1978). 


3.1.2.1 Human 

Information on the subchronic oral toxicity of 1,l-dichlorwthylene in humans was not available. 


Ramp et al. (1977) administered 50, 100, or 200 ppm 1,l-dichloroethylene in drinking water to male 

and female Sprague-Dawley rats for 90 days. The only adverse effect noted was an increased incidence of 

cytoplasmic vacuolization of hepatocytes in the high dose group. 

No adverse effects were obsexved in beagle dogs administered daily doses of 6.25, 12.5, or 25 mgkg 

of 1,l -dichloroethylene in gelatin capsules for 97 days (Quast et al., 1983). 

3.13 Chronic Toxicity 

3.1.3.1 Human 

Information on the chronic oral toxicity of 1,l -dichloroethylene in humans was not available. 


Male and female Sprague-Dawley rats were administered 50, 100, or 200 ppm 1,l-dichloroethylene in 

drinlung water for 2 years (Quast et al., 1983). The authors calculated a daily intake of 7, 10, or 20 

mg/kg/day for males and 9, 14, or 30 mgkg/day for females. There were no treatment-related effects on 

mortality, body weight, clinical chemistry, urinalysis, hematology, or tumor incidence. Female rats at all dose 

levels developed hepatic lesions, characterized as minimal hepatocellular fatty change and hepatocellular 

hypertrophy. In male rats, hepatocellular hypertrophy was seen at 100 and 200 ppm.

4 

In a 2-year gavage study conducted by NTP (1982), F344 rats and B6C3F, mice were administered 

1 , 1 -dichloroethylene at doses of 1 or 5 mg/kg/day (rats) and 2 or 10 mgkglday (mice), 5 daydweek for 2 

years. Mortality and growth rates were not af€ected in either species at either dose level. Compared with 

controls, an increased incidence of chronic inflammation of the kidneys occurred in high-dose male and 

female rats, and an increased incidence of liver necrosis was observed in high-dose male and low-dose female 

mice. 



Information on the developmental and reproductive oral toxicity of 1 , 1 -drchloroethylene in humans was 



No adverse effects were reported in Sprague-Dawley rats given 200 mg/L of 1,l-dichloroethylene in 

drinking water on gestation days 6-15 (Murray et al., 1979). In a three-generation study, Nitschke et al. 

(1983) found no treatment-related effects on reproduction or neonatal development in male and female 

Sprague-Dawley rats administered 50,100, or 200 mg/L of 1 , 1 -dichloroethylene in the drinking water. 

When rats were exposed to feed fumigated with 250 or 500 ppm 1,l-dichloroethylene, no changes in 

fetal mortality or fetal weight were found over several generations during a 2-year period (Alumot et al., 

1976). Based on the amount eaten and the measured residue level, the investigators calculated that due to 

volatility only 60 to 70% of the fumigant was actually consumed. 

3.1.5 Reference Dose 

3.1.5.1 Subchronic 

ORAL RfD: 

9E-3 mg/lcg/day (EPA, 1994b) 

LOAEL: 

9 mg/kg/day 

UNCERTAINTY FACTOR 1000 

PRINCIPAL STUDY: Quast et al., 1983 

COMMENTS: The chronic IUD was adopted as the subchronic IUD. The chronic IUD is under 

review and may be subject to change (EPA, 1994a). 

3.1.5.2 Chronic 

ORAL IUD: 

9E-3 mg/kg/day (EPA, 1994a) 

LOAEL: 

9 mg/kg/day 


PRINCIPAL STUDY: 

Quast et al., 1983 

CONFIDENCE: 

DATA BASE: 

RED: 

Medium 

Medium 

Medium 

VERIFICATION DATE: 1/22/85

5 

COMMENTS: The RfD is based on liver lesions seen in a 2-year drinlung water study with rats. An 

uncertainty factor of 10 each was applied for use of a LOAEL, interspecies variation, and 

protection of sensitive populations. The chroNc RfD is under review and may be subject to change 

(EPA, 1994a). 



3.2.1.1 Human 

The primary effect of acute exposure to high concentrations (approximately 4000 ppm) of 

1,l-dddoroethylene vapor is central nervous system (CNS) depression wluch may progress to 

unconsciousness (Gosselin et al., 1984). Lesions of the trigeminal nerve, causing motor weakness of the jaw, 

eye, and tongue muscles, have been reported following acute inhalation exposure to 1,l-dichloroethylene 

(Henschler et al., 1970). However, subsequent evaluation suggested that the toxic agent was either monoor 

dichloroacetylene (Haley, 1975). 


The lethality of 1,l-dichloroethylene appears to be dependent on dietary parameters. Inhalation LC+ 

for 4-hour exposures were 10,000-15,000 ppm in fed rats and 500-2500 ppm in fasted rats; death was due to 

vascular collapse and shock (Jaeger et al., 1973). 

Twenty 6-hour exposures to 500 ppm caused nasal irritation, reduced weight gain, and histopathological 

changes in the liver of rats (Gage, 1970). Exposure of fasted rats to 200 ppm 1,l-dichloroethylene for 4 hours 

produced injury to liver parenchymal cells (Reynolds et al., 1980). 


3.2.2.1 Human 

Information on the subchronic inhalation toxicity of 1,l-dic-mxthylene in humans was not available. 


Prendergast et al. (1967) exposed rats, guinea pigs, squirrel monkq, rabbits, and beagle dogs 

continuously to 20, 61, or 189 mg/m3 (5, 15, or 48 ppm) 1,l-dichloroethylene for 90 days. Early mortality 

occurred in guinea pigs and monkeys at all exposure concentrations without visible signs of toxicity 

compared with controls. All species had reduced body weight gains at 189 mg/m3. Also seen at the highest 

exposure level were increased liver alkaline phosphatase and serum glutamic-pyxuvic transaminase activities 

in rats and guinea pigs; kidney lesions in rats; and liver lesions in rats, dogs, and monkeys. The liver lesions 

were described as fatty changes, focal necrosis, hemosiderin deposition, lymphocyhc infiltration, bile duct 

proliferation, fibrosis, and pseudo-lobule formation.

6 


3.2.3.1 Human 

Ott et al. (1976) studied mortality and health examination data of 138 Dow Chemical Company 

workers who had been exposed to 1,l-lchloroethylene at concentrations rangmg from 70 ppm 

(time-weighted averages) in various job categories. The length of exposure ranged from 4 year to >10 years. 

Except for hepatic effects noted in two indwiduals with a history of alcohol consumption, mortality, 

spirometry, blood chemistry (including liver and renal tests), hematological parameters, and blood pressure 

measurements did not differ fiom controls matched for age and smoking. 

In a preliminary study, Tiemey et al. (1979) reported that 27 of 46 workers exposed to 1,ldichloroethylene 

for 6 years or less in a 1,l-dichloroethylene polymerization plant showed a 50% or greater 

loss of liver function. The study provided few detids, and a follow-up study has not been reported. 

3.23.2 Animal 

Lee et al. (1977) exposed both sexes of CD rats and CD-1 mice to 55 ppm 1,ldichloroethylene vapor, 

6 hourdday, 5 daydweek for up to 1 year. Most treated rats developed hepatocellular fatty changes, and 

treated mice developed various hepatocellular changes, as well as focal degeneration, and necrosis of the 

Iiver. 

Male and female Sprague-Dawley rats were exposed by inhalation to 10 or 40 ppm 1,ldichloroethylene, 

6 hours/day, 5 daydweek for 1 month (Quast et al., 1986). Because of lack of treatmentrelated 

effects, exposure was then increased to 25 or 75 ppm for 17 months, and surviving animals were held 

for an additional 6 months. The oniy effects attributed to 1,ldichloroethylene mhalation were hepatocellular 

changes in both male and female rats at both exposure levels. 



Idormation on the developmental and reproductive toxicity of 1 , 1 dichloroethylene following 

inhalation exposure in humans was not available. 


Short et al. (1977a) exposed CD rats and CD-1 mice to 1,ldichloroethylene for 23 hours/day on days 

6-16 of gestation. Rats were exposed to 15,57,300, or 449 ppm and mice to 15,30,57, 144, or 300 ppm. 

Maternal toxicity was seen in both species. In rats, 25% mortality occurred in dams exposed to the two 

highest concentrations; food consumption and weight gain was adversely af€ected at L 15 ppm. No pregnant 

mice survived exposure to 144 or 300 ppm. Early resorptions were common in all exposed groups, with 49 

and 64% resorptions in rats exposed to 57 and 449 ppm, respectively, and 100% resorptions in mice exposed 

to 30 and 57 ppm, respezt~vely. Some soft tissue anomalies were observed in offspring of rats at 15 and 57 

ppm, and a sigruficantly (p value not given) increased incidence of incomplete ossification of sternebrae 

occurred in offspring of mice at 15 ppm and in offspring of rats at 15,57, and 300 ppm. 

Murray et al. (1979) exposed Sprague-Dawley rats and New Zealand rabbits to 20 ppm (rats only), 80 

ppm, or 160 ppm 1,l-dichloroethylene vapor for 7 hourslday during organogenesis. Maternal toxicity 

(decreased weight gain, decreased food consumption, and increased liver weights) was observed in rats at 80

7 

and 160 ppm and in rabbits at 160 ppm. A statistically si&icant (pC0.05) increase of skeletal variations 

such as delayed ossification and wavy ribs was seen in offspring of rats exposed to both 80 and 160 ppm and 

in offspring of rabbits exposed to 160 ppm. In rabbits, resorptions were sigdicantly (p

8 


Information on the developmental and reproductive toxicity of 1,l-dichloroethylene in humans or 

animals by other routes of exposure was not available. 



3.4.1.1 Primary Target Organs 

1. Liver. Chronic oral exposure to 1,l dichloroethylene produced hepatocellular changes in rats 

and liver necrosis in mice. 

2. Kidneys. Chronic oral exposure to 1,l-dichloroethylene produced inflammation of the kidneys in 

rats. 

3.4.1.2 Other Target Organs 

Other target organs following oral exposure to 1,l -&chloroethylene were not identified. 



1. Liver. A prelimina~~ study reported loss of liver function in workers exposed to 

1,l dichloroethylene. Subchronic and chroNc inhalation exposure to 1 , 1-ddloroethylene 

produced mild to marked histological changes in the liver of several animal species. 

2. Kidneys. Subchronic exposure to 1,ldichloroethylene produced kidney lesions in rats. 

3. Development. Exposure to 1,ldichloroethylene during gestation produced increased 

resorptions and minor skeletal alterations in rats, rabbits, and mice at concentrations that 

caused matemd toxicity. 


Other target organs following inhalation exposure to 1 ,I-dichloroethylene were not identified. 

3.43 Other Routes of Exposure 


1. Skin. 1,1 -Dichlomethylene is initating to the skin of humans. 

2. Eyes. Direct contact of 1,ldichloroethylene to the eyes may cause conjunctivitis and 

transient corned injury in humans.

9 


Other target organs by other routes of exposure to 1,l -dichloroethylene were not idenMied. 


4.1 ORAL EXPOSURES 


Information on the carcinogenicity of 1,l-dichloroethylene in humans following oral exposure was not 

available. 


Oral carcinogenicity studies with rats and mice gave negative results. In a 2-year gavage study 

conducted by NTP (1982), F344 rats and B6C3F, mice were administered 1,l-dichloroethylene at doses of 

1 or 5 mg/kg/day (rats) and 2 or 10 mg/kg/day (mice), 5 dayslweek for 2 years. An increased incidence (not 

statistically sigmficant) of adrenal pheocytochromas was seen in high-dose male rats but not in female rats. 

Female mice admimstered the low dose exhibited an increased incidence of lymphomas and leukemia that 

was not considered treatment-related. In another gavage study, male and female Sprague-Dawley rats 

received 0.5, 5, 10, or 20 mg/kg/day, 4 to 5 daydweek for 78 weeks, followed by a 147-week observation 

pod (Maltoni et al., 1984, 1985). The pattern of neoplasms and their incidences was similar to that seen 

in controls. 

No carcinogenic effects were observed in Sprague-Dawley rats administered 50 to 200 ppm (7 to 

30 mgkg/day) 1,l-dichloroethylene in drinking water for 2 years (Quast et al., 1983). 



Ott et al. (1976) found no relationship between the occurrence of cancer or cancer mortality in 138 

workers primarily exposed to 1,l-dichloroethylene during 1950 to 1959 and 55 workers exposed from 1960 

to 1969. The subjects were divided into groups exposed to

10 

Maltoni et al. (1985) exposed male and female Swiss mice to 10 or 25 ppm 1,1-dichloroethyleneY 4 to 

5 daydweek for 12 months. bterim results of this study were reported in Maltoni et al., 1977.1 A 

statistically signtficant (p value not given) increase in ludney adenocarcinomas was reported in male mice 

exposed to 25 ppm. There were also statistically si&icant increases in mammary adenocarcinomas in 

female mice and pulmonary adenomas in both sexes; however, a dose-response relationship was not apparent. 

In a second study, Sprague-Dawley rats were exposed to 10, 25, 50, 100, or 150 ppm, 4 to 5 daydweek for 

12 months and observed until death. A statistically si&icant (p value not given) increase in total mammary 

tumors (but not carcinomas) was seen only at 10 ppm and 100 ppm but not at the other concentrations tested. 

In a study by Hong et al. (1981), small groups of CD rats and CD-I mice of both sexes were exposed 

to 55 ppm 1,l-ddoroethylene, 6 hourslday, 5 daydweek for 1,3,6 (rats and mice), or 10 months (rats only). 

Following treatment, all groups were observed for 12 months. There was a dose-related decrease in survival 

in male and female mice; survival in rats was similar to controls. No treatment-related tumors were reported 

in rats or mice. 

Female Chinese hamsters were exposed to 25 ppm 1,1,-dichloroethylene for 4 hours/day, 4-5 daydweek 

for 52 weeks and observed for life (164 weeks) (Maltoni et al., 1984). The tumor incidence was comparable 

to that in controls. 

43 OTHER ROUTES OF EXPOSURE 


Information on the carcinogenicity of IJ-dichloroethylene in humans by other routes of exposure was 


43.2 Animal 

Van Duuren et al. (1979) applied 40 or 121 mg ly1-dichlor0ethylene to the skin of Swiss mice three 

times weekly for 595 days. No skin tumors were observed. However, when 121 mg 1,1-dichloroethylene 

was applied once, followed 2 weeks later by dermal applications of the tumor promoter, phorbol myristate 

acetate (three times weekly for about 576 days), there was a statistically si@cant (p

11 



SLOPE FACTOR: 

UNIT RISK: 


6E-1 (mg/kg/dayy' (EPA, 1994a) 

1.7E-5 (pa)-' (EPA, 1994a) 

Quast et al., 1983; NTP, 1982 

COMMENT: The unit risk was derived from the highest of four oral slope factors calculated from two 

studies that did not show a statistically sigmficant increase in tumor incidence attributable to oral 

exposure to 1,l-dichloroethylene. The drinking water study in rats (Quast et al., 1983) produced 

the lowest slope factor of 0.2 (mg/kg/day)-'. The highest slope factor [0.6 (mgAcg/day)-'] was based 

on renal tumors in male rats (NTP, 1982). EPA indicated that use of data showing no statistically 

significant increase in tumor incidence appeared justified, since the slope factor derived was within 

a factor of 2 of the slope factor based on data from the inhalation study by Maltoni et al. (1977, 

1985). 


SLOPE FACTOR: 

UNIT RISK: 


1.2E4-0 (@g/day)-' (EPA, 1994b) 

5.OE-5 (pg/m3)-' (EPA, 1994a) 

Maltoni et al., 1977,1985 

COMMENT: The dation slope factor is based on kidney adenocarcinomas in male mice 

exposed for 12 months by inhalation. 

5. REFERENCES 

Alumot, E.O., E. Nachtomi, E. Mandel, et al. 1976. Tolerance and acceptable daily intake of chlorinated 

fumigants in the rat diet. Food Cosmet. Toxicol. 14: 105-1 10. 

ATSDR (Agency for Toxic Substances and Disease Registry). 1993. I, I-Dichloroethylene, Update. U.S. 

Department of Health and Human Services, Public Health Service. 

Budavari, S., M.J. O'Neill, A. Smith and P.E. Heckelman, Eds. 1989. The Merck Index: An Encycloma 

of Chemicals, Drugs, and Biologicals, 1 lth ed. Merck & Co., Rahway, NJ, pp. 1572-1573. 

Chieco, P., M.T. Moslen and E.S. Reynolds. 1981. Effect of administrative vehicle on oral 1,ldichloroethylene 

toxicity. Toxicol. Appl. Phannacol. 57: 146-1 55. 

Dallas, C.E., F.W. Weir, S. Feldman, et al. 1983. The uptake and disposition of 1,ldichloroethylene in rats 

during inhalation exposure. Toxicol. Appl. Phannacol. 68: 140-151. 

EPA (US. Environmental Protection Agency). 1983. Reportable Quantity Document for 1,I- 

Dichloroethylene (Vinylidne Chloride). Prepared by the Environmental Criteria and Assessment 

OBice, Cincinnati, OH, for the Office of Solid Waste and Emergency Response. ECAO-CIN-Rl02.

12 

EPA (U.S. Environmental Protection Agency). 1987. Health Efects Assessment for I, 1 -Dichloroethylene. 

Prepared by the Office of Health and Environmental Assessment, Environmental Criteria and 

Assessment Office, Cincinnati, OH, for the Office of Emergency and Remehal Response, Washington, 

DC. ECAO-CIN-HO5 la. 

EPA (U.S. Environmental Protection Agency). 1994a. Integrated Risk Information System (IRIS). 

Environmental Criteria and Assessment Office, Office of Health and Environmental Assessment, Cincinnati, 

OH. 

EPA (U.S. Environmental Protection Agency). 1994b. Health Assessment Summary Tables. Annual FY-94. 

Prepared by the OfEce of Health and Environmental Assessment, Environmental Criteria and 

Assessment Office, Cincinnati, OH, for the Office of Emergency and Remedial Response, Washington, 

DC. 

Forkert, P.G., L. Forkert, M. Farmqui, et al. 1985. Lung injury and repair: DNA synthesis following 1,ldichloroethylene. 

Toxicology 36: 199-214. 

Gage, J.C. 1970. The subacute inhalation toxicity of 109 industrial chemicals. Br. J. Ind. Med, 27: 1-18. 

Gosselin, RE., RP. Smith, H.C. Hodge, et al. 1984. Clinical Toxicology of Commercial Products, 5th ed. 

The Williams and Willcins Co., New York, p. II-163. 

Haley, T.J. 1975. Vinylidine chloride: A review of the literature. Clin. Toxicol. 8: 633-643. (Cited in U.S. 

Air Force, 1989) 

Henschler, D., F. Broser and H.C. Hopf. 1970. "Polyneuritis cranialis" following poisoning with chlorinated 

acetylenes while handling vinylidine chloride copolymers. Arch. Toxikol. 26: 62-75. 

Hong, C.B., J.M. Winston, L.P. Thornburg, et al. 1981. Follow-up study on the carcinogenicity of vinyl 

chloride and vinylidme chloride in rats and mice: Tumor incidence and mortality subsequent to 

exposure. J. Toxicol. Emiron. Health 7: 909-924. 

HSDB. 1994. Hazardous Substances Data Bank. MEDLARS online information Retrieval System, 

National Library of Medicine. Retrieved June, 1994. 

IARC (International Agency for Research on Cancer). 1986. Vilidine chloride. In. L4RC Monographs 

on the Evaluation of the Carcinogenic Risk of Chemicals to Humans, Vol. 39. IARC, Lyon, France, 

pp. 195-226. 

Jaeger, RJ., M.J. Trabulus and S.D. Murphy. 1973. The interaction of adrenalectomy, partial adrenal 

replacement therapy, and starvation with hepatotoxicity and lethality after 1,ldichloroethylene 

intoxication. Toxicol. Appl. Phannacol. 25: 491. 

Jaeger, RJ., L.G. Shoner and L. coffinan. 1977. 1,l-Dichloroethylene hepatotoxicity: Reposed mechanism 

of action and distribution and bin- of "C radioactivity following inhalation exposure in rats. 

Environ. Health Perspect. 21: 113-119. 

Jenkins, L.J., Jr., and M.E. Andersen. 1978. 1,l-Dichloroethylene nephrotoxicity in the rat. ToXcol. A&. 

Phannacol. 46: 131-141.

13 

Jones, B.K. and D.E. Hathway. 1978a. Differences in metabolism of Vinylidine chloride between mice and 

rats. Br. J. Cancer 37: 411-417. 

Jones, B.K. and D.E. Hathway. 1978b. The biological fate of vinylidine chloride in rats. Chem.- Biol. 

Interact. 20: 27-41. 

Lee, C.C., J.C. Bhandari, J.M. Winston, et al. 1977. Inhalation toxicity of vinyl chloride and vinylidine 

chloride. Emiron. Health Perspect. 2 1 : 25-32. 

Krijgsheld K.R, M.C. Lowe, E.G. Mimnaugh, et al. 1983. Lung-selective impairment of cytochrome P-450- 

dependent monooxygenases and cellular injury by 1 ,l-dichloroethylene in mice. Biochem. Biophys. 

Res. Commun. 110: 675-681. 

Maltoni, C., G. Gotti, L. Morisi and P. Chieco. 1977. Carcinogenicity bioassays of vinylidine chloride. 

Research Plan and Early Results. Med Lav. 68: 241-262. (Cited in EPA, 1992) 

Maltoni, C., G. Cotti and P. Chieco. 1984. Chronic toxicity and carcinogenicity bioassays of vinylidine 

chloride. Acta Oncol. 5: 91-145. (Cited in IARC, 1986) 

Maltoni, C., G. Lefemine, P. Chieco, et al. 1985. Experimental research on vinylidine carcinogenesis. In: 

Archives of Research on Industrial Carcinogenesis, Vol. 3, C. Maltoni and M. Mehlman, E&. 

Princeton Scientific Publishers, Princeton, NJ. (Cited in EPA, 1992) 

Murray, F.J., K.D. Nitschke, L.W. Rampy and B.A. Schwetz. 1979. Embvotoxicity and fetotoxicity of 

inhaled or ingested vinylidine chloride in rats and rabbits. Toxicol. Appl. Pharmacol. 49: 189-202. 

Nitschke, K.D., F.A. Smith, J.F. Quast, et al. 1983. A three-generation rat reproductive toxicity study of 

vinylidine chloride in the drinking water. Fund Appl. Toxicol. 3: 75-79. 

NTP (National Toxicology Program). 1982. Carcinogenesis Bioassay of Vinylidne Chloride (CAS No. 75- 

35-4) in F344 Rats and B6C3FI Mice (Gavage Studyl. NTP Tech. Rep. Series No. 228. NTP-80-82; 

NIH Publ. NO. 82-1784. 

Ott, M.G., W.A. Fishbeck, J.C. Townsend and E.J. Schneider. 1976. A health study of employees exposed 

to vinylidine chloride. J. Occup. Med. 18: 735-738. 

Prendergast, J.A., RA. Jones, L.J. Jenkins, Jr., and J. Siegel. 1967. Ef€ects on experimental animals of longterm 

inhalation of trichloroethylene, carbon tetrachloride, 1,1,1 -trichloroethane, 

dichlorodifluoromethane, and 1 , 1 dichloroethylene. Toxicol. Appl. Pharmacol. 10: 270-289. 

Quast, J.F., C.G. Humiston, C.E. Wade et al. 1983. A chronic toxicity and oncogenicity study in rats and 

subchronic toxicity study in dogs on ingested Vinylidbe chloride. Fund Appl. Toxicol. 3: 55-62. 

Quast, J.F., M.J. McKenna, L.W. h p y and J.M. Noms. 1986. Chronic toxicity and oncogenicity study 

on inhaled vinylidine chloride in rats. Fund. Appl. Toxicol. 6: 105-144. 

Rampy, L.W., J.F. Quast, C.G. Humiston, et al. 1977. Interim results of two-year toxicological studies in 

rats of vinylidine chloride incorporated in the dnnlang water or administered by repeated inhalation. 

Environ. Health Perspect. 21: 333-343.

14 

Reichert, D., H.W. Werner and D. Henschler. 1978. Role of liver glutathione in l,l-&chloroethylene 

metabolism and hepatotoxicity in intact rats and isolated perfused rat liver. Arch. Toxicol. 41 : 169- 179. 

Reynolds, E.S., M.T. Moslen, J.P. Boor and R.J. Jaeger. 1980. 1,l-Dichloroethylene hepatotoxicity. Time 

course of GSH changes and biochemical aberrations. Am. J. Pathol. 101: 331-342. (Cited in IARC, 

1986) 

Short, R.D., Jr., J.L. Minor, J.M. Winston, et al. 1977a. Toxicity Studies of Selected Chemicals. Task II. 

The Developmental Toxicity of Vinylidme Chloride Inhaled by Rats and Mice during Gestation. 

Prepared by Midwest Research Institute, Kansas City, MO for the Office of Toxic Substances, U.S. 

Environmental Protection Agency. EPA-560/6-77-022. (Cited in EPA, 1983) 

Short, RD., J.L. Minor, J.M. Winston, et al. 197%. A dominant lethal study in male rats after repeated 

exposures to vinyl chloride or vlnylidine chloride. J. Toxicol. Environ. Health 3: 965-968. 

Tierney D.R, T.R. Blackwood and M.R Piana. 1979. Status Assessment of Toxic Chemicals: Vinylidine 

chloride. Prepared by Monsanto Research Corporation for 0fk.e of Research and Development, U.S. 

Environmental Rotection Agency, Cincinnati, OH. EPA 600/2-79-2 100; PB80- 146442. 

Torkelson, T.R and V.K. Rowe. 1982. Halogenated aliphatic hydrocarbons. In: Patty’s Industrial Hygene 

and Toxicology, G.D. Clayton and F.E. Clayton, E&, Vol. IIC. John Wiley & Sons, New York, pp. 

3 5 45 -3 5 5 0. 

U.S. Air Force. 1989. 1,l-Dichloroethylene. In: The Installation Program Toxicology Guide, VoI. 2. 

Wright-Patterson Air Force Base, OH, pp. 14-1 to 14-30. 

Van Duuren, B.L., B.M. Goldschmidt, G. Loewengart, et al. 1979. Carcinogenicity of halogenated olefbic 

and aliphatic hydrocarbons in mice. J. Natl. Cancer Imt. 63: 1433-1339. (Cited in ATSDR, 1993).


INDENO[~,~,~-C~JPYRENE 

May 1994 

Prepared by 







Prepared for 



*Managed by Martin Marietta Energy Systems, Inc., for the U.S. Department of Energy under 

Contract No. DE-AC05-MOR2 1400



Indeno[l,2,3-cd]pyrene, a crystalline solid with a chemical formula of GH,2 and a molecular 

weight of 276.3, is a polycyclic aromatic hydrocarbon (PAH). There is no commercial production or 

known use of this compound (IARC, 1983). Indeno[l,2,3-~dJpyrene is found in fossil fuels and occurs 

ubiquitously in products of incomplete combustion (IARC, 1983) and has been identified in' soils, 

groundwater, and surface waters at hazardous waste sites (ATSDR, 1990). 

No absorption data were available for indeno[l,2,3-cd]pyrene; however, by analogy to structurallyrelated 

PAHs, primarily benzo[u]pyrene, it would be expected to be absorbed from the gastrointestinal 

tract, lungs, and skin (EPA, 1991). In vivo metabolites identified in mouse skin include the rruns-1,2- 

dihydrodiol and 8- and 9-hydroxy forms of indeno[l,2,3-cd]pyrene (Rice et al., 1986). Similar 

metabolites were formed in vitro in rat liver microsomes (Rice et al., 1985). 

No data were found concerning the acute, subchronic, chronic, developmental, or reproductive 

toxicity of indeno[l,2,3-cd]pyrene. Because of a lack of toxicity data, an oral reference dose (RfD) or 

inhalation reference concentration (RfC) has not been derived (EPA, 1994). 

No long-term oral or inhalation bioassays were available to assess the carcinogenicity of 

indeno[ 1,2,3-cdJpyrene. The compound was tested for carcinogenicity in dermal application, lung 

implant, subcutaneous (s.c.) injection, and intraperitoneal (i.p.) injection studies. Dermal application of 

0.1-0.5% solutions of indeno[l,2,3-cdJpyrene in acetone produced skin papillomas and carcinomas in 

mice (Hoffmann and Wynder, 1966). In initiation-promotion assays, indeno[l,2,3-cd]pyrene was active 

as an initiator of skin carcinogenesis (Hoffmann and Wynder, 1966; Rice et al., 1986). Dose-related 

increases of epidermoid carcinomas of the lungs were reported in rats receiving single lung implants of 

0.164.15 mg indeno[l,2,3-@pyrene (Deutsch-Wenzel et al., 1983). Injection site sarcomas developed 

in mice given three S.C. injections of 0.6 mg indeno[l,2,3-~dJpyrene (Lacassagne et al., 1963). The 

compound was not tumorigenic when newborn mice received 2.1 pmol indeno[l,2,3-~dJpyrene via i.p. 

injection (LaVoie et al., 1987). 

Based on no human data and sufficient evidence for carcinogenicity in animals, the United Stated 

Environmental Protection Agency @PA) has assigned a weight-of-evidence classification of B2, probable 

human carcinogen, to indeno[ 1,2,3-cd]pyrene (EPA, 1994). 

iii

THIS PAGE INTENTIONALLY LEFT BLANK 

iv


Indeno[l,2,3-cdJpyrene (CAS Reg. No. 193-39-5), also known as IP, ortho-phenylenepyrene, 

1 , lO-(ortho-phenylene)pyrene, 1,1@(l72-phenylene)pyrene, and 2,3-ortho-phenylenepyrene (IARC, 1983), 

is a polycyclic aromatic hydrocarbon (PAH) with one five-membered ring and five six-membered rings. 

It is a crystalline solid with a chemical formula of %Hl2, a molecular weight of 276.3, a melting point 

of 163.6"C (IARC, 1983), and a boiling point of 530°C (ATSDR, 1990). Indeno[l,2,3-cdJpyrene is 

insoluble in water but is soluble in organic solvents. It has a vapor pressure of - 1 ~10-~~ torr at 20°C, 

an estimated octanol/water partition coefficient of 6.584, and a Henry's Law constant of 6.95~10" 

(ATSDR, 1990). 

There is no commercial production or known use of indeno[l,2,3-cdJpyrene (IARC, 1983). The 

compound is found in fossil fuels and occurs ubiquitously in products of incomplete combustion. It has 

been detected in mainstream cigarette smoke; gasoline engine exhaust; emissions from burning coal; 

lubricating oils; used motor oils (IARC, 1983); and soils, surface waters, and groundwater at hazardous 

waste sites (ATSDR, 1990). Indeno[l,2,3-cd]pyrene is one of a number of PAHs on the United States 

Environmental Protection Agency's (EPA's) priority pollutant list (ATSDR, 1990). 



Data regarding the gastrointestinal or pulmonary absorption of indeno[l,2,3-cdJpyrene in humans 

or animals were not available. However, data from structurally-related PAHs, primarily benzo[u]pyrene, 

suggest that indeno[l,2,3-cdjpyrene would be absorbed from the gastrointestinal tract, lungs, and skin 

(EPA, 1991). 


No human or animal data were available concerning the tissue distribution of 

indenor 172,3-cdJpyrene. 


In mouse skin, Rice et al. (1986) identified 8-hydroxyindo[l,2,3-cdJpyrene as the most abundant 

metabolite; other major metabolites included 9-hydroxyindo[ 1,2,3-cdJpyrene and fruns- 1,2dihydro-l,2- 

dihydroxyindenol[ 1,2,3-~dJpyrene. In vitro metabolism studies using rat liver microsomes show that 

some metabolites identified included the franr-l,2dihydrodiol of indeno[ 172,3-cdJpyrene, the fruns-l,2- 

dihydrodiols of 8- and 9-hydroxy-indeno[l,2,3-cdjpyrene, and the 1,2quinone form of indeno[l,2,3- 

capyrene (Rice et al., 1985). 

1

2 

2.4 EXCRETION 

No human or animal data were available concerning the excretion of indeno[l,2,3-cdJpyrene. 



Information on the acute, subchronic, chronic, developmental, or reproductive oral toxicity of 

indeno[l,2,3-cd]pyrene in humans or animals was not available. Because of the lack of toxicity data, an 

oral reference dose (RfD) for indeno[l,2,3-cdJpyrene has not been derived (EPA, 1994). 



indeno[l,2,3-cdJpyrene in humans or animals following inhalation exposure was not available. Because 

of a lack of toxicity data, an inhalation reference concentration (FUC) for indeno[ 1,2,3-cd]pyrene has not 

been derived (EPA, 1994). 



indeno[l,2,3-cdJpyrene in humans or animals by other routes of exposure was not available. 

3.4 TARGET ORGANWCRITICAL EFFECTS 

No data were available to identify target organs or critical effects for oral, inhalation, or other 

routes of exposure to indeno[ 1,2,3-cd]pyrene. 



Infonnarion on the carcinogenicity of indeno[l,2,3-~dJpyrene in humans or animals following oral 

exposure was not available.

3 



Although there are no human data that specifically link exposure to indeno[l,2,3-~dlpyrene to 

human cancers, indeno[l,2,3-cdJpyrene is a component of mixtures that have been associated with human 

cancer. These mixtures include coal tar, soots, coke oven emissions, and cigarette smoke (EPA, 1994). 


Information on the carcinogenicity of indeno[ 1,2,3-cdJpyrene in animals following inhalation 




Information on the carcinogenicity of indeno[l,2,3-cdJpyrene in humans by other routes of exposure 



Indeno[ 1,2,3-Cd]pyrene was tested for carcinogenicity in skin application, initiation-promotion, lung 

implant, subcutaneous (s.c.) injection, and intraperitoneal (i.p.) injection bioassays. 

Hoffmann and Wynder (1966) applied solutions of indeno[ 1,2,3-cdJpyrene in dioxane or acetone 

to the skin of groups of 20 female Swiss albino mice. Solutions of 0.05 or 0.1 % indeno[l,2,3-cdJpyrene 

in dioxane did not induce skin tumors, whereas acetone solutions induced a dose-related increased 

incidence of skin tumors. No tumors were observed following treatment with 0.01 or 0.05% solutions 

in acetone; a concentration 0.1 % induced six papillomas and three carcinomas beginning at 9 months, 

and a concentration of 0.5% induced seven papillomas and five carcinomas, with the first tumor 

appearing after 3 months. By contrast, repeated topical application of up to 9.2 pg of indeno[l,2,3- 

cdJpyrene in acetone for a lifetime did not produce skin tumors in mice (Habs et al., 1980). 

Rice et al. (1986) evaluated the tumor-initiating activity of indeno[l,2,3-cdjpyrene by applying 

indeno[l,2,3-cdJpyrene in acetone every other day for 10 days (total dose 1 mg) to the skin of 20 

Cr1:CD-1 mice. This procedure was followed by treatment with 12-o-tetradecanoyl-phorbol-13-acetate 

(TPA) 3 times weekly for 20 weeks. The incidence of skin tumors was close to 100%. Hoffmann and 

Wynder (1966) reported that 10 skin applications at 2-day intervals at a total dose of 250 pg initiated skin 

carcinogenesis when female Swiss albino mice were subsequently treated with croton oil. A total of 10 

papillomas developed in 5 animals treated with croton oil. 

Female Osborne-Mendel rats (35/group) received single lung implants of 0.16, 0.83, or 4.15 mg 

indeno[172,3-cdJpyrene in a mixture of beeswax and trioctanoin (Deutsch-Wenzel et al., 1983). An 

untreated group and a group receiving the vehicle served as controls. Granulomatous inflammatory 

lesions developed at the injection sites. After a lifetime of observation, the incidence of epidermoid

4 

carcinomas in the lung showed a statistically significant (p=0.05) dose-related increase. The observed 

incidences were 3/35, 8/35, and 21/35, respectively, in the low-, mid-, and high-dose groups. In 

addition, one pleomorphic lung sarcoma developed in one lowdose rat. No lung tumors occurred in 

untreated or vehicle control animals. 

Male and female XW nc/Z mice (14/sex) were given S.C. injections of 0.6 mg indeno[l,2,3- 

capyrene in olive oil once a month for 3 months (Lacassagne et al., 1963). Injection site sarcomas 

developed in 10 male mice within 265 days and in 1 female mouse within 145 days. Although no 

concurrent controls were used, the authors reported that no spontaneous skin tumors had been observed 

in historical controls. 

LaVoie et al. (1987) administered i.p. injections of indeno[l,2,3-cdJpyrene in dimethyl sulfoxide 

to 30 CD-1 mice (males and females combined) on days 1, 8, and 15 of life at a total dose of 

2.1 pmoYmouse. The animals were sacrificed at 52 weeks of age. A lung adenoma developed in 1/11 

surviving male mice; no lung tumors were seen in female treated mice or in vehicle controls. 

Although several noncarcinogenic PAHs have been shown to reduce the ability of benzo[a]pyrene 

to produce injection site sarcomas, S.C. injections of indeno[ 1,2,3-cd]pyrene in tricaprylin vehicle had no 

such inhibiting effect ( Fa et al., 1964). 

4.4 EPA WEIGHT OF EVIDENCE 

Classification-B2; probable human carcinogen (EPA, 1994) 

Basis-Based on no human data and sufficient data from animal bioassays. Indeno[ 1,2,3-cdJpyrene 

produced tumors in mice after lung implants, S.C. injection, and dermal exposure. Indeno[l,2,3- 

cdJpyrene tested positive in bacterial gene mutation assays. 

# 


No carcinogenicity slope factors were calculated. 

5. REFERENCES 

ATSDR (Agency for Toxic Substances and Disease Registry). 1990. Toxicological Profile for Polycyclic 

Aromatic Hydrocarbons. Acenaphthene, Acenaphtlylene, Anthracene, Benzo (a)anthracene, 

Benzo (a)pyrene, Benzo Ofluoranthene, Benzo (g, i, h)perylene, Benzo (klfluoranthene, Chrysene, 

Dibenzo(a, h)anzhene, Fluoranthene, Fluorene, Indeno(1 I 2,3-cId)pyrene, Phenanthrene, Pyrene. 

Prepared by Clement international Corporation, under Contract No. 205-88-0608. ATSDIUTP-90- 

20. 

Deutsch-Wenzel, R.P., H. Brune, G. Grimmer, et al. 1983. "Experimental studies in rat lungs on the 

carcinogenicity and dose-response relationships of eight frequently occurring environmental 

polycyclic aromatic hydrocarbons." J. Natl. Carrcer I.!. 71: 539-544.

5 

Falk, H.L., P. Kotin, and S. Thompson. 1964. "Inhibition of carcinogenesis. The effect of polycyclic 

hydrocarbons and related compounds. " Arch. Environ. Health 9: 169-179. 

Habs, M., D. Schrnahl, and J. Misfeld. 1980. "Local carcinogenicity of some environmentally relevant 

polycyclic aromatic hydrocarbons after lifelong topical application to mouse skin. 'I Arch. 

Geschwulsgorsch. 50: 266-274. 

Hoffmann, D. and E.L. Wynder. 1966. "Beitrag zur carcinogen Wirkung von Dibenzopyrene." Z. 

Krebsforsch. 68: 137- 149. 

IARC (International Agency for Research on Cancer). 1973. "Indene( 1,2,3-cd)pyrene." In: IARC 

Monographs on the Evaluation of Carcinogenic Risk of Chemicals to Man. Certain Polycyclic 

Aromatic Hydrocarbons and Heterocyclic Compounds, Vol 3. IARC, Lyon, France, pp. 229-237. 

IARC (International Agency for Research on Cancer). 1983. "Indene[ 1,2,3-cd]pyrene." In: IARC 

Monographs on the Evalm'on of Carcinogenic Risk of Chemicals to Humans. Polycyclic Aromatic 

Compoundr, Part I, Chemical, Environmental and Experimental Data, Vol 32. IARC, Lyon, 

France, pp. 373-378. 

Lacassagne, A., N.P. Buu-Hoi, F. Zajdela, et al. 1963. "Activite cancerogene d'hydrocarbures 

aromatiques polycycliques a noyau fluoranthene. " Un. Int. Cancer Acta 19: 490-496. 

LaVoie, E.J., J. Braley, J.E. Rice, and A. Rivenson. 1987. "Tumorigenic activity for non-alternant 

polynuclear aromatic hydrocarbons in newborn mice." Cancer Lett. 34: 15-20. 

Rice, J.E., D.T. Coleman, T.J. Hosted, Jr., et al. 1985. "Identification of mutagenic metabolites of 

indeno[i,2,3-cd]pyrene formed in vitro with rat liver enzymes." Cancer Res. 45: 5421-5425. 

Rice, J.E., T.J. Hosted, Jr., M.C. DeFloria, et al. 1986. "Tumor-initiating activity of major in vivo 

metabolites of indeno[l,2,3-cd]pyrene on mouse skin. I' Carcinogenesis 7: 1761-1764. 

U . S . EPA. 1991. Drinking Water Criteria Document for Polycyclic Aromatic Hydrocarbons (PM). 

Prepared by the Environmental Criteria and Assessment Office,Office of Health and Environmental 

Assessment, U.S. Environmental Protection Agency, Cincinnati, OH, for the Office of Drinking 

Water. ECAO-CIN-DOlO. 

U.S. EPA. 1994. Integrated Risk Information System (IRIS). Environmental Criteria and Assessment 

Office, Office of Health and Environmental Assessment, Cincinnati, OH.


MANGANESE 

July 1995 

Prepared by: 

A. A. Francis and C. Forsyth 


Biomedical and Environmental Infomation Analysis Section 




Prepared for: 



*Managed by Lockheed Martin Energy Systems, Inc., for the U.S. Department of Energy under 

Contract No. DE-AC05-840R2 1400


Manganese is an essential trace element in humans that can elicit a variety of serious toxic 

responses upon prolonged exposure to elevated concentrations either orally or by inhalation. The 

central nervous system is the primary target. Initial symptoms are headache, insomnia, dsorientation, 

anxiety, lethargy, and memory loss. These symptoms progress with continued exposure and 

eventually include motor disturbances, tremors, and Mtculty in walking, symptoms similar to those 

seen with Parkinsonism. These motor difficulties are often irreversible. Based on human 

epidemiologcal studies, 0.8 mg/kg/day for dnnking water exposure and 0.34 mg/m’ in air for 

inhalation exposure have been estimated as lowest-observed-adverse-effect levels (LOAELs) for 

central nervous system effixts. 

Effects on reproduction (decreased fertility, impotence) have been observed in humans with 

inhalation exposure and in animals with oral exposure at the same or slmilar doses that initiate the 

central nervous system effects. An increased incidence of coughs, colds, dyspnea during exercise, 

bronchitis, and altered lung ventilatory parameters have also been seen in humans and animals with 

inhalation exposure. A possible effect on the immune system may account for some of these 

respiratory symptoms. 

Because of the greater bioavailability of manganese from water, separate reference doses (RfD) 

for water and diet were calculated. A chronic (EPA 1995) and subchronic RfD (EPA 1994) for 

drinking water of 0.005 mg/kg/day has been calculated by EPA fiom a human no-observed-adverseeffect 

level (NOAEL) of 0.005 mgkg/day; the NOAEL was determined fiom an epidemiological 

study of human populations exposed for a lifetime to manganese concentrations in drinking water 

rangmg fiom 3.6-2300 pg/L (Kondakis et al. 1989). A chronic (EPA 1995) and subchronic RfD 

(EPA 1994) of 0.14 mg/kg/day for dietary exposure has been Calculated by EPA fiom a human 

NOAEL of 0.14 mg/kg/day, which was determined from a series of epidemiological studies 

(Schroeder et al. 1966, WHO 1973, NRC 1989). Large populations with different concentrations of 

manganese in their diets were examined. No adverse effects that were attributable to manganese were 

seen in any of these groups. For both the drinlung water and dietary values, the RfD was derived 

from these studies without uncertamty factors since manganese is essential in human nutrition and 

the exposure of the most sensitive groups was included in the populations examined. EPA (1995) 

indicates that the chronic RfD values are pendmg change. 

A reference concentration (RE) of 0.05 pg/m’ @PA 1995) for chronic inhalation exposure was 

calculated fiom a human LOAEL of 0.05 m@m3 for impairment of neurobehavioral function from 

an epidemiological study by Roels et al. (1992). The study population was occupationally exposed 

to airborne manganese dust with a median concentration of 0.948 mg/m’ for 0.2 to 17.7 years with 

a mean duration of 5.3 years. Neurological examinations, psychomotor tests, lung function tests, 

blood tests, and urine tests were used to determine the possible effects of exposure. The LOAEL was 

derived from an occupational-lifetime integrated respirable dust concentration of manganese dioxide 

expressed as mg manganese/m3 x years. Coddence in the inhalation RfC is rated mdum by the 

EPA. 

Some conflicting data exist on possible carcinogenesis following injections of manganese 

chloride and manganese sulfate in mice. However, the EPA weight-of-evidence classlfication 

... 

u1

is: D, not classifiable as to human carcinogenicity based on no evidence in humans and inadequate 

evidence in animals (EPA 1995). 

iv


Manganese (CAS registry number 7439-96-5) makes up about 0.10% of the earth's crust and is 

the 12th most abundant element. It can exist in oxidation states fiom -3 to +7, the most common 

being +4 in the chemical form of manganese dioxide (Keen and Leach 1988). The oxides and 

peroxides are used in industry as oxidizers, and the metal is used for manufacturing metal alloys to 

increase hardness and corrosion resistance. In living systems, manganese is an essential element that 

is found most often in the +2 valence (Keen and Leach 1988, Stokinger 1981). 

Normal nutritional requirements of manganese are satisfied through the diet, which is the normal 

source of the element, with minor contributions fiom water and air (EPA 1984). The National 

Research Council (NRC 1989) recommends a dietary allowance of 2 to 5 mg/day for a safe and 

adequate intake of manganese for an adult human. Toxic exposures occur largely due to particulate 

material in the air fiom mining and manufacturing activity. 

2. METABOLISM AND DISTRIBUTION 


Intestinal absorption has been estimated to be between 3 and 10% of the amount of manganese 

ingested and is a multiple-step process similar to and involving some of the same binding sites as in 

iron absorption (EPA 1995). Experiments with isolated rat intestines indicate that manganese 

absorption is carrier-mdated with saturation Occurring at 0.5 mM (Testolin et al. 1993). The 

absorption of manganese by inhalation depends on the particle size. The larger particles are cleared 

from the respiratory tract by the cilia and swallowed; whereas, the fine particles (< 2.5 microns) are 

deposited in the lungs and must be cleared by absorption into the blood and lymph circulation (EPA 

1995). It is estimated that 60 to 70% of the inhaled particles are eventually swallowed (Stokhger 

1981). 


Once absorbed, manganese is transported to organs rich in mitochondria (in particular the liver, 

pancreas, and pituitary) where it is rapidly concentrated. Accumulation of manganese in the central 

nervous system following an intraperitoneal or intramuscular injection occurs slowly reaching a 

maximum in about 30 days. Distribution is homogeneous in the brain with lower concentrations in 

the spinal cord. The average turnover time in the central nervous system is reported to be about 1 10 

days following intraperitoneal injection and about 55 days for intramuscular injection 

(Stokinger 1981). 

1

2 

23 METABOLISM 

Manganese does not undergo metabolism; it is absorbed and excreted unchanged. However, 

manganese is an essential trace element and is involved as an activator or cofactor with a number of 

diverse enzymes involved with energy metabolism, digestion, and lipid and protein metabolism 

(Orten and Neuhaus 1975). 

2.4 EXCRETION 

The normal adult body pool of about 20 mg is maintained by the liver, and excess manganese 

is excreted into the intestine via the bile. This control is achieved with a daily intake of 10 to 20% 

of the total pool; therefore, relatively large amounts are handled by this mechanism. The normal 

urinary level of manganese averages about 2.75 pg/L with a range of about 1.0 to 8.0 p a. Urinary 

levels over 10 pg/L are indicative of manganese overexposure (Stokinger 198 1). 




3.1.1.1 Human 

Information on the acute oral toxicity of manganese in humans was unavailable. 


Due to the control exerted by mammals over manganese absorption and excretion, acute oral 

toxicity is observed only after relatively large doses. However, several LDS, values have been 

calculated. In one oral study using Sprague-Dawley rats, manganese dichloride tetrahydrate was 

given by stomach tube, and the animals were observed for 14 days. The LD, was calculated to be 

1484 mgkg or 7.5 mmoIeAcg. The manganese concentrations in the liver, kidney, spleen, heart, 

testes, brain, and blood of the surviving animals retumed to control values within the 14day period 

(Holbrook et al. 1975). 

Other oral values include an LD, of 1715 mgkg for manganese dichloride in mice and 

3730 mg/kg for manganese2' acetate in rats (Lew~s and Sweet 1984). Potassium permanganate, a 

strong oxidizing agent, is an irritant to mucosal tissues, is hemolyhc, and damages capillaries 

regardless of the route. An oral LDx, of 1090 mgkg has been determined for potassium 

permanganate in rats (Stokinger 1981). 

However, rats maintained on manganesedeficient diets for 2 1 days had higher plasma ammonia 

and lower plasma urea concentrations in association with lowered hepatic manganese concentrations 

and decreased arginase activity as compared to rats on diets containing 48 pg manganesdg diet 

(Brock et al. 1994). 

3.1.2 Subchronic Toxicity

3 

3.1.2.1 Human 

A number of epidemiological studies have been performed that document the response of human 

populations to subchronic or chronic exposure to elevated manganese concentrations. Signs of 

toxicity may appear within months and can continue for years. Initial signs of manganese toxicity 

usually include headache, disorientation, speech disturbances, memory loss, and acute anxiety. 

Prompt removal of the affected person from the source of manganese exposure usually results in 

reversal of most of the symptoms; however, the symptoms will increase and eventually become 

irreversible if the individual continues to be exposed to high manganese concentrations (Keen and 

Leach 1988). Section 3.1.3 provides discussions of individual studies. 


A decrease in brain amines was observed in a study of the effects of manganese chloride on 

brain chemistry. Male Sprague-Dawley rats were given 0.1 or 1.0 mg manganesdd in drinkrng 

water for 8 months after which the brains were removed, dissected, and analyzed for various brain 

amines. Effects were seen with both doses. Decreases in the following amines were observed: 

dihydroqphenylacetic, noradrenaline, homovanillic acid, 5-hydroqmdolacetic acid, noradrenaline, 

and serotonin. 

In a similar study, rats were given 0.54 mg MnC12.5H@n.L in drinking water for 90 days 

(Subhash and Padmashree 1991). Manganese accumulation in various brain regions was two- to 

three-fold that of controls. In addition, inhibition of dopamine P-hydroxylase and monoamine 

oxidase, decreased and increased dopamine levels, and increased serotonin were observed in various 

brain regions. 

Feedlot calves fed a diet supplemented with 50 ppm zinc methionine plus 40 ppm manganese 

methionine for 34 days had better response to disease challenge than control (no supplement) animals 

or calves supplemented with the oxide forms of zinc and manganese. Calves fed the organic form of 

the metals had lower temperatures, higher feed intake, and greater body weight gain foIlowing 

challenge with infectious bovine rhinotracheitis virus when compared to control or inorganic zinc 

and manganese supplemented calves (Chirase et al. 1994). 


3.1.3.1 Human 

An epidemiological study by Schrder et al. (1966) on n o d diets in the United States, 

England, and Holland, demonstrated that the average daily intake of manganese ranged from about 

2.3 to 8.8 mg/day. Certain other diets (vegetarian) were possibly higher in manganese, but all were 

considered safe for chronic human consumption. In another portion of the study, patients were given 

9 mg manganesdday as manganese citrate for many months. Assuming the average dietary intake 

of 2.5 mg/day, the total manganese intake was about 11.5 mg/day. No signs of toxicity were seen in 

either part of the study. 

The World Health Organization reviewed the previous study and other dietary information and 

concluded that 2 to 3 mg manganesdday is adequate for adults and 8 to 9 mg/day is safe (WHO 

1973). The Food and Nutrition Board of the National Research Council also examined the avadable 

evidence and determined 10 mg manganesdday to be safe. They chose an adequate and safe intake 

of manganese to be 2 to 5 mg/day for adults (NRC 1989).

4 

Sixteen cases of manganese toxicity from drinking contaminated water were reported in a study 

by Kawamura et al. (1941). The symptoms included lethargy, increased muscle tonus, tremor, and 

mental disturbances. Children were affected less than the elderly. The drinking water was estimated 

to contain at least 28 mg manganese& which would be equivalent to an intake of 0.8 mgkglday (56 

mg/day) for a 70-kg adult drinking 2 L of water/day. 

Kandalus et al. (1989) conducted an epidemiologtcal study in three areas of northwestern Greece 

containing maximum manganese concentrations of 14.6, 252.6 and 2300 pgL in dnnking water. 

Mean concentrations of manganese in hair samples were 3.5 1,4.49 and 10.99 pg/g dry weight from 

the areas with low, medium, and high manganese concentrations, respectively, in drinking water. The 

concentration in whole blood was the same for all three areas. The individuals in the study were 

given a neurological examination designed to test for the presence and severity of 33 different 

symptoms associated with manganese central nervous system toxicity. The combined average scores 

for both sexes were 2.7, 3.9, and 5.2 for the low, medium, and high concentrations, respectively. 

Although this effect was not large, the score for the hgh concentration was sigmfkantly higher than 

the score recorded for the low concentration. The experiment was criticized for the small numbers 

of individuals tested, the lack of scatter data, and the lack of dietary data. Nevertheless, the 

experiment established an uncertainty about extrapolating dietary risk factors to drinking water 

without considering the possibility of differential absorption @PA 1995). 

In addition to the central nervous system effects, an iron-responsive anemia is commonly found 

with orally-induced manganese toxicity (Keen and Leach 1988). 

3.13.2 Animal 

A number of studies have shown that biochemical changes occur in the brains of rodents 

following the administration of about 1 mglmL manganese dichloride tetrahydrate in drinking water 

(Lai et al. 1981, Leung et al. 1981; see Sect. 3.1.2.2 for further chscussion). Various forms of 

manganese in the diet of mice affect biogenic amine levels in the brain. Mice were fed 

2 g manganesekg in the form of MnC12.4H20, Mn(CQ COOL -4% 0, MnCQ , or h4nQ for 12 

months (Komura and Sakamoto 1992). Manganese dioxide feeding resulted in lowered dopamine 

levels in the corpus striatum, hypothalamus, and midbrain. Accumulation of manganese in the brain 

correlated with both reduced dopamine levels in the hypothalamus and suppression of motor activity 

in the manganese acetate group. 

A study of more relevance to humans was conducted by Gupta et al. (1980). Neurological 

symptoms, including muscular weakness and rigidity of the lower limbs, were seen in a group of 4 

rhesus monkeys after 18 months treatment with 6.9 mg manganese,/kg/day @veri as manganese 

dichloride tetrahydrate). Degenerated neurons in the substantia nigra and scanty neuromelanin 

granules in pigmented cells were reported upon histological analysis. 

Lambs on a high manganese diet developed a reduction in hemoglobin. This observation is 

consistent with the anemia seen in humans and indicates that large amounts of manganese can 

interfere with intestd iron absorption (Stokhger 198 1).



5 

Information on developmental and reproductive toxicity of manganese in humans following oral 



Groups of four adult male rhesus monkeys were given daily doses of 0 or 25 mg manganese 

chloride tetrahydratekg (6.94 mg manganesekg) by oral gavage for 18 months. The testes of the 

treated monkeys exhibited interstitial edema and degeneration of the seminiferous tubules 

(Murthy et al. 1980, EPA 1989). 

Other studies measured the effect of manganese chloride on various brain enzyme activities. 

Rats were exposed to 0, 1, or 10 mg/d in the drinking water from conception onwards. Both Na-K- 

ATPase and Mg-ATPase activities increased in most brain regions in treated rats as compared to 

controls between postnatal days 5 and 20 but were decreased by day 60. These transient enzyme 

changes occurred despite a dose-dependent increase in brain manganese levels (Lai et al. 1991). No 

differences were observed for brain monoamine oxidase activity (hung et al. 1993). 

Pregnant Long-Evans rats were fed diets containing 0,400,1100, or 3550 ppm manganese from 

day 2 of gestation. The F, offspring were fed the same diet until they were up to 225 days old. 

Decreased serum testosterone was observed in 100-day-old offspring exposed to 400 ppm 

manganese. Decreased fertility was seen upon mating the offspring receiving the 3550 ppm dose 

(Laskey et al. 1982). 

To determine the effect of excess aluminum on manganese deficiency in developing mice, dams 

were fed manganese deficient diets with or without hi& aluminum throughout gestation and 

lactation. Offspring exposed to manganese deficient diets had growth retardation and reduced 

forelimb and hindlimb grip strength as compared to controls on postnatal day 24. These effects were 

exacerbated by high aluminum (Golub et al. 1991). 

3.15 Reference Dose 

3.15.1 Subchronic: drinking water 

ORAL RtD,: 0.005 mgkg/day (EPA 1994) 


NOAEL: 0.005 mgkg/day 

Subchronic: diet 

ORAL RfD,: 0.14 mgkglday @PA 1994) 

UNCERTAINTY FACTOR: 1 

PRINCIPAL STUDIES: The same studies and comments apply for both the subchronic and 

chronic RfD derivations. Section 3.1.5.2 provides further discussion.

6 

3.1.5.2 Chronic: drinking water 

ORAL RfD,: 0.005 mg/kg/day (EPA 1995) 


MODIFYING FACTOR: 1 

NOAEL: 0.005 mg/kg/day 

CONFIDENCE: 

Study: Low-to-medium 

Data Base: Medium-to-low 

RfD: Medim-to-low 


PRINCIPAL STUDY: Kondakis et al. 1989 

Chronic: diet 

ORAL me: 0.14 mgkg/day (EPA 1995) 


MODIFYING FACTOR 1 

NOAEL: 0.14 mgkg/day 

LOAEL: none 

CONFIDENCE: 

Study: High 

Data Base: Medium 

RfD: Medium 


PRINCIPAL STUDIES: Schroeder et al. 1966, WHO 1973, NRC 1989 

COMMENTS: Because of the greater bioavailability of manganese fiom water, a separate RfD 

for water was calculated. The major advantage of the Kondakk et al. (1989) study is that it 

examined a sensitive human subpopulation exposed for a lifetime; however, confidence is low 

in the study because of lack of data on concumnt dietary manganese. The dietary RfD is based 

on a composite of data fiom the three! principal references. The UIlCertainty factor of 1 was

7 

applied because the information used to determine the RfD was taken from large adult human 

populations, and the most sensitive subpopulation was represented within the group. Humans 

exert an efficient homeostatic control over manganese. It is important to recogmze that 

manganese is an essential human nutrient (EPA 1995). The most current IRIS records (EPA 

1995) indicate that the RfDs are pending change. 



3.2.1.1 Human 

The inhalation of manganese oxide fumes, such as could be produced from welding, can result 

in chills, fever, sweating, nausea, and coughmg. These influenza-like symptoms begin 4-12 hours 

after exposure and diminish after 24 hours. This “metal fume fever” usually causes no permanent 

damage unless exposure is continually repeated (Proctor et al. 1988). 


Intratracheal injections of manganese oxides (particle size

8 


3.2.2.1 Human 

Most human studies on manganese toxicity are epidemiological studies on populations exposed 

to manganese compounds in dust particles. Individuals in these studies were exposed to manganese 

for less than one year to more than 20 years. The primary Merence between subchronic and chronic 

central nervous system symptoms is the reversibility of the early subchronic symptoms. 

An overlap exists between the inhalation and oral routes since manganese contained in larger 

particle sizes (greater than about 2.5 pm) is deposited in the tracheobronchial and extrathoracic 

regions and is cleared by the action of the cilia into the gastrointestinal tract. It is not surprising that 

the same central nervous system symptoms are seen with both routes (see Sect. 3.1.2.1). Respiratory 

system effects, nasal irritation, colds, bronchitis, and pneumonia are increased in exposed 

populations, and these symptoms can be seen following subchronic and chronic exposures (see Sect. 

3.2.3 for individual experiments). 


Dose-dependent hyperplasia of the peribronchial tissue, pulmonary emphysema and atelectasis, 

exudate in the bronchioles, and thickening of the alveolar wall were observed in rhesus monkeys 

exposed 22 hours/day for 10 months to manganese at concentrations of 0,0.7 or 3.0 mg/m3 (given 

as manganese dioxide dust) (Suzuki et al. 1978). 


3.23.1 Human 

A study was conducted by Roels et al. (1987) in which 141 males occupationally exposed to 

manganese dioxide, tetroxide, sulfate, carbonate, and nitrate were compared to a group of 104 males 

who were not occupationdly exposed to these compounds. The groups were matched in background 

environmental factors, work load, and shift responsibilities. The duration of employment ranged fiom 

1 to 19 years with a mean of 7.1 years. A higher frequency of coughs, dyspnea during exercise, 

episodes of acute bronchitis, and altered lung ventilatory paramem were found in the exposed 

group. SiMcant alterations were also found in visual reaction time, audioverbal short-term 

memory, eye-hand coordination, and hand steadiness in the exposed group. A LOAEL of 0.34 mg/m3 

was determined from these observations. 

A more recent study by Roels et al. (1992) examined 92 male workers exposed to manganese 

dioxide dust in a battery plant. Exposure time ranged fkom 0.2-17.7 years (mean, 5.3 years) and 

exposure concentrations of respirable and total dust were 0.215 mg/m3 and 0.948 mam, 

respectively. No differences were found in the manganese-exposed workers for respiratoxy or 

neurological symptoms, spirometric measurements, hormone levels, or calcium metabolism as 

compared to unexposed controls. However, visual reaction time, hand-eye coordination, and hand 

steadiness were sipficantly impaired. 

A group of 60 welders from three separate plants who were exposed to manganese fumes were 

studied by Chandra et al. (1981). The mean concentrations of manganese were 0.31,0.57 and 1.74 

mg/m3 measured in the air from plants 1,2, and 3, respectively. Frequent colds, coughmg, and fever 

were reported by the individuals fiom plant 1; workers from all three plants reported insomnia. Signs 

of neurological e ffi measured by “brisk, deep reflexes” in the legs andor arms were seen in 25,

9 

50, and 45% of workers in plant 1,2 and 3, respectively. Tremors were ais0 observed in one worker 

in plant 1 and four workers in plant 2. Increased urinary manganese and serum calcium levels were 

also seen in workers from all plants. A LOAEL of 0.11 mg/m3 was determined from the mean 

exposure at plant 1. 

A similar study was reported by Iregren (1990) in which 15 workers fiom each of two Swdsh 

foundries were studied for manganese exposure. The inhalation exposure concentration varied from 

0.02 to 1.4 mg/m3, and the time of exposure varied from 1 to 35 years. A reference group of two 

unexposed workers from the same geographic area was matched (age, type of work) to each exposed 

worker. Neurobehavioral function was evaluated by eight computerized tests fiom the Swdsh 

Performance Evaluation System and two manual dexderity tests. Signtficant differences were found 

between the exposed and unexposed groups in simple reaction time and manual dexterity (finger 

tapping speed). A concentration-response relationship, however, could not be established. A LOAEL 

of 0.09 mg/m3 was determined for the neurologml effects. 

Alloy workers with an average of 16.7 years of work in a ferromanganese and silicomanganese 

alloy facility were compared to matched controls for symptom reporting and on a series of nervous 

system function tests (Mergler et al. 1994). Respirable manganese levels in the alloy plant at 

stationary sampling sites averaged 0.122 mg/m’. Alloy workers had sipficantly higher manganese 

blood levels than the control group (1.12 pg/lOO mL vs 0.72 &lo0 mL). Symptoms reported more 

frequently for the alloy workers included fatigue, adverse emotional state, memory loss, amtion 

difficulties, nightmares, sweating without physical exertion, difficulty maintaming an erection, and 

tinnitus. Overall the alloy workers also performed more poorly than the controls on motor function 

tests, optic spatial organization of movement, dynamic organization, cognitive flexibility, and 

olfactory perception threshold. 

Respiratory effects, including an increased incidence of colds, bronchitis, and pneumonia, have 

been reported in at least four other human studies. It is believed unlikely that exposure to manganese 

is solely responsible for the increased respiratory symptoms. A decrease in resistance to infectious 

agents, possibly as a result of a weakened immune response, is probably a contributing factor (EPA 

1995). 

3.23.2 Animal 

Groups of 4 female rhesus monkeys were exposed to 0 or 30 mg/m3 manganese 6 hours/day, 5 

dayslweek for 2 years. Sigruficantly decreased dopamine concentrations were observed in the caudate 

and globus pallidus regions of the brains of treated monkeys. No behavioral abnormalities were noted 

during routine (cage side) observations. Nemobebvioral dyshction was not specifically tested 

(Bird et al. 1984). 



The same population of male factory workers studied by Roels (see Sect. 3.2.3.1) was also 

stded by Lauwerys et al. (1985) for reproductive effects. The results of a fertility questionnaire 

indicated that fewer children were born to workers exposed to manganese dust betwem the ages of 

16-25 and 26-35. The same LOAEL of 0.34 mdm3 was calculated for reproductive effects. 

3.2.4.2 Animal

10 

Decreased body weight and impaired neurobehavioral performance (balance and coordmation) 

were seen in the offspring of female M CR mice that were exposed to 48.9 mg manganese/m3 

7 hourdday for 5 daydweek. Exposure was initiated 4 months prior to breeding and continued 

through day 18 of gestation. Similar neurobehavioral responses were obtained from offspring of 

unexposed mice which were fostered to manganese-exposed females during lactation (Massaro et al. 

1980). 

3.2.5 Reference ConcentratiodDose 

3.2.5.1 Subchronic 

A subchronic RfC for manganese has not been derived (EPA 1994). 

3.2.5.2 Chronic 

INHALATION RfC: 0.00005 mg/m’ (EPA 1995) 


MODIFYING FACTOR 1 

NOAEL: none 

LOAEL: 0.05 mg/m3 

CONFIDENCE: 

Study: Medium 

Data Base: Medium 


PRINCIPAL STUDIES: Roels et al. 1987,1992 

COMMENTS: The LOAEL was derived from an occupational-lifetime integrated respirable 

dust concentration of manganese dioxide expressed as mg manganese/m3 x years. Effects were 

based on impairment of neurobehavioral function as a result of occupational exposure to 

manganese dust. The uncertainty factor accounts for the use of a LOAEL (lo), the protection 

of sensitive individuals (lo), and data base limitations reflecting both the less-than-chronic 

exposure time and the lack of developmental data, as well as potential but unquantdkd 

dif€erences in the toxicity of Merent forms of manganese (1 0).

11 



3.3.1.1 Human 

Taylor and Price (1982) reported a clinical case of acute pancreatitis that resulted from 

hemdalysis of a patient with a solution contarninated with manganese. Symptoms, which appeared 

within one hour from the start of dialysis, included severe vomitmg, epigastric pain, increased heart 

rate, and increased blood pressure. The dialysis was discontinued after 30 minutes. The dialysate was 

found to contain 715 pmoVL manganese sulfate. The diagnosis of acute pancreatitis was made the 

next day (day 2). The patient suffered fiom a high fever7 persistent abdominal pain, weakness, and 

a drop in serum calcium fiom day 2 through day 4. A high leukocyte count persisted past day 14 after 

which it returned to normal. The serum manganese levels were found to be 4.55, 1.71, and 

0.65 pmol/L on days 2,3, and 6, respectively. The patient was discharged free fiom abdominal pain 

and on a normal diet 3 1 days after manganese exposure. 


A number of experiments have indicated that manganese is considerably more toxic by injection. 

LD,, values of 121 and 255 mgkg in mice were determined for manganese dichloride given by 

intraperitoneal and intramuscular injections, respectively. LDso values for the tetrahydrate are 190 

mag for intraperitoneal injection in mice and 138 mgkg for intraperitoneal injection in rats. The 

latter value can be compared to the LD, of 1484 mgkg for oral exposure in rats as discussed in Sect. 

3.1.1.2 (Lew~s and Sweet 1984). 

Histological changes in the lungs of rats have been reported to occur within minutes after the 

injection of 40 mgkg of manganese dioxide. An injection of manganese dioxide followed by a like 

injection of manganese dichloride resulted in severe congestion and pulmonary edema that was often 

fatal (Stokinger 1981). 

Brain damage has been induced in rats by direct injection of manganese into the brain (Sloot et 

al. 1994). Intrastriatal injections of manganese chloride produced dosedependent (0.05-0.8 pmol) 

dopamine depletion and timedependent (0.4 mol) calcium accumulation. 

Sprague-Dawley or Osborne-Mendel rats injected intraperitoneally with 40 mg manganesekg 

(given as manganese dichloride) became hyperglycemic within 2 hours. The increase in blood sugar 

was accompanied by a decrease in plasma insulin. Manganese was rapidly concentrated in the liver 

(45 minutes) and the pancreas (15 minutes). Blood sugar values returned to control levels within 8 

hours after the injection (Baly et al. 1985). 

Intravenous injection of manganese dichloride to male New Zealand white rabbits caused a 

dose-responsive decrease in mean arterial pressure (3-100 pwg), an increase in heart rate (0.3-100 

pM/kg), and alterations in the electrocardiogram. These effects were not attenuated by 

coadministration of CaC1, (Lee 1993).

12 


3.3.2.1 Human 

Information on the subchronic toxicity of manganese in humans by other routes of exposure was 

unavailable. 

33.2.2 Animal 

Intraperitoneal injections to mice of 5 mg manganese chloridekglday, 5 daydweek, for 9 weeks 

did not alter the cholinergic muscarinic receptor density or the dwociation constant of 'Hquinuclidinyl 

benzilate in the striatum, fiontal cortex, or hippocampus brain regons (Villalobos et 

al. 1994). 


Information on the chronic toxicity of manganese in humans or animals by other routes of 


3.3.4 Developmental Toxicity 


Information on the developmental toxicity of manganese in humans by other routes of exposure 


3.3.4.2 Animals 

Swiss mice were given doses of manganese (II) chloride tetrahydrate by subcutaneous injection 

at doses of 0,2,4, 8, or 16 mg/kglday on gestation days 6-15. Maternal body weight gain and feed 

consumption were sigdicantly reduced in the 8 and 16 mg/kg groups as compared to controls. An 

increase was observed in the number of late resorptions in the 4,8, and 16 mgkg groups; a reduction 

in fetal body weights and an increase in delayed ossification of the bones of the skull and sternebra 

were observed in fetuses fiom the 8 and 16 mag groups (Shchez et al. 1993). 



3.4.1.1 Primary target(s) 

1. Central nervous system: Initial symptoms include headache, insomnia, disorientation, 

speech disturbances, memoxy loss, and acute anxiety. Prompt removal of the affected 

person from the manganese source usually results in reversal of most of these symptoms. 

Continued subchronic to chronic expo- can result in motor difficulties, tremors, 

difficulty walking, and exaggerated reflexes similar to Parkinsonism. These later stages 

of toxicity are apparently secondary effects and are not reversible although the manganese 

concentrations in the tissues decrease to normal levels upon removal from the manganese 

source.

13 

2. Reproductive system: Chronic feeding studles in rats have kdicated decreased fertility 

results fiom chronic manganese exposure. Similar subchronic studles in monkeys have 

shown degenerative changes in the seminiferous tubules. 

3.4.1.2 Other targets 

Blood: An iron-responsive anemia can occur with orally-induced manganese toxicity 

possibly due to an interference with intestinal iron absorption by excess manganese. 


3.4.2.1 Primary target@) 

1. Central nervous system: The same symptoms are seen as with acute to chronic oral 

exposure (Sect. 3.4.1.1). Since individuals are occupationally exposed to dust containing 

manganese during mining and manufacturing and to metal fumes during welding, 

inhalation is by far the most common route of exposure for manganese toxicity. 

2. Respiratory system: Subchronic to chronic symptoms include an increased incidence of 

colds, bronchitis, and pneumonia. Dyspnea during exercise, decreased vital capacity, and 

decreased forced expiratory vital capacity have also been reported. 

3. Reproductive system: Decreased f dty has been seen in subchronic to chronic human 

inhalation studies. 

3.4.2.2 Other targets 

1. Pancreas: Manganese is known to concentrate in the pancreas and alter insulin production 

in rats. Acute pancreatitis has been reported in humans following accidental intravenous 

exposure. 

2. Immune system: Evidence in animal studies suggests that acute manganese exposure by 

inhalation results in an immunosuppression. The observed increase in the incidence of 

respiratory dections with subchronic to chronic human exposure to manganese 

substantiates this observation. 



Information on the carcinogenicity of manganese by the oral route in humans or animals was 

unavailable. 


Information on the carcinogenicity of manganese by the inhalation route in humans or anrmals 

was unavailable.

14 



Information on the carcinogenicity of manganese by other routes of exposure in humans was 

unavailable. 


DBA/1 mice were injected subcutaneously or intraperitoneally with 0.1 mL, of a 1% aqueous 

solution of manganese chloride twice weekly for 6 months. An increased number of lymphosarcomas 

developed in the treated animals compared with the controls. The tumor incidendnumber of animals 

in the dose group was: 24/36, 16/39, and 16/66 for the subcutaneous, intraperitoneal, and water 

control groups, respectively. The tumors appeared earlier in the treated groups as well 

@hPaolo 1964). 

Groups of 10 male and 10 female each of strain A Strong mice were injected intraperitoneally 

with 0,6,15, or 30 mgkg manganous sulfate 3 timeslweek for 7 weeks. The ammals were sacrificed 

and examined for tumors after 30 weeks. An increase in the average number of pulmonary adenomadmouse 

was apparent at the mid and high doses but the increase was significant only at the high 

dose (Stoner et al. 1976). 

F344 rats and female Swiss mice were injected intramuscularly with manganese powder and 

manganese dioxide (10 mg each). The F344 rats were also injected with manganese” 

acetyl-acetonate. No differences were seen in tumor incidence between treated and control animals 

with manganese powder or manganese dioxide; however, there was a si@icant increase in injection 

site fibrosarcomas with the manganese” acetylacetonate (Furst 1978). 

Witschi et al. (1981) injected female A/J mice intraperitoneally with 80 mag 

methylcyclopentadienyl manganese tricarbonyl. Cell proliferation was produced in the lungs but no 

increase in tumor incidence was seen. 

4.4 EPA WEIGHT-OF-EVIDENCE 

Classification D-Not classifiable as to human carcinogenicity @PA 1995) 

Basis-Existing studies are madequate to assess the carcinogenicity of manganese. 


No slope factors for carcinogenicity have been calculated.

15 

5. REFERENCES 

Adkins, B., Jr., G. H. Luginbuhl, F. J. Miller, and D. E. Gardner. 1980. Increased pulmonary 

susceptibility to streptococcal infection following dation of manganese oxide, Environ. Res. 

23: 110-120. 

Baly, D. L., B. Lonnerdal, and C. L. Keen. 1985. Effects of high doses of manganese on 

carbohydrate homeostasis, Toxicology Letters 25: 95-102. 

Bird, E. D., A. H. Anton, and B. Bullock. 1984. The effect of manganese inhalation on basal ganglia 

dopamine concentrations in rhesus monkeys, Neurotoxicology 5( 1): 59-66. 

Brock, A. A., S. A. Chapman, E. A. Ulman, and G. Wu. 1994. Dietary manganese deficiency 

decreases rat hepatic arpase activity, J. Nutr. 124:340-344. 

Chandra, S. V., G. S. Shukla, R. S. Strivastava, H. Singh and V. P. Gupta. 1981. An exploratory 

study of manganese exposure to welders, Clin. Toxicol. 18: 407-416. 

Chirase, N. K., D. P. Hutcheson, G. B. Thompson, and J. W. Spears. 1994. Recovery rate and plasma 

zinc and copper concentrations of steer calves fed organic and inorganic zinc and manganese 

sources with or without injectable copper and challenged with infectious bovine rhinotracheitis 

virus,J. him. ScI. 72:212-219. 

DiPaolo, J. A. 1964. The potentiation of lymphosarcomas in mice by manganous chloride, Fed. 

Proc. 23: 393. 

EPA. 1984. Health Assessment Document for Manganese, prepared by the Office of Health and 

Environmental Assessment, Environmental Criteria and Assessment Office, Research Triangle 

Park, NC.EPA 600/8-83-013F. 

EPA. 1989. Reportable Quantity Document for Manganese, prepared by the Office of Health and 

Environmental Assessment, Environmental Criteria and Assessment Office, Cincinnati, OH for 

the Office of Solid Waste and Emergency Response, Washington, DC. 

EPA. 1994. Health Eflects Assessment Summary Tables FY-I 994 Annual, prepared by the Office of 

Research and Development, Environmental Criteria and Assessment Office, Cincinnati, OH for 

the Office of Emergency and Remedial Response, Washington DC. NTIS PB94-921199. 

EPA. 1995. Integrated Risk Information System (IRIS). Health Risk Assessment for Manganese, on 

line, Office of Health and Environmental Assessment, Environmental Criteria and Assessment 

Office, Cincinnati, OH. 

Furst, A. 1978. Tumorigenic effect of an organomanganese compound on F344 rats and Swiss albino 

mice: Brief communication, J. Natl. Cancer Inst. 60: 1171-1 173. 

Golub, M. S., B. Han, and C. L. Keen. 1991. AI and Mn: interactions in adult and developing mice, 

Teratology 43:490.

16 

Gupta, S. K., R C. Murthy and S. V. Chandra. 1980. Neuromelanin in manganese-exposed primates, 

Toxicol. Lett. 6(1): 17-20. 

Holbrook, C. J. Jr., M. E. Washington,H. B. hake and P. E. Brubaker. 1975. Studies on the 

evaluation of the toxicity of various salts of lead, manganese, platinum, and palladun, Environ. 

Health Persp. 10: 95-101. 

Iregren, A. 1990. Psychologd test performance in foundry workers exposed to low levels of 

manganese, Neurotox. Teratol. 12: (in press). 

Kawamura, R, H. Ikuta, S. Fukuzumi, et al. 1941. Intoxication by manganese in well water, Kitasato 

Arch. &p. Med. 18: 145-169. 

Kern, C. L. and R M. Leach. 1988. Manganese, In: Handbook on Toxiciry of Inorganic Compounds, 

eds. H.G. Seiler and H. Sigel, Marcel Dekker, Inc. pp. 405415. 

Komura, J. and M. Sakamoto. 1992. Effects of manganese forms on biogenic amines in the brain and 

behavioral alterations in the mouse: long-term oral administration of several manganese 

compounds, Environ. Res. 57:34-44. 

Kondakis, X. G., N. Makris, M. Leotsinidis, M. Prinou and T. Papapetropoulos. 1989. Possible 

health effects of high manganese concentration in drinking water, Arch. Environ. Healrh. 44(3): 

1 75- 1 78. 

Lai, J. C. K., T. K. C. Leung and L. Lim. 1981. Brain regional distribution of glutarmc acid 

decarboxylase, choline acetyltransferase, and acetylcholinesterase in the rat: Effects of chronic 

manganese chloride administration after two years, J. Neurochem. 36(4): 1443-1448. 

Lai, J. C., T. K. Leung, L. Lim, A. W. Chan and M. J. Minsk. 1991. Effects of chronic manganese 

treatment on rat brain regional sodium-potassium-activated and magnesium-activated adenosine 

triphosphatase activities during development, Metab. Brain Dis. 6: 165- 174. 

Laskey, J. W., G. L. Rehnberg, J. F. Hein and S. D. Carter. 1982. Effects of chronic manganese 

(Mn,O,) exposure on selected reproductive parameters in rats, J. Toxicol. Environ. Health. 9: 

677-687. 

Lauwerys, R, H. Roels, P. Genet, et al. 1985. Fertility of male workers exposed to mercury vapor 

or to manganese dust: A questionnaire study,Arn. J. Ind. Med. 7: 171-176. 

Lee, K. C. 1993. Hemodynamic and electrophysiologic effects of manganese independent of calcium 

in anesthetized rabbits, Meth. Find. Erp. Clin. Pharmacol. 15:743-750. 

Leung, T. K. C., J. C. K. Lai, and L. Lim. 1981. The regional distribution of monoamine oxidase 

activities towards Werent substrates: Effects in rat brain of chronic administration of 

manganese chloride and of aging, J. Neurochem. 36(6): 2037-2043. 

Leung, T. K. C., L. Lim, and J. C. K. Lia 1993. Brain regional distributions of monoamine oxidase 

activities in postnatal development in normal and chronically manganese-treated rats, Metab. 

Brain Dis. 8:137-149.

17 

Lewis, R J. and D. V. Sweet, eds. 1984. Regrstry of Toxic Eficts of Chemical Substances, Vol. I, 

U.S. Department of Health and Human Services, Public Health Service, Centers for Disease 

Control, National Institute for Occupational Safety and Health, Cincinnati, OH. 

Massaro, E. J., R B. D'Agostino, C. Stineman, J. B. Marganti, and B. A. Lown. 1980. Alterations 

in behavior of adult offspring of female mice exposed to MnO, dust during gestation, Fed. Proc. 

Fed. Am. SOC. Exp. Biol. 39: 623. 

Mergler, D., G. Huel, R Bowler, A. kegren, S. BBlanger, M. Baldwin, R Tardif, A. Amargiassi, and 

L. Martin. 1994. Nervous system dysfunction among workers with long-term exposure to 

manganese, Environ. Res. 64: 151-180. 

Murthy, R C., R S. Srivastava, S. K. Gupta, and S. V. Chandra. 1980. Manganese induced testicular 

changes in monkeys, Exp. Path. 18: 240-244. 

NRC (National Research Council). 1989. Recommended Dietary Allowances, 9th rev. ed, Food and 

Nutrition Board, National Research Council, National Academy Press, Washington, DC. p. 

230-235. 

Orten, J. M. and 0. W. Neuhaus. 1975. Human Biochemist?y, Ninth Edition, The C.V. Mosby 

Company, St. Louis. pp. 546-547. 

Proctor, N. H., J. P. Hughes, and M. L. Fischman. 1988. Manganese (and Compounds) in Chemical 

Hazard of the Workplace, Second Edition, J.B. Lippincott Company, Philadelphia. pp.307-308. 

Roels, H., R Lauwexys, J. P. Buchet, et al. 1987. Epidemiological survey among workers exposed 

to manganese: Effects on lung, central nervous system, and some biological indices, Am. J. Ind. 

Med. 11: 307-328. 

Roels, H., P. Ghyselen, J. P. Buchet, E. Ceulemans, and R R Lauwexys. 1992. Assessment of 

permissible exposure level to manganese in workers exposed to manganese dioxide dust, Br. J. 

Ind. Med. 49:25-34. 

Shchez., D. J., J. L. Dominge, J. M. Llobet, and C. L. Keen. 1993. Maternal and developmental 

toxicity of manganese in the mouse, Toxicol. Lett. 69:45-52. 

Schroeder, H. A., D, D. Balassa, and I. H. Tipton. 1966. Essential trace metals in man: Manganese, 

a study in homeostasis, J. Chron. Dis. 19: 545-571. 

Shiotsuka, RN. 1984. Inhalation toxicity of manganese &oxide and magnesium oxide-manganese 

dioxide mixture. GRAI. 85(7): 34. 

Sloot, W. N., A. J. van der Sluijs-Gelling and J. B. P. Gramsbergen. 1994. Selective lesions by 

manganese and extensive damage by iron after injection into rat striatum or hippocampus, J. 

Neurochem. 62:205-2 16. 

Stdanger, H. E. 198 1. The Metals, In: Putty's Industrial Hygiene and Toxicology, Vol2A, eds. G.D. 

Clayton and F.E. Clayton, John Wiley & Sons, New York pp. 1749-1769.

18 

Stoner, G. D., M. B. Shimlun, M. C. Troxell, T. L. Thompson, and L. S. Terry. 1976. Test for 

carcinogenicity of metallic compounds by the pulmonary tumor response in strain A mice, 

Cancer Res. 36: 1744-1747. 

Subhash, M. N. and T. S. Padmashree. 1991. Effect of manganese on biogenic amine metabolism in 

regions of the rat brain, Fd. Chem. Toxic. 29579-582. 

Suzuki, Y., N. Fujii, H. Yano, T. Ohkita, A. Ichikawa, and K. Nishiyama. 1978. Effects of the 

lnhalation of manganese dioxide dust on monkey lungs, Tokushima J. Exp. Med. 25: 1 19-125. 

Taylor, P. A. and J. D. E. Price. 1982. Acute manganese intoxication and pancreatitis in a patient 

treated with a contaminated dialysate, Can. Med. Assoc. J. 126: 503-505. 

Testolin, G., S. Ciappellano, A. Alberio, F. Piccinini, L. Paracchini, and A. Jotti. 1993. Intestinal 

absorption of manganese: an in vitro study, Ann. Nutr. Metab. 37:289-294. 

Villalobos, V., F. Castro, E. Bonilla, J. Estdvez, and J.O. Ddvila. 1994. Manganese toxicity: 

muscarinic receptor binding in the mouse braq J. Toxicol. Environ. Health 42: 185-191. 

WHO (World Health Organization). 1973. Trace elements in human num.tion: Manganese. Report 

of a WHO Expert Committee, Technical Report Service, 532, Who, Geneva, Switzerland. 

p. 34-36. 

Witschi, H. P., P. J. Hakkinen, and J.,P. Kehrer. 1981. Mdication of lung tumor development in 

A.J mice, Toxicology. 2 1: 3745.


METHYLENE CHLORIDE 


Prepared by 

Cheryl B. Bast 






Prepared for 



*Managed by Martin Marietta Energy Systems, Inc., for the US. Department of Energy under 

Contract No. DE-AC05-840R21400 

1

This page intentionally left blank 

2


Methylene chloride (CH,Cl,, CAS No. 75-09-2), also known as dichloromethane is a colorless 

volatile liquid with a penetrating ether-like odor. In industry, methylene chloride is widely used as a 

solvent in paint removers, degreasing agents, and aerosol propellants; as a polyurethane foam-blowing 

agent; and as a process solvent in the pharmaceutical industry. The compound is also used as an 

extraction solvent for spice oleoresins, hops, and caffeine (ATSDR, 1989; IARC, 1986). 

Methylene chloride is readily absorbed from the lungs, the gastrointestinal tract, and to some extent 

through the skin. Metabolism of methylene chloride produces CO, and CO, which readily binds with 

blood hemoglobin to form carboxyhemoglobin (CGHb). The primary adverse health effects associated 

with methylene chloride exposure are central nervous system (CNS) depression and mild liver effects. 

Neurological symptoms described in individuals occupationally exposed to methylene chloride included 

headaches, dizziness, nausea, memory loss, paresthesia, tingling hands and feet, and loss of consciousness 

(Welch, 1987). Major effects following acute inhalation exposure include fatigue, irritability, analgesia, 

narcosis, and death (ATSDR, 1989). CNS effects have also been demonstrated in animals following acute 

exposure to methylene chloride (Weinstein et al., 1972; Berger and Fodor, 1968). 

Impaired liver function has been associated with occupational exposure to methylene chloride 

(Welch, 1987). Liver effects have also been documented in a number of inhalation studies with laboratory 

animals. Subchronic exposure of rats, mice, dogs, and monkeys caused mild hepatic effects such as 

cytoplasmic vacuolization and fatty changes (U.S. EPA, 1983; Haun et al., 1972; Weinstein and Diamond, 

1972; Heppel, 1944). Hepatocellular foci, fatty changes, and necrosis were reported following chronic 

inhalation exposure of rats and mice (Nitschke et al., 1986~ N", 1986). Chronic oral exposure to 

methylene chloride via drinking water resulted in histopathological alterations of the liver in rats and mice 

(NCA, 1982, 1983). In addition, inhalation exposure of rats caused nonspecific degenerative and 

regenerative changes in the kidneys (U.S. EPA, 1983; Ham et al., 1972). 

A subchronic and chronic oral reference dose (RfD) of 6E-2 mg/kg/day for methylene chloride has 

been calculated by U.S. EPA (1993a,b). This value is based on a NOAEL of 5.85 mg/kg/day derived 

from a chronic drinking water study with rats (NCA, 1982). This same study was adapted for the 

derivation of the subchronic and chronic reference concentration (RfC) of 3E+O mg/m' (NOAEL, 694.8 

mg/m3) (U.S. EPA, 1993a). 

Studies of workers exposed to methylene chloride have not recorded a significant increase in cancer 

cases above the number of cases expected for nonexposed workers (Heame et al., 1987; Ott et al., 1983~ 

Friedlander et al., 1978). However, long-term inhalation studies with rats and mice demonstrated that 

methylene chloride causes cancer in laboratory animals. Mice exposed via inhalation to high 

concentrations of methylene chloride (2000 or 4000 ppm) exhibited a significant increase of malignant 

liver and lung tumors compared with nonexposed controls (NTP, 1986). Rats of both sexes exposed to 

concentrations of methylene chloride ranging from 500 to 4000 ppm showed increases of benign 

mammary tumors (Nitschke et al., 1988~ NTP, 1986; Burek et al., 1984). An inhalation study with rats 

and hamsters revealed sarcomas of the salivary gland in male rats, but not in female rats or hamsters 

(Burek et al., 1984). Liver tumors observed in rats and mice that ingested methylene chloride in drinking 

water for 2 years provided suggestive evidence of carcinogenicity (NCA, 1982, 1983). Based on 

inadequate evidence of carcinogenicity in humans and on suficient evidence in animals, U.S. EPA 

(1993b) has placed methylene chloride in weight-of-evidence group B2, probable human carcinogen. A 

3

slope factor and unit risk of 7SE-3 (mg/kg/day)-' and 2.1E-7 (pg/L)-', respectively, (U.S. EPA, 1993b) 

was derived for oral exposure to methylene chloride. The inhalation unit risk is 4.7E-7 (pg/m')-' (U.S. 

EPA, 1993b). 

4


Methylene chloride (CH,Cl,, CAS No. 75-09-2), also known as dichloromethane, is a halogenated 

aliphatic hydrocarbon with a molecular weight of 84.94. It is a colorless liquid with a penetrating etherlike 

odor, a boiling point of 39.7SoC, and a density of 1.3348 (2OoC/4OC). It is soluble in about 50 parts 

of water and is miscible with alcohol and ether (Budavari et al., 1989; IARC, 1986). The vapor is not 

flammable and when mixed with air is not explosive (Budavari et al., 1989); however, methylene chloride 

reacts vigorously with some metals. When heated to decomposition, it emits highly toxic fumes of 

phosgene (Sax, 1984). Methylene chloride is not known to occur naturally; it is produced by 

hydrochlorination of methanol or chlorination of methane or methyl chloride. Methylene chloride is 

widely used in a variety of industrial and commercial applications. It is used as a solvent in paint 

removers, degreasing agents, and aerosol propellants; as a polyurethane foam-blowing agent; as a process 

solvent in the pharmaceutical industry; and as an extraction solvent for spice oleoresins, hops, and caffeine 

(ATSDR, 1989; IARC, 1986). 

Human exposures to methylene chloride am highest in occupational settings and near industrialized 

urban areas. Consumers may be exposed to significant amounts of methylene chloride vapor in such 

products as paint strippers and thinners, water repellents, wood stain and varnishes, and spray paint 

(ATSDR, 1989). Most of the methylene chloride released to the environment enters the atmosphere, while 

smaller amounts enter surface water and ground water. The chlorination of drinking water also produces 

methylene chloride. In the atmosphere, reaction with photochemically generated hydroxyl radicals is 

expected to be the predominant removal mechanism. Losses of methylene chloride from water are 

primarily due to volatilization (U.S. EPA, 1989). 


2.1. ABSORPTION 

Humans and animals readily absorb methylene chloride from the lungs and the gastrointestinal tract 

into systemic circulation. The compound is also absorbed to some extent through intact skin (ATSDR, 

1989; U.S. EPA, 1989). DiVincenzo and Kaplan (1981) exposed groups of 4-6 volunteers to 50, 100, 

150, or 200 ppm methylene chloride for 7.5 hours. Pulmonary absorption (measured as concentration in 

expired air) was rapid during the first hour, then began to decrease as steady-state was approached. 

Following cessation of exposure, methylene chloride concentrations in exhaled air dropped rapidly. U.S. 

EPA (1980) reported lung absorption efficiencies of 3 1-75%. The absorption of methylene chloride 

increased with exposure concentration, length of exposure, and activity level. The absorption of methylene 

chloride also appears to be related to degree of obesity in humans angstrom and Bjurstrom, 1977). When 

exposed to 750 ppm for 1 hour, obese subjects absorbed 30% more methylene chloride than lean subjects. 

Studies with rats and mice showed that methylene chloride is almost completely absorbed from the 

gastrointestinal tract of both species following daily gavage treatment with 50 or 200 mg/kg/day (rats) or 

50 or 1000 mg/kg/day (mice) for 14 days (Angel0 et al., 1986a,b). The presence of methylene chloride 

in various tissues of rats following immersion of the tails indicates that the compound can be absorbed 

through the skin (NIOSH, 1976). 

5

2.2. DISTRIBUTION 

Following absorption, methylene chloride concentrations rapidly increase in the blood to reach 

equilibrium levels that depend primarily on exposure concentrations. A fairly uniform distribution to 

heart, liver, and brain is reported (U.S. EPA, 1980). Biopsy and analysis of subcutaneous fat of obese 

and lean human subjects following exposure to 750 ppm methylene chloride for 1 hour showed a 

substantial accumulation in adipose tissue (10.2 and 8.4 mg/kg wet tissue, 1 and 4 hours postexposure, 

respectively). Although the concentrations in fat were slightly lower in the obese, the total amount of 

body fat resulted in greater total accumulation of methylene chloride (Engstrom and Bjurstrom, 1977). 

Methylene chloride crosses the placenta (Anders and Sunram, 1982). The compound has been 

detected in fetuses of pregnant women who had been chronically exposed to methylene chloride in the 

work place. It has also been found in milk of lactating women a few hours into a work shift (U.S. EPA, 

1980). 


Extensive toxicokinetic studies have shown that methylene chloride is metabolized in vivo by two 

pathways: (1) a mixed function oxidase (MFO) pathway mediated by the P-450 system yielding CO and 

CO, and (2) a glutathiondependent (GST) pathway yielding only CO,. Other metabolites of methylene 

chloride include formaldehyde and formic acid (ATSDR, 1989). The detection of formic acid in the urine 

of workers exposed to methylene chloride has led investigators to suggest that methylene chloride is fmt 

metabolized to formaldehyde and then to formic acid (Kulova and Vlask, 1966). The MFO pathway 

is saturable at air concentrations of a few hundred ppm. However, the GST pathway shows no indication 

of saturation at inhaled concentrations up to 10,000 ppm (ATSDR, 1989). Biotransformation of methylene 

chloride occurs primarily in the liver, but also occurs in the lungs and kidneys (NTP, 1986). 

Although some CO is exhaled, a significant amount is involved in the formation of 

carboxymethemoglobin (CO-Hb). The formation of CGHb leads to interference with normal oxygen 

transport capabilities of blood, resulting in oxygen deprivation and secondary toxic effects. Bioconversion 

of CO and formation of CO-Hb continues after exposure (U.S. EPA, 1980). 

2.4. EXCRETION 

Excretion of methylene chloride from the body occurs primarily via expired air from the lungs as 

unchanged parent compound or as CO and CO,, the primary metabolites. The absorbed dose is a major 

determinant of the elimination produm At low exposure concentrations, a large percentage of 

administered methylene chloride is metabolized and eliminated as CO and CO,. At higher concentrations, 

more of the unchanged parent compound is exhaled in expired air (ATSDR, 1989). A small fraction of 

absorbed methylene chloride is also eliminated in the urine. Methylene chloride and formic acid were 

detected in the urine of humans exposed by inhalation to 100 or 200 ppm methylene chloride for 24 hours 

(DiVincenzo et al., 1972). 

6

3. NONCARCINOGENIC HEALTH EFFECTS- 



3.1.1.1. Human 

Information on the acute oral toxicity of methylene chloride in humans was not available. 

3.1.1.2. Animal 

Oral LD,, values for methylene chloride of 2121 mgkg for rats and 1987 mgkg for mice indicate 

that the two species are similarly susceptible to the lethal effects of methylene chloride (ATSDR, 1989). 

3.1.2. Subchronic Toxicity 

3.1.2.1. Human 

Information on the subchronic oral toxicity of methylene chloride in humans was not available. 

3.1.2.1. Animal 

No adverse effects on behavior, body weight, survival, or clinical chemistry were observed in male 

and female Wistar rats exposed to drinking water containing 125 ppm methylene chloride5 for 3 months. 

Histopathological examination of internal organs revealed no lesions (Bommann and Loeser, 1967). 

Minor hematological changes and clinical chemistry parameters that reflected impaired liver function were 

observed in F344 rats and B6C3F, mice exposed to drinking water containing 1500,4500, or 15,000 ppm 

methylene chloride for 90 days (Kirschman et al., 1986). A doserelated decrease of urinary pH was seen 

in all treated groups of rats and increased kidney weights in female rats exposed to the highest dose. 

Some mid-dosed female and high-dosed male and female rats had centrilobular necrosis of the liver. Mild 

centrilobular fatty changes of the liver occurred in mice at 24500 ppm. 


3.13.1. Human 

Infomation on the chronic oral toxicity of methylene chloride in humans was not available. 


Drinking water studies conducted by the National Coffee Association (NCA, 1982, 1983; also 

reported by Serota et al., 1986qb) exposed F344 rats to 0, 5, 125, or 250 mgkglday and B6C3F, mice 

to 0, 60, 125, 185, or 250 mg/kg/day of methylene chloride for 104 weeks. Slight effects on 

hematological parameters and serum chemistry were seen in rats. Treatment-related liver effects, most 

prominently increased foci of cellular alterations and fatty changes, occurred in rats at all doses except 

7

the lowest. In mice, histomorphologic alterations of the liver were observed only in males and females 

receiving the highest dose. 



Information on the developmental and reproductive toxicity of methylene chloride in humans 

following oral exposure was not available. 


Administration of 125 ppm methylene chloride in drinking water for 91 days did not affect the estrus 

cycle or reproduction of male and female rats (Bornmann and Loeser, 1967). 

3.1.5. Reference Dose 

3.1.5.1. Subchronic 

ORAL RfD: 6E-2 mg/kg/day (U.S. EPA, 1993a) 


LOAEL: 52.58 mg/kg/day 


PRINCIPAL STUDY: NCA, 1982 

COMMENTS: The same study applies to the subchronic and chronic RfD. The study is 

described in Section 3.1.3.2. 

3.1.5.2. Chronic 

ORAL RfD: 6E-2 mg/kg/day (U.S. EPA, 1993b) 


LOAEL: 52.58 mg/kg/day 


CONFIDENCE: 

Study: High 

DataBase: Medium 

m: Medium 


PRINCIPAL STUDY: NCA, 1982 

COMMENTS: The same study applies to the subchronic and chronic RfD. The chronic RfD 

was based on a no-observed-adverseffect level (NOAEL) of 5.85 mg/kg/day in male rats 

derived from the 2-year drinking water study described in Section 3.1.3.2. Histopathological 

8

lesions of the liver were seen at 52.58 mg/kg/day which was considered h e lowest-observedadverse-effect 

level (LOAEL). The uncertainty factor includes two factors of 10 for intra- and 

interspecies variability. 

3.2. INHALATION EXPOSURES 


3.2.1.1. Human 

Humans exposed to high concentrations of methylene chloride for short time periods may experience 

central nervous system effects, including narcosis, irritability, analgesia, and fatigue (ATSDR, 1989). 

Human volunteers exposed by inhalation to methylene chloride concentrations exceeding 300 ppm for 4 

hours exhibited decreased auditory and visual firnctions; exposure to approximately 800 ppm for 4 hours 

resulted in impaired performance of most psychomotor functions (Winneke, 1974). Exposure to 25,000 

ppm for 2 hours was not lethal. Exposure to 7,200 ppm caused paresthesia of the extremities after 8 

minutes, acceleration of the pulse after 16 minutes, and congestion of the head, a sensation of heat, and 

slight irritation of the eyes during the first 20 minutes. At 2300 ppm, nausea occd der a 30-minute 

exposure (Sax, 1984). Exposure to very high (unspecified) concentrations of methylene chloride has lead 

to rapid unconsciousness and death, but prompt removal from exposure usually leads to complete recovery 

(Torkelson and Rowe, 1981). Accidental deaths have been reported as a result of acute methylene 

chloride exposure during paint stripping operations (Stewart and Hake, 1976; Bonventre et al., 1977). In 

f d poisonings, cardiac injury and heart failure have been reported as cause of death (U.S. EPA, 1980). 

33.13. Animal 

Inhalation LC,, values for methylene chloride listed by ATSDR (1989) range from 14,155 ppm (6- 

hour exposure) to 26,710 ppm (20-minute exposure) for mice. The LC,, for guinea pigs exposed for 6 

hours is 11,600 ppm. Short-term inhalation studies showed that exposure to high concentrations of 

methylene chloride produces central nervous system effects in several species. Slight narcosis was seen 

in dogs exposed to 6000 ppm after 2 hours, in guinea pigs after 2.5 hours, and in rabbits and cats after 

3-4 hours (Weinstein et al., 1972); deep narcosis occurred in rats exposed to 16,000-18,000 ppm for 6 

hours merger and Fodor, 1968). 


333.1. Human 

Unspecified neurological symptoms were reported by a group of 46 male workers who had been 

exposed to methylene chloride concentrations ranging from 75 to 100 ppm (duration of exposure not 

reported) (Cherry et al., 1980). A follow-up study on 29 of the exposed workers provided no evidence 

of neurological or behavioral impairment or cardiac abnormalities. Exposure of 56 workers to a 9:l 

methylene ch1oride:methanol atmosphere caused mental and physical tiredness and sleepiness. These 

parameters were significantly different only for the morning shift and correlated with blood CO-Hb levels 

at the end of the shift (Cherry et al., 1983). Welch (1987) reported that workers from various industries 

experienced a variety of CNS effects, such as headaches, dizziness, nausea, memory loss, paresthesia, 

tingling hands and feet, and loss of consciousness. Workers were exposed to methylene chloride levels 

measured up to 100 ppm and duration of exposure was 6 months to 2 years. 

9

Ott et al. (1983a) found no excess mortality from circulatory system diseases among employees of 

a fiber production plant that used methylene chloride as a solvent. Workers were exposed for at least 

three months to a time-weighted-average concentration of 140 ppm methylene chloride. In a related study 

on cardiac function, Ott et al. (1983b) examined EKGs of 50 workers from two fiber-producing plants. 

Data from the plant where exposure concentrations ranged from 60-474 ppm (time-weighted-average) were 

compared with data from a similar plant not using methylene chloride. No significant changes in 

ventricular or supraventricular ectopic activity, nor ST-wave segment depression were associated with 

exposure to methylene chloride. 

A case of hepatitis was reported in a worker who had used methylene chloride in combination with 

other solvents. Although exposure levels were not reported, methylene chloride levels in the serum were 

significantly higher than those reported for other solvents. Several workers exposed to solvents in similar 

work environments had abnormal liver function tests (Welch, 1987). 

3.2.2.2. Animal 

In early experiments, Heppel et al. (1944) exposed rats, rabbits, and guinea pigs to 5000 ppm 

methylene chloride, 7 hodday, 5 daydweek for up to 6 months. Decreased growth in guinea pigs was 

the only observed adverse effect. Exposure to 10,000 ppm, 4 hodday, 5 daydweek for up to 8 weeks 

caused fatty liver changes in guinea pigs and dogs, but no adverse effects in rats and rabbits. 

A number of subchronic inhalation experiments were initiated due to a concern of potential exposure 

of astronauts to methylene chloride vapors emanating from materials used in spacecrafts. A summary of 

these studies was presented by U.S. EPA (1983). Mice exposed to 25 or 100 ppm methylene chloride 

continuously for 14 weeks had increases in spontaneous motor activity and at the lower concentration but 

not at the higher concentration. Rats subjected to the same exposure protocol had nonspecific renal 

tubular degeneration and regeneration and hepatic fatty changes and cytoplasmic vacuolization at both 

exposure levels. Exposure to the same concentrations produced increased carboxymethemoglobin levels 

in monkeys at both concentrations and in dogs only at 125 ppm. Exposure of the same four species to 

1000 or 5000 ppm resulted in signs of severe toxicity at 5000 ppm: narcosis was observed during the first 

24 hours and pronounced lethargy for the remainder of the exposure period. All rats survived, but high 

rates of mortality occurred in mice, dogs, and monkeys. Common findings in all species were liver and 

kidney damage. 

Exposure of ICR mice to 100 ppm methylene chloride for 10 weeks produced centrilobular hepatic 

fat accumulation and decreased glycogen levels in mice (Weinstein and Diamond, 1972). Cytoplasmic 

vacuolization and fatty liver changes were also reported in rats and dogs exposed to 25-100 ppm 

methylene chloride for 100 days. Rats additionally exhibited nonspecific renal tubular degenerative and 

regenerative changes (Haun et al., 1972). 

10


3.23.1. Human 

Epidemiological studies have not shown adverse effects in humans occupationally exposed to 

methylene chloride. A study of male workers at Eastman Kodak exposed primarily to methylene chloride 

concentrations of 30-120 ppm methylene chloride for up to 30 years did not reveal any indication of 

increased risk of death fiom circulatory disease or other causes compared with nonexposed workers or the 

general population (Friedlander et al., 1978). 


Nitschke et al. (1988a) exposed male and female Sprague-Dawley rats by inhalation to 0, 50,200, 

or 500 ppm methylene chloride, 6 hodday, 5 daysfweek for 2 years. An increased incidence of 

hepatocellular vacuolization was observed in male and female rats exposed to 500 ppm; female rats also 

had an increased incidence of multinucleated hepatocytes. In another long-tern bioassay, increased 

incidences of hemosiderosis, cytomegaly, cytoplasmic vacuolization, necrosis, granulomatous 

inflammation, and bileduct fibrosis were observed in the livers of treated male and female F344/N rat 

and B6C3FI mice (NTP, 1986). The exposure concentrations were 1000,2000, or 3000 ppm for rats and 

2000 or 4000 ppm for mice. 



A case-control study on possible causes of spontaneous abortions among 44 women 

working in the Finnish pharmaceutical industry showed an increased risk associated with exposure to 

several chemicals and solvents, including methylene chloride (Taskinen et al., 1986). 


Nitschke et al. (1988b) evaluated reproductive parameters in F344 rats following exposure to 

concentrations of 0, 100, 500, or 1500 ppm methylene chloride over the course of two successive 

generations. No adverse effects on fertility, litter size and neonatal growth, or survival were noted in 

animals exposed to methylene chloride in either the F, or F, generation. Similarly, there were no 

treatment-related gross pathologic observations in either the F, or F, adults or the F, or F, weanlings. 

In a 2-year NTP (1 986) study, dose-related increases were observed in the incidences of testicular 

atrophy in male B6C3FI mice exposed to concentrations of methylene chloride ranging h m 1000 to 4000 

ppm, and increased incidence of ovarian and uterine atrophy was seen in female mice exposed to 2000 

or 4000 ppm. 

3.2.5. Reference Concentration 


INHALATION W: 3E+O mg/m3 (U.S. EPA, 1993a) 

NOAEL: 694.8 mg/m3 

11


PRINCIPAL STUDY: Nitschke et al., 1988a 

COMMENTS: The same study applies to the subchronic and chronic RfC. The study is described 

in Section 3.2.3.2. 


INHALATION RfC: 3E+0 mg/m3 (U.S. EPA, 1993a) 

NOAEL: 694.8 mg/m3 


PRINCIPAL STUDY: Nitschke et al., 1988a 

COMMENTS: A 2-year inhalation study with rats served as the basis for the RfC. The RfC 

was based on a NOAEL of 200 ppm (694.8 mg/m3) and liver toxicity seen at 500 ppm (1737 

mg/m3) as the critical effect. The uncertainty factor includes two factors of 10 for intra- and 

interspecies variability. 



33.1. Humans 

Dennatitis has been reported in individuals exposed to methylene chloride while using paint remover 

formulations (Torkelson and Rowe, 1981). 

333. Animals 

For mice, the subcutaneous and intraperitoneal LD,,, values for methylene chloride are 6452 and 

1987 mgkg, respectively (Kutob and Plaa, 1962; Klaassem and Plaa, 1966). Repeated dermal contact with 

methylene chloride, if allowed to evaporate, is mildly irritating to the skin of rabbits (Torkelson and Rowe, 

1981). 

333. Subchronic Toxicity 

Momation on the subchronic toxicity of methylene chloride by other mutes of exposure in humans 

or animals was not available. 

333. Chronic Toxicity 

Information on the chronic toxicity of methylene chloride by other routes of exposure in humans or 

animals was not available. 

. 

12


Information on the developmental or reproductive toxicity of methylene chloride by other routes of 

exposure in humans or animals was not available. 

3.4. TARGET ORGANS/CFUTICAL EFFECTS 

3.4.1. Oral Exposures 


Liver: Subchronic and chronic exposure of aninals to methylene chloride in drinking water 

has produced changes in clinical chemistry parameters suggesting impaired liver function, 

centrilobular fatty changes, and necrosis. 

3.4.13. Other Target O&UIS 

Kidneys: Increased kidney weights and decreased urinary pH suggestive of renal effects were 

observed in animals subchronically exposed to methylene chloride in drinking water. 

3.43. Inhalation Exposures 


1. Central nervous system: Neurological symptoms including headaches, dizziness, nausea, 

memory loss, paresthesia, tingling hands and feet, and loss of consciousness were reported in 

workers subchronically exposed to methylene chloride. Major effects following acute exposure 

include fatigue, irritability, analgesia, narcosis, and death. CNS effects have also been 

demonstrated in animals following acute exposure. 

2. Liver: Chronic inhalation exposure of animals has produced hemosiderosis, cytomegaly, 

cytoplasmic vacuolization, necrosis, inflammation, and bile-duct fibrosis in animals. Fatty liver 

changes and cytoplasmic vacuolization were reported in subchronic studies. Impaired liver 

function has been associated with occupational exposure to methylene chloride. 

3. Kidneys: Subchronic inhalation exposure of animals has produced nonspecific renal tubular 

degenerative and regenerative changes. 

3.4.2.2. Other Target Organs 

Reproduction: An increased risk of spontaneous abortions has been associated with 

occupational exposure to various chemicals and solvents, including methylene chloride. 

Chronic exposure of animals to methylene chloride has resulted in testicular atrophy in males 

and in uterine and ovarian atrophy in females. 

3.43. Other Routes of Exposure 

Skin: Dermal contact has produced skin irritation. 

13




Information on the carcinogenicity of methylene chloride in humans following oral exposure was 



In drinking water studies sponsored by the National Coffee Association (NCA, 1982, 1983), F344 

rats were administered 0, 5, 50, 125, or 250 mg/kg/day and B6C3F, mice were administered 0, 60, 125, 

185, or 250 mg/kg/day of methylene chloride for 104 weeks. A statistically significant (p

Another long-term inhalation study of methylene chloride exposed Sprague-Dawley rats and Syrian 

Golden hamsters to 0, 500, 1500, or 3500 ppm methylene chloride, 6 hoursjday, 5 daydweek for 2 years 

(Burek et al., 1984). Reduced survival was seen in female rats exposed to the highest concentration. 

Female rats showed a dose-related statistically nonsignificant increase in the number of benign mammary 

tumorsht. A similar response was seen in male rats, but to a lesser degree. Male rats exposed to 3500 

ppm also had a statistically significant (p

4.5. CARCINOGENICITY SLOPE FACTORS 

4.5.1. Oral 

SLOPE FACTOR: 7.5E-3 (mg/kg/dayy' (U.S. EPA, 1993b) 

UNIT RISK 2.1E-7 (&IJ' (US. EPA, 1993b) 

PFUNCIPAL STUDY: NTP, 1986; NCA, 1983 

COMMENT: The slope factor is an arithmetic mean of slope factors derived from the NTP 

(1986) and the NCA (1983) data. The use of liver tumor data from the NTP inhalation 

bioassay was considered valid since methylene chloride is rapidly absorbed following either 

inhalation or ingestion (U.S. EPA, 1993b). 

4.5.2. Inhalation 

UNIT RISK: 4.E-7 (pg/m')-' (U.S. EPA, 1993b) 

PRINCIPAL STUDY: NTP, 1986 


COMMENT: The unit risk incorporates information on pharmacokinetics and metabolism of 

methylene chloride. 

16

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Angelo, M.J., A.B. Pritchard, D.R, Hawkins, et al. 1986b. The pharmacokinetics of dichloromethane. 

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Bonventre, J., D. Brennan, D. Juson, et al. 1977. Two deaths following accidental inhalation of 

dichloromethane and 1,1,2-trichloroethane. J. Anal. Toxicol. 1: 158-160. (Cited in ATSDR, 1989) 

Bornmann, G. and A. Loeser. 1967. Zur Frage einer chronisch-toxischen Wirkung von Dichloromethan. 

Z. LebensmAJntersuch. Forsch. 136: 14-18. (Cited in U.S. EPA, 1989) 

Budavari, S., M.J. O'Neil and A. Smith (Eds.) 1989. The Merck Index: An Encyclopedia of Chemicals, 

Drugs, and Biologicals, 11th ed. Merck and Co., Rahway, NJ, p. 5979. 

Burek, J.D., K.D. Nitschke, T.J. Bell, et al. 1984. Methylene chloride: A two-year inhalation toxicity 

and carcinogenicity study in rats and hamsters. Fund. Appl. Toxicol. 4: 30-47. 

Cherry, N., C.R. Wolf and R.M. Philpot. 1981. Some observations on workers exposed to methylene 

chloride. Br. J. Ind. Med. 38: 351-355. 

Cherry, N., H. Venable and H.A. Waldron. 1983. The acute behavioral effects of solvent exposure. J. 

SOC. Occup. Med. 33: 13-18. (Cited in ATSDR, 1989) 

DiVincenzo, G.D., F.J. Yanno and B.D. Astill. 1972. Human and canine exposure to methylene chloride 

vapor. Am. Ind. Hyg. Assoc. J. 33: 125-135. 

DiVincenzo, G.D. and C.J. Kaplan. (1981) Uptake, metabolism and elimination of methylene chloride 

vapor by humans. Toxicol. Appl. Pharmacol. 59: 130-140. 

Engstrom, J. and R. Bjurstrom. 1977. Exposure to methylene chloride. Content in subcutaneous adipose 

tissue. Scand. J. Work Environ. Health 3: 215-224. 

' 

Friedlander, B.R., F.T. Heame and S. Hall. 1978. Epidemiologic investigation of employees chronically 

exposed to methylene chloride. J. Occup. Med. 20: 657-666. (Cited in IARC, 1986) 

17

Haun, C.C., E.H. Vernot, K.I. Danner, et al. 1972. Continuous animal exposure to low levels of 

dichloromethane. Proc. 3rd. Ann,. Conf. Env. Toxicol. Aerospace Med. Res. Lab., Wright-Patterson Air 

Force Base, Ohio. AMRL-TR-130., Paper No. 12, pp. 199-208. (Cited in U.S. EPA, 1983) 

Hearne, F.T., F. Grose, J.W. Pifer, et al. 1987. Methylene chloride mortality study: Dose-response 

characterization and animal model comparison. J. Occup. Med. 29: 217-228. (Cited in ATSDR, 1989) 

Heppel, L., P. Neal, T. Perrin, et al. 1944. Toxicology of dichloromethane (methylene chloride). I. 

Studies on effects of daily inhalation. J. Ind. Hyg. Toxicol. 26: 8-16. (Cited in NTP, 1986) 

IARC (International Agency for Research on Cancer). 1986. Dichloromethane. In: iARC Monographs 

on the Evaluation of the Carcinogenic Risk of Chemicals to Humans. Some Halogenated Hydrocarbons 

and Pesticide Exposures. Vol. 41. World Health Organization, Lyon, France, pp. 43-85. 

Kirschman, J.C., N.M. Brown, R.H. Coots and K. Morgareigde. 1986. Review of investigations of 

dichloromethane metabolism and subchronic oral toxicity as the basis for the design of chronic oral studies 

in rats and mice. Food Chem. Toxicol. 24: 943-949. 

Klaassen, C. and G. Plaa. 1966. Relative effects of various chlorinated hydrocarbons on kidney and liver 

function in mice. Toxicol. Appl. Pharmacol. 9: 139-151. 

Kutob, S. and G. Plaa. 1962. A procedure for estimating the hepatotoxic potential of certain industrial 

solvents. Toxicol. Appl. Pharmacol. 4: 34-361. 

Kuzelova, M. and R. Vlasak. 1966. The effect of methylene dichloride on the health of workers in 

production of film foils and investigation on formic acid as a methylene dichloride metabolite. Prawvni 

Lekor 18: 167-170. (Cited in NTP, 1986) 

- 

NCA (National Coffee Association). 1982. 24-Month Chronic Toxicity and Oncogenicity Study of 

Methylene Chloride in Rats. Final Report. Prepared by Hdeton Laboratories America, Inc., Vienna, 

VA. (Unpublished; cited in U.S. EPA, 1992a) 

NCA (National Coffee Association). 1983. 24-Month Chronic Toxicity and Oncogenicity Study of 

Methylene Chloride in Mice. Final Report. Prepared by Hazleton Laboratories America, Inc., Vienna, 

VA. (Unpublished, cited in U.S. EPA, 1992a) 

NIOSH (National Institute of Occupational Safety and Health). 1976. Criteria for a Recommended 

standard ... Occupational Exposure to Methylene Chloride. US. DHEW, Cincinnati, OH. 

Nitschke, K.D., J.D. Bud, T.J. Bell, et ai. 1988a. Methylene chloride: A 2-year inhalation toxicity and 

oncogenicity study in rats. Fund. Appl. Toxicol. 11: 48-59. 

Nitschke, K.D., D.L. Eisenbmndt, L.G. Lomax, et al. 1988b. Methylene chloride: Two-generation 

reproductive study in rats. Fund. Appl. Toxicol. 11: 60-67. 

NTP (National Toxicology Program). 1986. Toxicology and Carcinogenesis Studies of Dichloromethane 

(Methylene Chloride) (CAS No. 75-09-2) in F344M Rats and B6C3F, 

18

Mice (Inhalation Studies). U.S. Department of Health and Human Services, Public Health Service, 

Research Triangle Park, N.C., NTP TR 306. 

Ott, M.G., L.K. Skory, B.B. Holder, et al. 1983a. Health surveillance of employees occupationally 

exposed to methylene chloride. I. Mortality. Scand. J. Work Environ. Health 9 (Suppl. 1): 8-16. (Cited 

in U.S. EPA, 1989) 

Ott, M.G., L.K. Skory, B.B. Holder, et al. 1983b. Health surveillance of employees occupationally 

exposed to methylene chloride. Twenty-four hour electrocardiographic monitoring. Scand. J. Work 

Environ. Health 9 (Suppl. 1): 26-30. (Cited in U.S. EPA, 1989) 

Sax. 1984. Methane dichloride. In: Dangerous Properties of Industrial Materials, 6th ed. Van Nostrand 

Reinhold Company, New York, NY, p. 1763. 

Smta, D.G., A.K. Thakur, B.M. Ulland, et al. 1986a A two-year drinking water study of 

dichloromethane in rodents. I. Rats. Food Chem. Toxicol. 24: 951-958. 

Serota, D.G., A.K. Thakur, B.M. Ulland, et al. 1986b. A two-year drinking water study of 

dichloromethane in rodents. I. Mice. Food Chem. Toxicol. 24: 959. 

Stewart, R.D. and C.L. Hake. 1976. Paint remover h d . J. Med. Assoc. 235: 398401. (Cited in 

ATSDR, 1989) 

Taskinen, H., M.-L. Lindbohm and K. Hemminki. 1986. Spontaneous abortions among women working 

in the pharmaceutical industry. Br. J. Ind. Med. 43: 199-205. 

Theiss, J.C., G.D. Stoner, M.B. Shimkin and E.K. Weisburger. 1977. Test for carcinogenicity of organic 

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Clayton, Eds., Patty’s Industrial Hygiene and Toxicology, 3rd. ed., Vol. 2B. John Wiley and Sons, New 

York, NY, pp. 3537-3545. 

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Halomethanes. Ofice of Water Regulations and Standards, Criteria and Standards Division, U.S. 

Environmental Protection Agency, Washington, DC, EPA 44015-80-05 1. 

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Document for Dichloromethane. Updated Carcinogenicity Assessment. Prepared by the Health 

Assessment Group, U.S. Environmental Protection Agency, Washington, DC. EPA/600/8-82/004/FF. 

19

U.S. EPA. (US. Environmental Protection Agency). 1989. Updated Health-Assessment for Methylene 

Chloride. Final Draft. Prepared for the Office of Solid Waste and Emergency Response by 

Environmental Criteria and Assessment Ofice, Office of Health and Environmental Assessment, U.S. 

Environmental Protection Agency, Cincinnati, OH, ECAO-CIN-H028a. 

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DC . 

U.S. EPA (U.S. Environmental Protection Agency). 1993b. Integrated Risk Information System (IRIS), 

Environmental Criteria and Assessment Office, Office of Health and Environmental Assessment, 

Cincinnati, OH. 

Weinstein, R.S. and S.S. Diamond. 1972. Hepatotoxicity of dichloromethane (methylene chloride) with 

continuous inhalation exposure at a low dose level. Proc. 3rd. Ann,. Conf. Env. Toxicol. Aerospace Med. 

Res. Lab., Wright-Patterson Air Force Base, Ohio. AMRL-TR-72-130., pp. 209-220. (Cited in ATSDR, 

1989) 

Weinstein, R.S., D.D. Boyd and K.C. Back. 1972. Effects of continuous inhalation of dichloromethane 

in the mouse-morphological and fimctional observations. Toxicol. Appl. Pharmacol. 23: 660. 

Welch, L. 1987. Reports of clinical disease secondary to methylene chloride exposure - a collection of 

141 cases. Unpublished study. Submitted to OPTSEPA 3/31. (Cited in ATSDR, 1989) 

Winneke, G. 1974. Behavioral effects of methylene chloride and carbon monoxide as assessed by sensory 

and psychomotor performance. In: Behavioral Toxicology, C. Xintaras, B.L. Johnson and I. de Gmt, 

Eds. U.S. Printing Ofke, Washington, DC, pp. 130-144. (Cited in ATSDR, 1989) 

20


NICKEL AND NICKEL COMPOUNDS 

July 1995 

Prepared by: 

Robert A. Young, PbD., D.A.B.T. 






Prepared for: 



- 

*Managed by Lockheed Martin Energy Systems, Inc., for the US. Department of Energy under 

Contract No. DE-AC05-840R2 1400


Nickel is a naturally occurring element that may exist in various mineral forms. It is used in a 

wide variety of applications including metallurgical processes and electrical components, such as 

batteries (ATSDR 1988, USAF 1990). Some evidence suggests that nickel may be an essential trace 

element for mammals. 

The absorption of nickel is dependent on its physicochemical form, with water soluble forms 

being more readily absorbed. The metabolism of nickel involves conversion to various chemical 

forms and bindmg to various ligands (ATSDR 1988). Nickel is excreted in the urine and feces with 

relative amounts for each route being dependent on the route of exposure and chemical form. Most 

nickel enters the body via food and water consumption, although inhalation exposure in occupational 

settings is a primary route for nickel-induced toxicity. 

In large doses (>OS g), some forms of nickel may be acutely toxic to humans when taken orally 

(Daldrup et al. 1983, Sunderman et al. 1988). Oral LD,, values for rats range from 67 mg nickelkg 

(nickel sulfate hexahydrate) to >9000 mg nickelkg (nickel powder) (ATSDR 1988). Toxic effects 

of oral exposure to nickel usually involve the kidneys with some evidence from animal studes 

showing a possible developmentalheproductive toxicity effect (ATSDR 1988, Goyer 1991). 

Inhalation exposure to some nickel compounds will cause toxic effects in the respiratory tract 

and immune system (Smialowicz et al. 1984, 1985, 1987; ATSDR 1988; Goyer 1991). Inhalation 

LC,, values for anrmals range from 0.97 mg nickeVm3 for rats (6-hour exposure) to 15 mg nickeVm’ 

for m ea pigs (time not specified) (USAF 1990). Acute inhalation exposure of humans to nickel 

may produce headache, nausea, respiratory disorders, and death (Goyer 1 99 1, Rendall et al. 1994). 

Asthmatic conditions have also been documented for inhalation exposure to nickel (Goyer 1991). 

Soluble nickel compounds tend to be more toxic than insoluble compounds (Goyer 1991). In 

addition, nickel carbonyl is known to be extremely toxic to humans upon acute inhalation exposure 

(Goyer 1991). 

Data on nickel-induced reproductive/developmental effects in humans following inhalation 

exposure are equivocal. No clinical evidence of developmental or reproductive toxicity were reported 

for women workmg in a nickel refinery (Warner et al. 1979), but Chashschin et al. (1994) reported 

possible reproductive and developmental effects in humans of occupational exposure to nickel 

(0.13-0.2 mg nickeVm3). Although not validated by quantitative epidemiologic data or statistical 

analyses, the authors reported an apparently abnormal increase in spontaneous and threatening 

abortions (1617% in nickel-exposed workers vs 8-9% in nonexposed workers), and an increased 

incidence of non-specified structural malformations (1 7% vs 6%) was reported also. Furthermore, 

sensitivity reactions to nickel are well documented and usually involve contact dermatitis reactions 

resulting from contact with nickel-containing items such as cooking utensils, jewelry, coins, etc. 

(ATSDR 1988). 

A chronic (EPA 1995) and subchronic @PA 1994) oral reference dose (RtD) of 0.02 mg/kg/day 

for soluble nickel salts is based on changes in organ and body weights of rats receiving dietary nickel 

sulfate hexahydrate (5 madday) for 2 years. A no-observed-adverse-effect level (NOAEL) and 

lowest-observed-adverse-effects level (LOAEL) 

Ill

of 5 mg/kg/day and 50 mg/kg/day, respectively, were reported in the key study 

(Ambrose et al. 1976). An uncertainty factor of 300 reflects interspecies extrapolation uncemty, 

protection of sensitive populations, and a m m g factor of 3 for a database deficient in 

reproductivddevelopmental studies. 

An inhalation reference concentration (RfC) for soluble nickel salts is under review by the 

RfDm Work Group (EPA 1995) and currently is not available. 

The primary target organs for nickel-induced systemic toxicity are the lungs and upper 

respiratory tract for inhalation exposure and the kidneys for oral exposure (ATSDR 1988, 

Goyer 199 1). Other target organs include the cardiovascular system, immune system, and the blood. 

Epidemiologic studies have shown that occupational inhalation exposure to nickel dust 

(primarily nickel subsulfate) at refmeries has resulted in increased incidences of pulmonary and nasal 

cancer (NAS 1975, Enterline and Marsh 1982, ATSDR 1988). Inhalation studies using rats have also 

shown nickel subsulfate or nickel carbonyl to be carcinogenic (Sunderman et al. 1959, Sunderman 

and Donnelly 1965, Ottolenght et al. 1974). Based on these data, the EPA (1995) has classified nickel 

subsulfate and nickel refinery dust in weight-of-evidence group A, human carcinogen. 

Carcinogenicity slope factors of 1.7E-M and 8.4E-01 (mg/lcg/day)” and unit risks of 4.8E-04 (pg/m3)- 

’ and 2.4E-04 (pfl) have been calculated for nickel subsulfide and nickel refinery dust, 

respectively (EPA 1994, 1995). Based on an increased incidence of pulmonary carcinomas and 

malignant tumors in animals exposed to nickel carbonyl by inhalation or by intravenous injection, 

this compound had been placed in weight-of-evidence group B2, probable human carcinogen (EPA 

1995). No unit risk values were available for nickel carbonyl. Recent analyses of epidemiologic data, 

however, indicate that definitive identification of a specific nickel compound as the causative agent 

is not yet possible (Easton et al. 1994, Langhd 1994, Roberts et al. 1994). 

iv


Nickel is a naturally occurring metal existing in various mineral forms and may be found 

throughout the environment includmg rivers, lakes, oceans, soil, air, drinking water, plants, and 

animals. Soil and sedunent are the primary receptacles for nickel, but mobilization may occur 

depending on physico-chemical characteristics of the soil (ATSDR 1988, USAF 1990). Nickel is 

used in a wide variety of metallurgical processes such as electroplating and alloy production as well 

as in nickel-cadmium batteries. Some evidence suggests that nickel may be an essential trace element 

for mammals (Coyer 1991). As for most metals, the toxicity of nickel is dependent on the route of 

exposure and the solubility of the nickel compound (Coogan et al. 1989). 



Pulmonary absorption is the major route of concern for nickel-induced toxicity. Nickel may be 

absorbed as the soluble nickel ion (Ni”) while sparingly soluble nickel compounds may be 

phagocytized. The chemical form and its deposition site (determined by size, shape, density, and 

electrical charge of the nickel particles) in the lungs will affect the extent of absorption 

(ATSDR 1988). Nickel may be removed fiom portions of the respiratoxy tract via mucociliary 

transport resulting in the material entering the gastrointestinal tract. Although nickel is poorly 

absorbed from the gastrointestinal tract, dietary exposure and exposure via drinking water provide 

most of the intake of nickel and nickel compounds (Coogan et al. 1989, Goyer 1991). As reviewed 

by the EPA (1986), humans and animals absorb approximately 1-10% of dietary nickel. Similar 

values were reported for drinking water exposure and gavage administration (ATSDR 1988). Nickel 

metal is poorly absorbed dermally but some nickel compounds such as nickel chloride or nickel 

sulfate can penetrate occluded skin resulting in up to 77% absorption within 24 hours (ATSDR 

1988). 


Nickel is readily distributed throughout the body but may be affected by route of exposure, the 

chemical form, and time &r exposure (Coogan et al. 1989). Although the kidney and lungs are the 

primaxy sites of accumulation of nickel, other organs such as the spleen, liver, heart and testes may 

also accumulate the metal to a much lesser extent. Nickel is known to bind to specific proteins andor 

amino acids in the blood serum and the placenta. These ligands are instrumental in the transport and 

distribution of nickel in the body. Nickel distribution may be altered by the formation of lipophilic 

nickel complexes. 

1

2 


Nickel is not destroyed in the body, but its chemical form may be altered. The metabolism of 

nickel is most appropriately viewed in light of its binding to form ligands and its transport throughout 

the body. Much of the toxicity of nickel may be associated with its interference with the 

physiological processes of manganese, zinc, calcium, and magnesium (Coogan et al. 1989). Various 

disease states (myocardial infarction and acute stroke) and injuries (burn injury) are associated with 

altered transport and serum concentrations of nickel (ATSDR 1988). 

2.4 EXCRETION 

Nickel is excreted in the urine and feces, but because it is poorly absorbed, most ingested nickel 

is excreted in the feces. It has been reported that fecal nickel is usually about 100 times that of 

urinary nickel and represents the removal of unabsorbed nickel (ATSDR 1988, Goyer 1991). 

Furthermore, nickel that is absorbed is excreted primarily in the urine (ATSDR 1988). Urinary nickel 

levels of 0.4-6.0 pg/L in nonexposed, healthy adults were reported by Sunderman et al. (1986% 

1989) while levels as high as 400 pg/L were reported by Sunderman et al. (1986b) for workers 

occupationally exposed to nickel and nickel compounds. 

In a study of nickel-chromium electroplaters, White and Boran (1994) noted that urinary nickel 

is a valid and sensitive (0.6 pg nickem urine) method of monitoring occupational exposure to 

soluble nickel salts. Nickel may also be excreted in the hair and sweat (ATSDR 1988). 


3.1 ORAL, EXPOSURES 


3.1.1.1 Human 

The acute lethality of nickel following oral exposure is dependent upon the chemical form of 

nickel. A fatal case of nickel poisoning was reported for a 2 %-year-old girl who had ingested 15 g 

of nickel sulfate (Daldrup et al. 1983). The cause of death was cardiac arrest. Death due to nickelinduced 

Adult Respiratory Distress Syndrome (ARDS) was reported for a worker spraying nickel 

using a thermal arc process (Rendall et al. 1994). Death occurred 13 days following 9O-minute 

exposure to an estimated nickel concentration of 382.1 mg/m3; total nickel intake was estimated at 

nearly 1 g. Nausea, vomiting, abdomtnal pain, diarrhea, headache, cough, shortness of breath, and 

giddiness were reported for workers of an electroplating plant who drank water contaminated with 

nickel chloride and nickel sulfate (1.63 g/L) (Sunderman et al. 1988). Signs and symptoms of toxicity 

lasted for up to 2 days with uneventiid recoveries for all 32 workers. The nickel doses were estimated 

to be 0.5 to 2.5 g, serum nickel concentrations were 13 to 1340 pg/L, and urinary nickel 

concentrations were 0.15 to 12 mg/g creatinine. 

Some studies have provided dormation indicating the aggravation of nickel-induced dermatitis 

in women following exposure to dietary nickel (ATSDR 1988).

3 


Oral LDso values for rats range from 67 mg nickelkg for nickel sulfate hexahydrate to >9000 mg 

nickelkg for nickel powder (ATSDR, 1988). Generally, soluble nickel compounds are more toxic 

than insoluble compounds. A 2-week exposure of rats to 1000 ppm nickel chloride in the drinktng 

water resulted in excessive mortality (RTI 1987). 


3.1.2.1 Human 

No data were available regarding the toxicity of nickel or nickel compounds in humans 

following subchronic oral exposure. 


With the exception of vomiting during the initial phase of exposure to the highest dose, exposure 

of dogs to dietary nickel sulfate hexahydrate (100, 1000, or 2500 ppm) for 2 years failed to produce 

significant signs of compound-related toxicity (Ambrose et al. 1976). 

A 91-day study using rats given nickel chloride hexahydrate by gavage at doses of 5,35, or 100 

mg nickel/kg/day resulted in the death of all rats in the high-dose group by day 78, in an increase in 

white blood cell counts for those in the 35 mgkglday group at an interim sacrifice, and an elevated 

platelet count and decreased blood glucose level in the 35 mgkg group at final sacrifice (American 

Biogenics Corp. 1986). 

Renal tubular degeneration was reported for rats receiving dietary nickel acetate (0.1 to 1.0%) 

for several weeks. 


3.13.1 Human 

No studies were available regarding the toxicity of nickel or nickel compounds in humans 

following chronic oral exposure. 

3.13.2 Animal 

No studies were available that examined the chronic oral systemic toxicity of nickel or nickel 

compounds in animals. 



No studies were available that addressed the developmentaVreproductive toxicity of orally 

administered nickel or nickel compounds.

4 


Research Triangle Institute (1987) conducted a multigeneration study using rats exposed to 

nickel chloride in the drinking water at nickel concentrations of 50,250, or 500 ppm (equivalent to 

7.3,30.8, or 51.6 mg nickel/kg/day). The highest exposure produced maternal toxicity characterized 

by a decrease in body weight and decreased absolute and relative liver weights of the dams. A 

decrease in the number of live pups per litter, an increase in pup mortality, and a decrease in the 

average body weight of the pups was noted for the F1, and Flb generations of the 500 ppm test group. 

Following statistical analyses, both the 50 and 250 ppm exposures were considered to be a noobserved-adverse-effect 

level (NOAEL). 

3.15 Reference Dose 

3.15.1 Subchronic 

ORAL RfD,: 2E-2 mg/kg/day (soluble nickel salts) (EPA 1994) 


NOAEL: 100 ppm (5 mg/kg/day) 

3.15.2 Chronic 

ORAL RfDc: 2E-2 mg/kg/day (soluble nickel salts) (EPA 1995) 



NOAEL: 100 ppm (5 mg/kg/day) 

LOAEL: 1000 ppm (50 mgkglday) 

CONFIDENCE: 

study: Low 

Data base: Medium 


PRINCIPAL STUDY: Arnbrose et al. 1976 

COMMENTS: The IUD is based on decreased organ and body weights of rats receiving 

dietary nickel sulfate hexahydrate (100 ppm equivalent to a dose of 5 mg/kg/day) for 2 years. 

An uncertainty factor of 100 reflects interspecies extrapolation and protection of sensitive 

populations. A moddjmg factor of three was applied to 8ccount for the absence of definitive 

reproductivddwelopmental studies.

5 



3.2.1.1 Human 

Acute inhalation exposure to nickel carbonyl results in initial headache, nausea, vomiting, and 

chest pain, progressing to hyperpnea, cyanosis, respiratory failure, and death if the exposure is severe 

(Goyer 1991). A lowest toxic concentration (TC,) of 7 mg/m’ for nickel carbonyl has been reported 

(Sax and Lewis 1989). 

Asthmatic disease resulting fiom inhalation exposure to nickel and nickel compounds has been 

reported for nickel-plating workers and stainless steel welders (ATSDR 1988). Nicklin and Nielsen 

(1994) categorized these responses as (1) a rapid onset attack (antibody-mediated Type I 

hypersensitivity) associated with acute bronchospasm, (2) a late response reaction at 6-1 2 hours after 

exposure (antigen-antibody immune complex-mediated lnnammatory reaction), and 3) a mixed or 

combined response. 


Acute halation toxicity studies in d s have provided LC, values ranging from 0.97 mg/m’ 

for 6-hour exposure of rats to nickel subsulfate to 15 mg/m’ (time not specified) for guinea pigs 

exposed to nickel dust (USAF 1990). Acute toxic effects wil be dependent upon the chemical form, 

exposure concentration, and exposure duration. 

Several studies summarized in ATSDR (1988) indicated that 2-hour exposure of mice to nickel 

chloride at concentrations of 0.25 to 0.50 mg nickeYm’ caused a suppression of immune responses. 


3.2.2.1 Human 

In an evaluation of workers welding hgh-nickel alloys, it was reported that 6-week exposure 

to nickel fumes (0.07 to 1.1 mg nickel/m’) caused an increase in airway and eye irritations, 

headaches, and tiredness (Akesson and Skervfkg 1985). 


A number of studies have examined the toxic effects of short-term exposure of animals to 

various chemical forms of nickel (ATSDR 1988). Exposure of rats and mice to aerosols of nickel 

sulfate hexahydrate (0.7 to 13.5 mg nickel/m’) for 12 days resulted in pulmonary inflammation, 

degenerative changes in the bronchiolar mucosa, and atrophy of the olfactory epithelium 

(Benson et al. 1988). Another study using the same protocol and nickel subsulfate (0.4,0.9, 1.8,2.7, 

3.7, or 7.3 mg nickel/m3) showed that exposure to L 5 mg Ni,S, (3.7 mg dckeVm) caused 

necrotizing pneumonia, emphysema, and fibrosis in both rats and mice (Benson et al. 1987). 

Degeneration of the olfactory epithelium was reported for the rats and mice exposed to 

concentrations L 1.2 mg/m3 (0.9 mg nickel/&). Inhalation exposure of rats to nickel chloride (0.109 

mg nickeYm’) produced hyperplastic changes in the bronchial epithelium and increased mucus 

secretion (Bingham et al. 1972). Similar effects have been observed for rabbits inhahng nickel dust 

for 3-8 months (Curstedt et al. 1983,1984; Johansson et al. 1983).

6 

A 13-week inhalation study conducted by the Inhalation Toxiwlogy Research Institute 

compared the effects of exposure of rats and mice to nickel sulfate hexahydrate, nickel subsulfate, 

and nickel oxide at occupationally relevant exposure concentrations. Severity of inflammation and 

fibrosis of the lungs and alveolar macrophage hyperplasia corresponded to the water solubility of the 

nickel compounds with nickel sulfate being the most toxic, followed by nickel subsulfate and nickel 

oxide (Dunnick et al. 1989). Biochemical indexes of pulmonary toxicity (lactate dehydrogenase and 

beta-glucuronidase activity; total protein levels) indicated the order of toxicity to be NiSO, > Ni, S, 

> NiO (Benson et al. 1989). Varying degrees of immunological effects in mice were also noted for 

these three compounds, with effects depending on dose and physicochemical form (Haley et al. 

1990). The investigators concluded that inhalation of these nickel compounds at occupationally 

relevant concentrations can result in signtficant alterations of pulmonary and systemic immune 

defenses. 

The immunotoxic effects of nickel compounds have been affumed by other investigators. Haley 

et al. (1990) reported immunotoxic effects in mice following 13-week exposures to various nickel 

compounds. Nickel subsulfide (1.8 mg nickellm’) decreased activity levels of natural killer cells 

while both nickel oxide (0.47, 2.0, and 7.9 mg nickellm’) and nickel subsulfate (0.45 and 1.8 mg 

nickeYm3) inhibited phag-c ability of alveolar macrophages. In studies with mice and rats, 

!bialowicz et al. (1984, 1985, 1987) found that nickel chloride affected T-cell-mediated immune 

responses (but not humoral immune responses) and that natural killer cells were target cells of the 

immunotoxic effects of nickel. 


3.23.1 Human 

Most chronic inhalation exposures involve occupational exposure to nickel dust or nickel vapors 

resulting from welding nickel alloys. Generally, chronic inhalation exposure to nickel dusts and 

aerosols contribute to respiratory disorders such as asthma, bronchitis, rhinitis, sinusitis, and 

pneumoconiosis (USAF 1990). Chronic exposure to nickel and nickel compounds have been 

implicated in carcinogenic responses as discussed in Sect. 4.2. 

3.23.2 Animal 

A 31-month exposure of rats to nickel oxide (0.06 or 0.20 mg nickellm’) resulted in the 

development of focal septal fibrosis and histological changes indicative of alveolar proteinosis 

(Takenaka et al. 1985). A lifetime exposure of rats to nickel oxide (42 mg nickellm3) produced 

emphysema and other proliferative and inflammatory changes (Wehner et al. 1975). 



No clinical evidence of developmental or reproductive toxicity were reported for women 

working in a nickel refinery (Warner et al. 1979). More recently, however, Chashschin et al. (1994) 

reported on possible reproductive and developmental effects in humans of occupational exposure to 

nickel (0.13-0.2 mg nickel/m3). Although not validated by quantitative epidemiologic data or 

statistical analyses, the authors reported an apparedy abnormal increase in spontaneous and 

threatening abortions (1617% in nickelexposed workers versus 8-9% in nonexposed workers) and 

an increased incidence of nonspecified structural malformations ( 17% vs 6%) was also reported.

7 


A reduction in fetal body weight was observed for pregnant rats exposed to nickel oxide (1.3 or 

2.5 mg/m’) throughout gestation (Weischer et al. 1980). The number of fetuses per litter was 

unaffected. Benson et al. (1988) reported degeneration of the germinal epithelium of testes in rats 

exposed to nickel sulfate at concentrations 2 7 mg/m’ (2 1.6 mg nickel/& ) for 12 days. Similar 

effects were observed for mice and rats exposed to nickel subsulfate at concentrations of 2 2.5 mg/m’ 

(2 1.8 mg nickel/m3) (Benson et al. 1987). 

3.2.5 Reference Concentration 

Subchronic and chronic &alation RfCs for soluble nickel salts are currently under review by 

the R€DmWork Group @PA 1995). 



3.3.1.1 Human 

Nickel-induced contact dermatitis is well documented for humans and is the most prevalent 

effects of nickel in humans (ATSDR 1988). Both occupational and nonoccupational exposures are 

common, the latter involving commodities such as eating utensils, coins, jewelry, and tools. Data 

indicate women to be at greater risk for dermatitis of the hands, possibly due to more fiequent contact 

with nickel-containing items. No dose-response data are available for nickel sensitivity reactions. 


Nickel sensitivity has not been adequately demonstrated in animals (ATSDR 1988), and no 

mformation was available regardmg other acute effects following dermal exposure to nickel or nickel 

compounds. 


No information was available on the subchronic toxicity of nickel or nickel compounds in 

humans or animals by other routes of exposure. 

333 Chronic Toxicity 

No information was available on the chronic toxicity of nickel or nickel compounds in humans 

or animals by other routes of exposure.

8 

3.3.4 Developmental Toxicity 

No definitive information was available. Mathur et al. (1 977) reported that application of nickel 

sulfate hexahydrate (60 or 100 mgkglday for 30 days) to the shaved backs of rats resulted in tubular 

damage of the testes and sperm degeneration. However, the effects may have been due to ingestion 

of the compound during grooming. 

3.4 TARGET ORGANS/CRITICAL EFFECI'S 


3.4.1.1 Primary target(s) 

1. Kidney: Although not documented for humans, parenteral administration studies in animals 

have venfied the nephrotoxicity of nickel and nickel compounds (ATSDR 1988, USAF 

1990). 

2. Blood: Alterations in whte blood cell counts of mice and decreased hematocrit in rats have 

been reported following gavage administration of nickel chloride (USAF 1990). 

3.4.1.2 Other target@) 

1. Skin: Some studies are available documenting the aggravation of nickel-induced dermatitis 

in women following exposure to dietary nickel. 

2. Cardiovascular system: Anecdotal information suggested that very high (15 g) acute doses 

of nickel sulfate may cause cardiac arrest. 


3.4.2.1 Primary target@) 

1. Respiratory tract: Inhalation of nickel or nickel compounds may cause respiratory conditions 

such as asthma, bronchitis, rhinitis, sinusitis, and pneumocOniosis. Inhalation of nickel 

carbonyl may be fatal. The nature and severity of the adverse effects may vary depending 

on the specific nickel compound and the duration of exposure. 

2. Immune system: Exposure of mice to nickel subsulfide decreased activity levels of natural 

killer cells, and both nickel oxide (0.47-7.9 mg nickeVm3) and nickel subsulfide (0.45-1.8 

mg nickel/m3) inhibited phagocytic ability of alveolar macrophages. Exposure of rats and 

mice to nickel chloride inhibited T-cell-mdated immune responses. 

3.4.2.2 Other target@) 

1. Testes: Degeneration of the germinal epithelium of the testes was observed in rats exposed 

to nickel sulfate at concentrations -2 7 mg/m3 (2 1.6 mg nickel/m3) for 12 days.

9 




No information was available on the carcinogenicity of nickel or nickel compounds in humans 

following oral exposure. 


Although several studes have been conducted assessing the carcinogenic potential of nickel 

compounds following oral exposure, the studies suffered from inadequate design (ATSDR 1988). 

t 

4.2 INHALATION EXPOSURE 


Several epidemiologic studies have investigated the potential carcinogenicity of inhaled nickel 

and nickel compounds (ATSDR 1988). Based on analyses of studies completed prior to 1975, the 

National Academy of Sciences (NAS 1975) concluded that nickel refinery workers demonstrated an 

increase in the incidence of pulmonary and nasal cavity cancers, specifically epidermoid, anaplastic, 

and pleomorphic cancers. Enterline and Marsh (1982) showed that there was an excess risk of nasal 

sinus cancer in nickel refi.neT workers. The standardized mortality ratio (SMR) was 2443. 

Doll et al. (1977) also reported an excess of lung and nasal cancer among nickel refinery 

workers. The incidence was virtually eliminated after the implementation of respirators. 

Magnus et al. (1980) studied workers fiom several job categories in a nickel refinery and found 

an increase in the risk of nasal cancer in all jobs, with the highest risk being in roastinghmelting jobs 

and for electrolysis workers. The authors also reported that smoking and nickel exposure appeared 

to be additive in their carcinogenic potential. 

For epidemiologic studies on stainless steel welders, Langbd (1994) noted that it was not 

possible to determine whether exposure to nickel or chromium VI was a greater factor in the reported 

increased cancer incidences for this occupational group. Additionally, Easton et al. (1994) noted that 

currently available data and analyses would not allow for a valid association of a specific nickel 

compound with the observed cancer incidences. In the absence of more definitive data, it is assumed 

that exposure to any nickel compound with a particle size small enough to reach nasal and bronchial 

tissue may constitute a respiratory cancer hazard. 

Although data are not available to positively identtfy which nickel compounds are responsible 

for inducing carcinogenic responses in humans, recent analyses have indicated nickel oxide, 

subsulfate, and soluble nickel to be likely candidates (Roberts et al. 1994).

10 


In an inhalation study by Ottolenghl et al. (1974), rats of both sexes were exposed to nickel 

subsulfate (0.97 mg nickevm’) for 78 to 84 weeks followed by a 30-week observation period. 

Relative to controls, there was an increase in the incidence of adenomas and adenocarcinomas in the 

nickel-exposed rats. 

Sunderman et al. (1 959) showed that repeated inhalation exposures of rats to nickel carbonyl 

(0.03 or 0.06 mgL) over a l-year period resulted in an increased incidence of tumors relative to 

controls. Lifetime inhalation exposure of rats to nickel carbonyl vapor (0.6 mgL for 30 minutes or 

0.03 mg/L, three timedweek) resulted in pulmonary carcinomas and metastases (Sunderman and 

Donnelly 1965). Lau et al. (1972) induced malignant tumors at various sites in rats injected with 

nickel carbonyl. 


No information was available on the carcinogenicity of nickel or nickel compounds in animals 

by other routes of exposure. 

4.4 EPA WEIGHT-OF-EVIDENCE CLASSIFICATION 

Nickel subsulfide: 

Classification-A, Human carcinogen @PA 1995) 

Basis-Increased risks of lung and nasal cancer in humans exposed to nickel refinery dust, most 

of which is believed to be nickel subsulfate; increased tumor incidences in several species and 

strains of animal for multiple routes of administration; positive results in genotoxicity assays. 

Nickel refinery dust: 

Classification-A, Human carcinogen (EPA 1995) 

Basis-Epidemiologic studies in several Merent countries showed nickel refinery dust to cause 

lung and nasal tumors in nickel sulfide matte refinery workers; animal data showed an increased 

incidence of carcinomas in rats following adminrstration via dation or injection. 

Nickel carbonyl: 

Classification-B2, Probable human carcinogen @PA 1995) 

Basis-Observation of pulmonary carcinomas and malignant tumors at various sites in rats 

administered nickel carbonyl by inhalation and intravenous injection, respectively; nickel 

administered as nickel carbonyl binds to DNA. 

The EPA has not evaluated soluble nickel salts for potential human carcinogenicity.

11 

4.5 CARCINOGENICITY SLOPE FACTOR 


No slope factors for carcinogenicity of nickel and nickel compounds through ingestion have 

been calculated. 


SLOPE FACTORS: 8.4E-01 (mg/kg/day)-' (nickel refinery dust) (EPA 1994) 

1.7Ei-O (mg/kg/day)-' (nickel subsulfide) (EPA 1994) 

No slope factors have been calculated for other nickel compounds. 

PRINCIPAL STUDY: Data sets from several occupational exposure stucjles were used and are 

described in EPA (1986). 

, VERIFICATION DATE: 04/01/87 

UNIT RISKS: 4.8E-4 (pg/m3)-' (nickel subsulfide) (EPA 1995) 

2.4E-4 (pg/m3)-' (nickel refinery dust) (EPA 1995) 

Nickel refinery dust is a mixture of many nickel moieties, and the identity of the specific 

carcinogenic nickel species is not known. 

5. REFERENCES 

Akesson, B. and S. Skervfing. 1985. Exposure in welding of high nickel alloy, Int. Arch. Occup. 

Environ. Health 56: 11 1-1 17. 

Ambrose, A. M., P. S. Larson, J. R Borzelleca and G. R Hennigar, Jr. 1976. Long term toxicologic 

assessment ofnickel in rats and dogs,J. Food. Sci. Technol. 13: 181-187. 

American Biogenics Corp. 1986. Ninety day gavage study in albino rats using nickel, Final Drafi 

report to Research Triangle Inst. (Cited in ATSDR 1988). 

ATSDR (Agency for Toxic Substances and Disease Regisby). 1988. Toxicologcal Profile for Nickel, 

ATSDR/U.S. Public Health Service, ATSDR/TP-88/19. 

Benson, J. M., R L. Carpenter, F. F. Hahn, et al. 1987. Comparative inhalation toxicity of nickel 

subsulfate to F344M rats and B6C3FI mice exposed for twelve days, Fund. Appl. Toxicol. 9: 

25 1-265. 

Benson, J. N., D. G. Burt, R L. Carpenter, et al. 1988. Comparative inhalation toxicity of nickel 

sulfate to F344M rats and B6C3F, mice exposed for twelve days, Fund. Appl. Toxicol. 10: 

164-178.

12 

Benson, J. M., D. G. Burt, Y.4. Yung, et al. 1989. Biochemical responses of rat and mouse lung to 

inhaled nickel compounds, Toxicology 57: 255-266. 

Bingham, E., W. Barkley, M. Zerwas, K. Sterner, and P. Taylor. 1972. Responses of alveolar 

macrophages to metals. I. Inhalation of lead and nickel, Arch. Environ. Health 25: 406-414. 

Chashschm, V. P., P. A. Arhmna, and T. Norseth. 1994. Congenital defects, abortion and other 

health effects in nickel refinery workers, Science Total Environ. 148: 287-29 1. 

Coogan, T. P., D. M. Latta, E. T. Snow, and M. Costa. 1989. Toxicity and carcinogenicity of nickel 

compounds, In: Critical Reviews in Toxicology, Vol 19. McClellan, RO., ed., CRC Press, Boca 

Raton, FL. pp. 341-384. 

Curstedt, T., M. Hafinan, B. Robertson, and P. Camner. 1983. Rabbit lungs after exposure to low 

nickel dust combustion. I. Effects on phospholipid concentration and surfactant activity, 

Environ. Res. 30: 89-94. 

Curstedt, T., M. Casarett-Bruce, and P. Camner. 1984. Changes in glycerophosphatides and their 

ether analogs in lung lavage of rabbits exposed to nickel dust, Exp. Mol. Pathol. 4 1 : 226-234. 

Daldrup, T., K. Haarhoff and S. C. Szathmary. 1983. Toedliche nickel sulfate-intoxikation, Benchte 

zur Gerichtlichen Medizin 41:141-144. (Cited in ATSDR 1988) 

Dunnick, J. K., M. R Elwell, J. M. Benson, et al. 1989. Lung toxicity after 13-week inhalation 

exposure to nickel oxide, nickel subsulfate, or nickel sulfate hexahydrate in F344M rats and 

B6C3F, mice, Fundam. Appl. Toxicol. 12: 584-594. 

Easton, D. F., J. Peto, L. G. Morgan, et al. 1994. Respiratory cancer mortality in Welsh nickel 

refiners: which nickel compounds are responsible, In: Nickel and Human Health, Nieboer, E. 

and J.O. Nriagu, eds., John Wiley and Sons, Inc., New York, NY. pp. 603-619. 

Enterline, P. E. and G. M. Marsh. 1982. Mortality among workers in a nickel refinery and alloy plant 

in West VirginiqJ. Natl. CancerInst. 68: 925-933. 

EPA. 1986. Health Assessment Document for Nickel and Nickel Compounds, Office of Health and 

Environmental Assessment, Environmental Criteria and Assessment Office, Research Triangle 

Park, NC. EPA-600/8-83-012F. NTIS PB 86-232212. 

EPA. 1994. Health Effects Summary Tables, FY-1994 Annual, Office of Research and Development, 

Office of Emergency and Remdal Response, Washington,D.C. NTIS PB94-921199. 

EPA. 1995. Nickel. Integrated Risk Wonnation System (IRIS), Environmental Criteria and 

Assessment Office,Office of Health and Environmental Assessment, Cincinnati, OH. 

Guyer. R 1991. Toxic effects of metals, In: Casarert and Douli's Toxicoiogy, 4th4. Amdur, M.O., 

J.D. hull and C.D. Klaassen, eds., Pergamon Press, New York. pp.623-680. 

Haley, P. J., Shopp, G. M., J. M. Benson et al. 1990. The immunotoxicity of three nickel compounds 

following 13-week inhalation exposure in the mouse, Fundam. Appi. Toxicol. 15: 476487. 

Langhd, S. 1994. Nickel-related cancer in welders, Science of the Total Environ. 148: 303-309.

13 

Lau, T. J., R. L. Hackett, and F. W. Sunderman. 1972. The carcinogenhty of intravenous nickel 

carbonyl in rats, Cancer Res. 32: 2253. 

Magnus, K. A. Anderen, and A. C. Hogetveit. 1980. Cancer of respiratory organs among workers at 

a nickel refmery in Norway, Int. J. Cancer 30: 681-685. 

Mathur, A. K., T. S. S. Dikshith, M. M. Llal, and S. K. Tandon. 1978. Distribution of nickel and 

cytogenetic changes in poisoned rats, Toxicology 10: 105-1 13. (Cited in ATSDR 1988) 

Nicklin, S. and G. D. Nielsen. 1994. Nickel and the irnmune system: current concepts, In: Nickel and 

Human Health, Nieboer, E. and J.O. Nriagu, eds., John Wiley and Sons, Inc., New York, NY. 

pp. 239-259. 

Ottolenghl, A. D., J. K. Haseman, W. W. Payne, H. L. Falk, and H. N. MacFarhad. 1974. Inhalation 

studies of nickel sulfide in pulmonary carcinogenesis of rats, J. Natl. Cancer Inst. 54: 

1 165- 1 172. 

Rendall, R E. G., J. I. Phillips, and K. A. Renton. 1994. Death following exposure to fine particulate 

nickel fiom a metal arc process, Ann. Occup. HE. 38: 92 1-930. 

Roberts, R. S., J. A. Julian, N. Jadon, and D. C. F. Muir. 1994. Cancer mortality in Ontario nickel 

workers: 1950-1984. In: Nickel and Human Health, Nieboer, E. and J.O. Nriagu, e&., John 

Wiley and Sons, Inc., New York, NY. pp. 629-648. 

RTI (Research Triangle Institute). 1987. Two generation reproduction andfertifity study of nickef 

chloride administered to CD ruts in drinking water, report submitted to Office of Solid Waste, 

EPA, Washington, DC. 

Sax, N.I. and RJ. Lewis, Jr., eds. 1989. Dangerous Properties ofIndustnalMaterials, 7th Ed., Van 

Nostrand Reinhold, New York. 

Shen, H. M. and Q. F. Zhang. 1994. ksk assessment of nickel carcinogenicity and occupational lung 

cancer, Environ. Health Perspect. Suppl. 102: 275-282. 

Smialowicz, R J., R R Rogers, M. M. Riddle, and G. A. Scott. 1984. Immunologic effects of nickel: 

I. Suppression of cellular and humoral immunity, Environ. Res. 33: 413-427. (Cited in Shen and 

Zhang 1994) 

Smialowicz, R J., R R Rogers, M. M. Riddle, et al. 1985. Immunologic effects of nickel: II. 

suppression of natural killer cell activity, Environ. Res. 36: 56-66. (Cited in Shen and 

Zhang 1994) 

Smialowicz, R J., R R Rogers, D. G. Rowe, et al. 1987. The effects of nickel on immune function 

in the rat, Toxicology 44: 271-281. (Cited in Shen andzhang 1994) 

Sunderman, F. W., Jr., A. Aito, L. G. Morgan, and T. Norseth. 1986a. Biological monitoring of 

nickel. In: Nickel and Human Health, Nieboer, E. and J.O. Nriagu, eds., John Wiley and Sons, 

Inc., New York, NY. pp. 49-68. 

Sunderman, F. W., A. J. Donnelly, B. West, and J. F. Kincaid. 1959. Nickel poisoning. E. 

Carcinogenesis in rats exposed to nickel carbonyl, Arch. Ind. Health 20: 36.

14 

Sundman, F. W. and A. J. Donnelly. 1965. Studies of nickel carcinogenesis metastasizing 

pulmonary tumors in rats induced by the inhalation of nickel carbonyl, Am. J Pathol. 46: 1027. 

Sunderman, F. W., Jr., B. Dingle, S. M. Hopfer, and T. Swift. 1988. Acute nickel toxicity in 

electroplating workers who accidentally ingested a solution of nickel sulfate and nickel chloride, 

Am. J. Indust. Med. 14: 257-266. 

Sunderman, F. W., Jr., S. M. Hopfer, M. C. Cristomo, and M. Stoeppler. 1986b. Rapid analysis of 

nickel in urine by electrothermal atomic absorption spectrophotometry. Ann. Clin. Lab. Sci., In: 

Nickel and Human Health, Nieboer, E. and J.O. Nriagu, eds., John Wiley and Sons, Inc., New 

York, NY. pp. 49-68. 

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inhalation of nickel oxide. In: Progress in Nickel Toxicology. Proc. 3rd. Int. Congress on Nickel 

Metabolism and Toxicology, Brown, S.S. and F.W. Sunderman, Jr., eds., Blackwell Publ. Co., 

Oxford, UK. pp. 89-92. 

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Armstrong Aerospace Mdcal Research Laboratory, Wright Patterson AFB, OH. 

Warner, J. S. 1979. Nickel carbonyl. Prenatal exposure, Science 203: 1194-1 195. 

Wehner, A. P., R H. Busch, R J. Olson, and D. K. Craig. 1975. Chronic inhalation of nickel oxide 

and cigarette smoke in hamsters, Am. Ind. Hyg. Assoc. J. 36: 801-809. (Cited in ATSDR 1988) 

Weischer, C. H., W. Kordel, and D. Hochrainex. 1980. Effects of NiC1, and NiO in Wistar rats after 

oral uptake and lnhalation exposure, respectively, Zenfral Bakreriol. Mikrobiol. Hyg. (B) 

171:336-351. (Citedin ATSDR 1988) 

White, M. A. and A. M. Boran. 1994. Urinary excretion of nickel in nickel-chromium electroplaters, 

In: Nickel and Human Health, Nieboer, E. and J.O. Nriagu, eds., John Wiley and Sons, Inc., 

New York, NY. pp. 89-96.


TRICHLOROETHENE 

MARCH 1993 

Prepared by 

Rosmarie A. Faust, PbD 






Prepared for 






Trichloroethene (TCE) is an industrial solvent used primarily in metal degreasing and 

cleaning operations. TCE can be absorbed through the lungs, mucous membranes, gastrointestinal 

tract, and the skin. TCE is extensively metabolized in humans to trichloroacetic acid and 

trichloroethanol, as well as to several minor metabolites, with most of the absorbed dose excreted 

in urine (ATSDR, 1989; U.S. EPA, 1985). 

Human and animal data indicate that exposure to TCE can result in toxic effects on a 

number of organs and systems, including the liver, kidney, blood, skin, immune system, reproductive 

system, nervous system, and cardiovascular system. In humans, acute inhalation exposure 

to TCE causes central nervous system symptoms such as headache, dizziness, nausea, and unconsciousness 

(U.S. EPA, 1985). Among the reported effects from occupational exposure studies are 

fatigue, light-headedness, sleepiness, vision distortion, abnormal reflexes, tremors, ataxia, 

nystagmus, increased respiration, as well as neurobehavioral or psychological changes. Cardiovascular 

effects include tachycardia, extrasystoles, EKG abnormalities, and precordial pain (Landrigan 

et al., 1987; Grandjean et al., 1955; Milby, 1968). The use of TCE as an anesthetic has been 

associated with cardiac arrhythmias (U.S. EPA, 1985). 

Cases of severe liver and kidney damage, including necrosis, have been reported in 

humans following acute exposure to TCE (Defalque, 1961), but these effects generally are not 

associated with long-term occupational exposures. In animals, TCE has produced liver enlargement 

with hepatic biochemical andor histological changes (Nomiyama et al., 1986; Kjellstrand 

et al., 1981, 1983; Stott et al., 1982; Tucker et al., 1982) and kidney enlargement, renal tubular 

alterations and/or toxic nephropathy (NTP, 1982, 1986% 1988). Also observed in animals were 

hematological effects (Tucker et al., 1982; Ma~a 

and Brancaccio, 1967) and immunosuppression 

(Sanders et al., 1982). Inhalation studies with rats indicate that TCE is a developmental toxicant 

causing skeletal ossification anomalies and other effects consistent with delayed maturation (Healy 

et al., 1982; Dorfinueller et al., 1979). TCE may cause dermatitis and dermographism (U.S. EPA, 

1985). 

Reference Doses 0 s ) and Reference Concentrations (RfCs) for subchronic and chronic 

oral and inhalation exposure to TCE am prtsently under review by EPA (U.S. EPA, 1992a). 

Epidemiologic studies have been inadequate to determine if a correlation exists between 

exposure to TCE and increased cancer risk. Chronic oral exposure to TCE increased the 

incidences of hepatocellular carcinomas in mice and renal adenocarcinomas and leukemia in rats 

(NTP, 1988; Maltoni et al., 1986; NTP, 1986% 1982; NCI, 1976). Chronic inhalation exposure 

induced lung and liver tumors in mice and testicular Leydig cell tumors in rats (Maltoni et al., 

1986, 1988; Fukuda et al., 1983; Bell et al., 1978). Although U.S. EPA's Science Advisory 

Board recommended a weight-of-evidence classification of C-B2 continuum (C = possible human 

carcinogen; B2 = probable human carcinogen), the agency has not adopted a current position on 

the weight-of-evidence classification (US. EPA, 1992b). In an earlier evaluation, TCE was 

assigned to weight-of-evidence Group B2, probable human carcinogen, based on tumorigenic 

responses in rats and mice for both oral and inhalation exposure and on inadequate data in humans 

(US. EPA, 1987, 1990). Carcinogen slope factors are l.lE-2 (mgAcg/day)-' and 6.OE-3 

1

(mgkg/day)-' for oral and inhalation exposure, respectively. The corresponding unit risks are 

3.2E-7 (pg/Ly' and 1.7E-6 (pg/rn'y', respectively (U.S. EPA, 1992b). 

2


Trichloroethene (trichlorothylene; TCE; CAS No. 79-0 1-6) is a colorless, highly volatile 

liquid that is miscible with water and a number of organic solvents (U.S. EPA, 1985). It has a 

molecular weight of 131.4, a boiling point of 87OC, and a density of 1.4642 at 20/4OC (Weast, 

1989). TCE is a man-made chemical and is not known to occur naturally. It is mainly used as 

a solvent in industrial degreasing and cleaning of metals, but is also used as a solvent for waxes, 

fats, resins, and oils, and in numerous other applications. Prior to 1977, TCE had been used as 

an anesthetic, grain fumigant, disinfectant, and extractant of spice oleoresins in food and of 

caffeine in the production of decaffeinated coffee. Workers in the vapor degreasing industry 

appear to be exposed to the highest atmospheric levels of TCE. TCE has been detected in both 

surface and ground waters; however, most (80-95%) TCE used is released to the atmosphere by 

evaporative losses (ATSDR, 1989). 

The evaluation of the toxicity of TCE is complicated by the presence or absence of 

stabilizers. Industrial grade TCE usually contains stabilizers such as triethylamine, triethanolamine, 

epichlorohydrin, or stearates, chemicals that can be toxic by themselves. In the absence 

of stabilizers, TCE readily decomposes to dichloroacetylene, phosgene, carbon monoxide, and 

hydrogen chloride. These decomposition products are also toxic (O'Donoghue, 1985). 



Trichloroethene can be absorbed through the lungs, digestive tract, skin, and mucous 

membranes. The primary route of human exposure to the chemical is through pulmonary uptake, 

which is rapid but requires about 8 hours to teach tissue equilibrium. The total dose absorbed is 

directly proportional to the concentration in inspired air, and for a given concentration, body 

burden increases with duration and frequency of exposure, and with exercise (U.S. EPA, 1985). 

After ingestion, 90-95% of a dose of 40-60 mgkg was recovered in expired air and in urine of 

rats, suggesting almost complete absorption of the compound (Daniel, 1963). Tsuruta (1978) 

estimated skin absorption by in vivo and in vitro techniques and reported rates of 7.82 to 12.1 

pg/min/cm2 in mice. 


Following uptake into the body, TCE is rapidly distributed from blood to all tissues, 

particularly adipose tissue, and appears in sweat and saliva (U.S. EPA, 1985). TCE readily passes 

through the placenta and was detected in the blood of babies at birth after the mothers had 

received TCE anesthesia (Laham, 1970). 

3


The principal site of TCE metabolism is the liver, although metabolism may also occur 

in the lungs, kidneys, spleen, and small intestine (ATSDR, 1989). The initial biotransformation 

may involve the formation of two intermediates, TCE epoxide and chloral. In man and animals, 

TCE is extensively metabolized to trichloroacetic acid, trichloroethanol, and trichloroethanol 

glucuronide. Several minor metabolites have also been identified, including oxalic acid, 

dichloroacetic acid, N-(hydroxyacetyl>aminoethanol, and carbon dioxide. Reactive intermediate 

metabolites, such as the epoxide, covalently bind to cellular macromolecules, principally protein 

and to a much smaller extent, DNA. It is estimated that humans metabolize between 40 and 75% 

of the retained dose (U.S. EPA, 1985). At relatively low TCE concentrations, saturation of TCE 

metabolism has not been demonstrated in humans. However, both oral and inhalation studies have 

provided evidence for saturation of TCE metabolism in rats (ATSDR, 1989). There are 

quantitative differences in the rates of metabolism in different species. For example, mice 

metabolize TCE at a greater rate than rats and as a result produce more tissue-binding metabolites 

in the liver and kidney when compared to rats (Stott et al., 1982). 


TCE is eliminated by two major processes, liver metabolism with subsequent elimination 

of metabolites and pulmonary excretion of the parent compound. In humans, most of retained 

TCE is excreted as urinary metabolites (58%); 5% or more may be excreted in the feces; and 

about 1 1% is eliminated through the lungs (ATSDR, 1989). In contrast, when TCE was given 

by gavage to rats, 10-20% of the dose was excreted in the urine as trichloroacetic acid and 

trichloroethanol, 0-0.5% as TCE in the feces, and 7245% as TCE in the expired air (Daniel, 

1963). 




3.1.1.1. Human 

Fatalities have been reported following accidental or intentional ingestion of TCE. The 

lethal oral dose for adults is approximately 7 g/kg (WHO, 1985). Accidental ingestion of TCE 

has resulted in inebriety, vomiting, diarrhea, collapse and coma, followed by either death or 

recovery with transient neurological sequelae (amnesia, headache, numbness, weakness of extremities, 

psychosis or hemiparesis). At autopsy, pulmonary edema and liver and kidney necrosis were 

observed Oefalque, 1961). Hepatorenal failure was reported in one fatal case of accidental 

ingestion of TCE (Kleinfield and Tabemhaw, 1954). There are indications that the hepatotoxic 

effects of TCE are enhanced by concomitant exposure to ethanol or isopropyl alcohol (IARC, 

1979). Case studies suggest that ingestion of 350-500 mL of TCE can produce cardiac arrhythmias 

(Dhuner et a]., 1957). 

. 

4

3.1.1.2. Animal 

Oral LD,,s for TCE are 2402 and 2443 mgkg for male and female mice, respectively, 

4920 mgkg for rats, and 5680 mgkg for dogs (ATSDR, 1989). 


3.1.2.1. Human 

Information on the subchronic oral toxicity of TCE in humans was Unavailable. 

3.1.2.2. Animal 

Male mice given 250-2400 mgkg TCE by gavage, 5 daydweek for 3 weeks exhibited a 

dose-related hepatocellular hypertrophy (Stott et al., 1982). Significantly increased liver weights 

were seen in male CD-1 mice given daily gavage doses of 240 mg/kg/day, but not 24 mgkg/day, 

for 14 days (Tucker et al., 1982). The same investigators administered TCE in drinking water 

to CD- 1 mice for 6 months at concentrations of 18-660 mg/kg/day (males) and 18-793 mgkg/day 

(females). Treatment-related effects included increased relative liver weights and increased 

urinary ketone and protein concentrations at 393 mg/kg/day (males) and increased liver and kidney 

weights at the highest doses in both sexes. Also observed at the highest doses were decreased 

erythrocyte and leukocyte counts and increased fibrinogen levels in males after 4 and 6 months 

and shortened prothrombin time in females after 6 months (Tucker et al., 1982). 

Sanders et al. (1982) evaluated the immune status of male and female CD-1 mice 

following exposure to TCE in drinking water at doses of 18-666 mgkg/day (males) and 18-793 

mgkg/day (females) for 4 or 6 months. The TCE-induced immunotoxic effects observed were 

more pronounced in females and included depressed cell-mediated response to sheep erythrocytes 

at 2 18 mgkg after 4 months and at 739 mg/kg/day after 6 months; depressed antibody-forming 

cell response at 2 437 mg/kg/day after 4 months but not after 6 months; and inhibited bone 

marrow stem cell colonization after 4 and 6 months. 


3.13.1. Human 

Information on the chronic oral toxicity of TCE in humans was unavailable. 


Renal effects characterized as cytomegaly were observed in F344 rats treated by gavage 

with 500 or 1000 mg/kg/day TCE, 5 daydweek for 103 weeks and in B6C3F, mice similarly 

treated with 1000 mg/kg/day OIJTP, 1982; 1986a). Also observed in rats were signs of central 

nervous system (CNS) toxicity, including ataxia, lethargy, convulsions, and hind limb paralysis. 

These effects were described as sporadic and transient. Cytomegaly of renal tubular cells and 

toxic nephropathy was seen in ACI, August, Marshall, and OsbornaMendel rats treated by gavage 

with 500 or 1000 mg/kg/day for 103-104 weeks (NTP, 1988).



Information on the developmental and reproductive toxicity of TCE in humans following 

oral exposure was unavailable. 


Rats exposed to TCE by gavage in corn oil at doses of 0, 10, 100, or 1000 mg/kg/day for 

2 weeks prior to and throughout mating to day 21 of gestation exhibited increased maternal 

mortality, decreased maternal weight gain, and decreased neonatal survival in the high-dose group 

(Manson et al., 1984). 

Two-generation fertility studies (NTP, 1985, 1986b) exposed male and female F344 rats 

and CD-1 mice to diets containing 75, 150, or 300 mg/kg/day TCE. In tats, the two higher doses 

caused a reduction in the number of live pupdlitter and the highest dose caused increased testis 

and epididymis weights (combined) in the F, generation. Mice exposed to the highest dose 

exhibited increased neonatal mortality, increased testis and epididymis weights (combined) in F, 

mice, and reduced sperm motility in F, and F, mice. 


The development of a Reference Dose for TCE is under review by EPA (U.S. EPA, 

1992a). 



3.2.1.1. Human 

Acute inhalation exposure to TCE causes central nervous system symptoms, such as 

headache, dizziness, nausea, and in some cases unconsciousness. Lower levels may affect visual 

and motor performance (U.S. EPA, 1985). Case reports reviewed by Grant (1974) indicate that 

acute exposure to TCE may produce paralysis of the trigeminal nerve or extraocular muscle as 

well as vision disturbances. It was suggested that the observed visual effects were produced by 

decomposition products such as dichlomacetylene rather than by TCE. Although permanent 

central nervous system damage has been reported after exposure to TCE, respiratory and cardiac 

failure are the likely causes of death following acute inhalation exposure. The use of TCE as an 

anesthetic has been associated with cardiac arrhythmias, bradydia, atrial and ventricular 

premature contractions, and ventricular extrasystole (U.S. EPA, 1985). In controlled studies of 

human exposure, impairment of psychophysiological function was seen in volunteers exposed to 

1 10 ppm for two 4-hour periods. Exposure to 200 ppm for 7 hours over 5 days produced fatigue 

and sleepiness (IARC, 1979). 

6

Cases of severe liver damage, including necrosis, resulting from acute occupational 

exposure to lethal concentrations of TCE have been reported. A few case reports described renal 

dysfunction and failure resulting &om occupational or intentional exposure (U.S. EPA, 1985). 


Reported LC,, values for TCE range from 7,480 to 49,000 ppm for mice and from 12,500 

to 26,300 ppm for rats (ATSDR, 1989). Rats exposed to 250-4,OOO pprn TCE for up to 4 hours 

exhibited decreased avoidance responses (Kishi et al., 1986). Sensitization of the heart to 

epinephrine-induced arrhythmia was observed in dogs exposed to 5,000-10,000 ppm for 10 min 

and in rabbits exposed to 6,000 ppm for 1 hour (U.S. EPA, 1985). Chakrabarti and Tuchweber 

(1988) reported that rats exposed to 1,000 or 2,000 ppm TCE for 6 hours exhibited significantly 

increased urinary levels of gamma-glutamyltranspeptidase activity, and glucose and protein concentrations, 

which are biochemical changes indicative of renal injury. 

3.23. Subchronic Toxicity 

3.2.2.1. Human 

Landrigan et al. (1987) reported that seven of nine TCE-exposed workers involved in a 

metal degreasing operation experienced fatigue, light-headedness, sleepiness, shortness of breath, 

dyspnea on exertion, palpitations, nausea, and headache. Similar symptoms were not reported in 

non-exposed controls. The mean duration of employment of exposed workers was 4.4 years. 

Breathing zone levels of TCE for the five workers who were exposed to the highest TCE concentrations 

ranged h m 117 to 357 mdm’ and averaged 89 mg/m’. Short-term peak exposures 

ranged h m 413 to 2000 mg/m3. 

Grandjean et al. (1955) evaluated the effects of TCE in 50 workers who had been occupationally 

exposed for an average of 3.75 years. Signs of severe neurological disturbances (vision 

distortion, abnormal reflexes, slow tremors, ataxia, or nystagmus) occurred in 28% of the exposed 

workers. Symptoms of autonomic nervous system involvement (excessive respiration, circulatory 

symptoms, tremors, gastrointestinal upset, palpitations, tachycardia, extrasystoles, precordial pain, 

and pronounced modification of dermographism) occurred in 36% of the workers. Slight to 

moderate psychic disturbances (short-term memory loss, slow understanding, emotional instability, 

and fewer word associations) occumd in 34% of the workers. 

In a case study reported by Milby (1968), vomiting and abdominal cramps, as well as an 

erratic heart beat, an abnormal EKG, sleepiness, weakness, and loss of appetite occd in a 

worker who had been exposed to TCE for 1 month. Breathing zone measurements after the 

incident ranged from 260 to 280 ppm TCE. James (1963) reported fatty degeneration of the liver 

in a worker who had become addicted to TCE over a 9-year period. 

3.233. Animal 

Nomiyama et al. (1 986) found significant hepatic dysfunction in male SpragueDawley 

rats continuously exposed to 50,200, or 800 ppm TCE for 12 weeks. Liver weight, total protein, 

albumidglobulin ratio, plasma glutamic pyruvate transaminase activity, triglyceride, cholesterol 

ester ratio, and cholinesterase were affected. Renal dysfunction as indicated by glycosuria and 

7

alterations in plasma creatine, urine nitrogen, uric acid, and creatine clearance, as well as 

concentration-related changes in hematocrit, and erythrocyte, reticulocyte, and erythroblast counts 

were also seen. 

Rats exposed to 55 ppm TCE for 14 weeks exhibited enlarged livers but no other adverse 

hepatic effects (Kimmerle and Eben, 1973). Increased relative liver weight was the only hepatic 

effect reported in male and female rats, mice, and gerbils exposed to concentrations up to 150 

ppm TCE for 30 days, but the effect was more pronounced in mice than in rats or gerbils (Kjellstrand 

et al., 1981). Histological alterations of the liver characterized by cellular atrophy were 

associated with liver enlargement in a study with mice exposed to 37 ppm TCE for 30 days 

(Kjellstrand et al., 1983). 

Haglid et al. (1981) reported that continuous exposure to 60 ppm TCE for 3 months 

resulted in biochemical and histopathological changes in the brain of Mongolian gerbils. These 

changes are indicative of astroglial hypertrophy andor proliferation. Behavioral changes (reduced 

activity) were seen in rats exposed for 12 weeks to TCE at concentrations ranging from 100 to 

1000 ppm (Silverman and Williams, 1975). 

Exposure to 2790 ppm TCE, 4 hodday, 6 daydweek for 45 days caused myelotoxic 

anemia in rabbits (Maim and Brancaccio, 1967). A concentration-related decrease in deltaaminolevulinate 

dehydratase activity (an enzyme involved in heme regulation) was seen in rats 

continuously exposed to 50, 400, or 800 ppm for 10 days (Fujita et ai., 1984). 


3.23.1. Human 

Bardodej and Vyskocif (1956) evaluated 75 individuals in dry cleaning and metal dew- 

ing workshops who had been exposed to 5-632 ppm TCE for 1-25 years. Prenarcotic symptoms 

of chronic exposure included headache, sleepiness, a drunken feeling, nausea, and tinnitus. Other 

symptoms were intolerance to heat and sunlight, hot flashes, perspiration, exaggerated heart beat, 

respiratory difficulties, reddening of the skin after mechanical or heat insults, intolerance to 

alcohol, and dermographism. Cardiovascular effects included vasomotor changes, bradycardia, 

supraventricular extrasystole, and conduction velocity disturbances. In addition, numerous 

subjective CNS effects were reported. There was no evidence of liver or kidney damage. 


Male Sprague-Dawiey rats were exposed to 100,300, or 600 ppm TCE, 7 hodday, 5 

daydweek for 108 weeks. Renal cytokaryomegaly occurred at 300 and 600 ppm, but not at 100 

ppm (Maltoni et al., 1988, 1986). 

8



Two studies suggest that medical personnel exposed to various solvents, including TCE, 

are susceptible to reproductive effects. A survey of operating mom personnel in the U.S. showed 

that women exposed to anesthetic waste gases (containing TCE) were subject to increased risks 

of spontaneous abortions and congenital abnormalities in their children. Increased risks of 

congenital abnormalities were also present among non-exposed wives of male operating room 

personnel (Cohen et al., 1974). Another survey involving 7949 physicians in the United Kingdom 

revealed a significantly higher fiequency of spontaneous abortions in women anesthesiologists 

compared with non-anesthesiologists. The frequency of minor abnormalities in children of 

exposed fathers was 3.09% compared with 2.35% for nonexposed fathers (Knill-Jones et al., 

1975). 


Dorfmueller et al. (1979) exposed female rats to 1800 ppm TCE for two weeks prior to 

mating and for 20 days during gestation and found no evidence of maternal toxicity, embryotoxicity, 

severe teratogenicity, or behavioral deficits in the offspring. Offspring of rats exposed 

during pregnancy alone showed significant increases of skeletal and soft tissue abnormalities. 

Reduced body weights were seen in offspring of rats with pregestational exposure alone. 

Wistar rats exposed to 100 ppm TCE for 4 hours daily on days 8-21 of gestation exhibited 

increased resorptions, reduced fetal weight gains, and increased frequency of bipartite or absent 

skeletal ossification centers (Healy et al., 1982). However, Sprague-Dawley rats and Swiss 

Webster mice exposed to 300 ppm TCE on days 5-15 of gestation exhibited no significant 

matemal, embryonal, or fetal toxicity and no evidence of teratogenicity (Schwetz et al., 1975). 

Sperm abnormalities were reported in mice exposed to 2000 ppm anesthetic-grade TCE 

vapor, 4 houdday for 5 days (Land et al., 1979) or to 500 ppm TCE, 7 houdday for 5 days 

(Beliles et al., 1980). 

33.5. Reference Concentration 

The development of a Reference Concentration is under review by EPA (U.S. EPA, 

1992a). 

3.3. OTHER ROUTES OF EXPOSURE 


33.1.1. Human 

Acute dermal exposure to TCE has been associated with reddening and dermatographic 

skin bums. The vapor may cause general dermatitis (U.S. EPA, 1985). Hypersensitivity to TCE, 

resulting in severe dermatological abnormalities, such as Steven-Johnson syndrome (erythema 

multiformis major), was reported in one study (Phoon et al., 1984). A skin condition termed 

9

“degreasers’ flush” has been reported in workers who had consumed alcohol before or after 

exposure to TCE (Stewart et al., 1974). Direct contact of TCE vapor or liquid with the eye 

causes superficial damage to the cornea, but complete recovery occurs within a few days (Grant, 

1974). 

3.3.1.2. Animals 

The dermal LD,, for TCE in rabbits is > 20 m ug (Smyth et ai., 1969). 


Information on the subchronic toxicity of TCE by other routes of exposure in humans or 

animals was unavailable. 


Information on the chronic toxicity of TCE by other routes of exposure in humans or 

animals was unavailable. 


Information on the developmental and reproductive toxicity of TCE by other routes of 

exposure in humans or animals was unavailable. 

3.4. TARGET ORGANS/CRITICAL EFFECTS 



- 

1. Liver: Mice developed increased liver weight and hepatocellular hypertrophy 

following oral exposure to TCE. 

2. Kidney: Rats and mice developed increased kidney weights, cytomegaly of 

renal tubular cells, and toxic nephropathy following oral exposure to TCE. 


1. Central nervous system: Chronic oral exposure of rats caused transient CNS 

effects including ataxia, lethargy, convulsions, and hind limb paralysis. 

2. Reproduction: Increased neonatal mortality, increased testis and epididymis 

weights, and reduced sperm motility was seen in a two-generation fertility study 

with rats. 

3. Hematopoietic system: Rats exposed to TCE in drinking water exhibited 

decreased erythrocyte and leukocyte counts, increased fibrinogen levels, and 

shortened prothrombin time. 

10

4. Immune system: Mice exposed to TCE in drinking water exhibited immunotoxic 

effects characterized by delayed hypersensitivity, suppressed antibody 

forming cell response, and decreased bone marrow stem cell colonization. 

3.4.2. Inhalation Exposures 


1. Nervous system: CNS symptoms in workers exposed to TCE by inhalation 

included headache, sleepiness, vision distortion, nausea, abnormal reflexes, 

tremors, ataxia, nystagmus, and increased respiration. TCE exposure may also 

cause psychic disturbances such as short-term memory loss and fewer word 

associations. Subchronic exposure of gerbils induced biochemical and 

histopathological changes in the brain. 

2. Liver: Following inhalation exposure to TCE, rodents developed enlarged 

livers and biochemical changes indicative of liver damage. Liver damage in 

humans is primarily associated with acute exposure to TCE. The hepatotoxic 

effects of TCE are enhanced by concomitant exposure to alcohol. 

3. Kidney: Rats developed renal cytokaryomegaly following chronic inhalation 

exposure to TCE. 

4. Cardiovascular system: Occupational exposure to TCE has been associated 

with vasomotor changes, tachycardia, bradycardia, extrasystoles, conduction 

disturbances, and precordial pain. TCE sensitizes the heart to diac 

arrhythmias. 

5. Hematopoietic system: Inhalation of TCE induced myelotoxic anemia in 

rabbits and produced dose-related changes in several hematological indices in rats. 

6. Reproduction: Inhalation studies with rodents indicate that TCE may cause 

increased resorptions, reduced fetal body weight, and ossification anomalies. 

Exposure to high concentrations produced spem abnormalities in mice. 


Skin: Reddening of the skin following mechanical or heat insults and demographism 

was seen in workers exposed to TCE by inhalation. 

11

3.4.3. Other Routes of Exposure 

Skin: Dermal exposure to TCE may cause general dermatitis and hypersensitivity. 

"Degreasers' flush" may occur in conjunction with alcohol consumption. 




Mortality statistics for 1969- 1979 in Woburn, Massachusetts revealed a significantly 

elevated rate of childhood leukemia. Two of the eight municipal wells serving the community 

were known to be contaminated with TCE and several other chlorinated organic compounds, but 

the causes of leukemia were not identified in these studies (Kotelchuck and Parker, 1979; Parker 

and Rosen, 1981). 


Maltoni et al. (1986) treated male and female Sprague-Dawley rats by gavage with TCE 

(99.9% pure) in olive oil at doses of 50 or 250 mg/kg/day, 4-5 daydweek for 52 weeks. There 

was a dose-related increase in the incidence of leukemia in males, but no increased tumor 

incidence in females. 

Significantly increased incidences of hepatocellular carcinomas occumd in B6C3F, mice 

that were administered time-weighted-average doses of 1170 or 1340 mg/kg/day (males) or 870 

or 1740 mg/kg/day (females) by gavage, 5 daydweek for 78 weeks. No compound-related 

carcinogenic effects were found in Osborne-Mendel rats similarly treated with 550 or 1100 

mg/kg/day, but this finding was inconclusive because of poor survival. The TCE used in the 

study was 299% pure but contained stabilizers, including epichlorohydrin, a known carcinogen 

(NCI, 1976). 

Studies by NTP (1982, 1986a) showed significantly increased incidences of hepatocellular 

carcinomas in male and female B6C3F, mice treated by gavage with epichlorohydrin-free TCE 

at a dose of 1000 mg/kg/day, 5 daydweek for 103 weeks. F344 rats treated with 1000 mg/kg/day 

by the same regimen exhibited renal adenomas and adenocarcinomas; this effect was not seem at 

500 mg/kg/day or in females at either dose level. Due to poor survival, the results in rats were 

considered inadequate. A third NTP study (NTP, 1988) exposed groups of male and female ACI, 

August, Marshall, and Osborne-Mendel rats by gavage to epichlorohydrin-free TCE in corn oil 

at doses of 0, 500, or 1000 mgkg, 5 daydweek for 103 weeks. There were significantly 

increased incidences of renal tubular cell neoplasms in low dose male Osborne-Mendel rats and 

interstitial cell neoplasms of the testis in high-dose Marshall rats. This study also was considered 

inadequate for assessment of carcinogenic activity because of toxic nephrosis and low survival. 

Henschler et ai. (1984) compared the carcinogenicity of TCE stabiIized with epichlorohydrin 

(0.8%) or 1,2-epoxybutane (0.8%) to that of industrial-grade TCE in male and female 

12

ICRMa Swiss mice. TCE was administered daily by gavage (2.4 gkg, females; 1.8 g/kg, males) 

for 18 months, with and without the addition of the epoxides. Animals exposed to epichlorohydrinor 

1,2-epoxybutane-stabilized TCE exhibited an increased incidence of papillomas and carcinomas 

of the forestomach. This effect was not observed without stabilizers. 

4.2. INHALATION EXPOSURES 


Epidemiologic studies conducted by Axelson et al. (1978), Malek et al. (1979), and Tola 

et al. (1980) reported no significant excess cancer risks associated with occupational exposure to 

TCE, but the studies do not permit definite conclusions because of various study limitations such 

as inadequate latency periods, small sample size, lack of analysis by tumor site, and multiple 

chemical exposure (ATSDR, 1989; U.S. EPA, 1985). An update of one of the studies (Axelson, 

1986) found a slight increase of bladder cancer and lymphomas in an expanded cohort study; 

however, details of TCE exposure were not given. A retrospective cohort mortality study of drycleaning 

and/or laundry workers (Blair et al., 1979) found significant increases in the incidence 

of cancer at several sites (lung/bronchVtrachea, cervix, and skin) among a group of 330 deceased 

workers. This cancer increase was possibly due to dry-cleaning chemicals (carbon tetrachloride, 

tetrachloroethylene, and TCE) but could not be related to TCE alone. Paddle (1983) examined 

tumor registry records in Great Britain and found no association between liver cancer and TCE 

exposure in workers employed in one TCE production facility. 

4.22. Animal 

Bell et al. (1978) reported no carcinogenic effects in Charles River rats exposed to 

technical grade TCE at concentrations of 0, 100,300, or 600 ppm, 6 hodday, 5 daydweek for 

24 months. Hepatocellular carcinomas were seen in B6C3F1 mice similarly exposed to TCE, with 

a greater incidence of tumors occurring in males than in females. The TCE employed contained 

0.148% epichlorohydrin and several other additives. 

Wistar rats, NMR mice, and Syrian hamsters were exposed to purified TCE at 0,100, or 

500 ppm, 6 houdday, 5 daydweek for 18 months (Henschler et al., 1980). The only statistically 

significant effect was an increased incidence of malignant lymphomas in female mice. US. EPA 

(1987) suggested that lymphoma susceptibility may have been enhanced by virus and immunosuppression. 

Fukuda et al. (1983) exposed female ICR mice and Sprague-Dawley rats to reagent-grade 

TCE (containing 0.019% epichlorohydrin) at concentrations of 0, 50, 150, or 450 ppm, 7 

houdday, 5 daydweek for 104 weeks. Although then were a number of tumors at several sites 

in rats and mice, only lung adenocarcinomas were significantly increased in mice at the two 

highest concentrations compared with controls. 

Maltoni et ai. (1986, 1988) exposed male and female Sprague-Dawley rats, Swiss mice, 

and B6C3F1 mice to 100,300, or 600 ppm epoxide-fiee TCE, 7 hodday, 5 daydweek for 104 

weeks (rats) or 78 weeks (mice). Statistically significant increased incidences of tumors included 

testicular Leydig cell tumors in rats at 2100 ppm, lung adenomas in male Swiss mice at 2300 

13

ppm, hepatomas in male Swiss mice at 600 ppm, and lung adenomas in female B6C3F, mice at 

600 ppm. 



Information on the carcinogenicity of TCE in humans by other routes of exposure was 

unavailable. 


Three weekly topical applications of 1 mg TCE for 581 days did not induce skin tumors 

in female Swiss ICRha mice. Negative results were also reported in a tumor initiation assay in 

which mice received a single dermal application of 1 mg TCE, followed by 3 weekly applications 

of a phorboi ester for 581 days (Van Duuren et al., 1979). 


Classification: C-B2 continuum (C = possible human carcinogen; B2 = probable human 

carcinogen) (U.S. EPA, 1992b). 

Comment: This classification is a recent recommendation by EPA's Science 

Advisory Board. However, EPA has not adopted a current position on the 

weight-of-evidence classification (U.S. EPA, 1992b). An earlier evaluation (U.S. 

EPA, 1990) classified TCE as a weight-of-evidence B2 chemical, based on tumor 

responses in rats and mice exposed to TCE by the oral and inhalation routes of 

exposure. The available epidemiological data were inadequate to refute or 

demonstrate a human carcinogenic potential (U.S. EPA, 1987). 


4.5.1. Oral 

SLOPE FACTOR: l.lE-2 (mg/kg/day)*' (US. EPA, 1992b) 

UNIT RISK. 3.2E-7 (pg/L)-'(US. EPA, 1992b) 

PRINCIPAL STUDIES: NCI (1976); NTP (1983); U.S. EPA (1985, 1987, 1988) 

COMMENT: The slope factor and unit risk values were provided in U.S. EPA (1985). 

However, the carcinogenicity files for TCE have been withdrawn from IRIS pending resolution 

of the weight-of-evidence classification. 

4.5.2. Inhalation 

SLOPE FACTOR 

UNIT RISK: 


6.OE-3 (mg/kg/day)-' (U.S. EPA, I992b) 

1.E-6 (pg/m3y* (US. EPA, 1992b) 

Maltoni et al. (1986); Fukuda et al. (1983); U.S. EPA (1988) 

14

COMMENT: The slope factor and unit risk values were provided in U.S. EPA (1987). 

However, the carcinogenicity files for TCE have been withdrawn from IRIS pending resolution 

of the weight-of-evidence classification. 

15

5. REFERENCES 


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Bell, Z.G., K.H. Olson and T.J. Benja. 1978. Find Report of Audit Findings of the Manufacturing 

Chemists Association: Administered Trichloroethylene Chronic Inhalation Study at Industrial 

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Blair, A., P. Decoufle and D. Grauman. 1979. Causes of death among laundry and dry cleaning 

workers. Am. J. Public Health 69: 508-5 1 1. 

Chakrabarti, S.K. and B. Tuchweber. 1988. Studies of acute nephrotoxic potential of trichlomethylene 

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Dhuner, K.G., P. Nordqvist and B. Renstrom. 1957. Cardiac irregularities in trichloroethylene 

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Dorlinueller, M.A., S.P. Heme, R.G. York, et al. 1979. Evaluation of teratogenicity and 

behavioral toxicity with inhalation exposure of maternal rats to trichloroethylene. Toxicology 14: 

153-166. 

16

Fujita, H., A. Koizumi, M. Yamamoto, et al. 1984. Inhibition of delta-aminolevulinate dehydratase 

in trichloroethylene-exposed rats, and the effects on heme regulation. Biochem. Biophys. 

Acta 800: 1-10. (Cited in ATSDR, 1989) 

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in mice and rats. Ind. Health 21: 243-254. 

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to trichloroethylene in mechanical engineering. Brit. J. Ind. Med. 12: 131-142. 

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Thomas, Springfield, IL, pp. 1034-1045. 

Haglid, K.G., C. Briving, H.-A. Hanson, et al. 1981. Trichloroethylene: Long-lasting changes 

in the brain after rehabilitation. Neurotoxicology 2: 659-673. 

Healy, T.E.J., T.R. Poole and A. Hopper. 1982. Rat fetal development and maternal exposure 

to trichloroethylene at 100 ppm. Br. J. Anaesth. 54: 337-341. 

Henschler, D., H. Elasser, W. Romer, et al. 1984. Carcinogenicity study of trichloroethylene, 

with and without epoxide stabilizers in mice. J. Cancer Res. Clin. Oncol. 107: 149-156. 

Henschler, D., W. Romer, H.M. Elasser, et al. 1980. Carcinogenicity study of trichloroethylene 

by long-tern inhalation in the animal species. Arch. Toxicol. 43: 237-248. 

IARC (International Agency for Research on Cancer). 1979. Trichloroethylene. In: IARC 

Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to Humans. Some 

Halogenated Hydrowbons, Vol. 20. World Health Organization, Lyon, France, pp. 545-572. 

James, W.R.L. 1963. Fatal addiction to trichloroethylene. Br. J. Ind. Med. 20: 47-49. 

Kimmerle, G. and A. Eben. 1973. Metabolism, excretion, and toxicology of trichloroethylene 

after inhalation. 1. Experimental exposures on rats. Arch. Toxicol. 30: 115-126. 

Kishi, R., I. Harabuchi, T. Ikeda, et al. 1986. Effects of trichloroethylene vapor on schedulecontrolled 

behavior in relation to blood and brain concentration, dose and time. Toxicol. Lett. 

3 l(Supp1.): 150. 

Kjellstrand, P., B. Holmquist, P. Ah, et al. 1983. Trichlorothylene: Further studies of the 

effects on body and organ weights and plasma butyryl cholinesterase activity in mice. Acta 

Pharmacol. Toxicol. 53: 375-384. 

Kjellstrand, P., M. Kanje, L. Manson, et al. 1981. Trichloroethylene: Eff& 

weights in mice, rats, and gerbils. Toxicology 21: 105-115. 

on body and organ 

Kleinfield, M. and I.R. Tabershaw. 1954. Trichloroethylene toxicity: Report of five fatal cases. 

AMA Arch. Ind. Hyg. Occup. Med. 10: 134-141. 

. 

17

Knill-Jones, R.P., B.J. Newman and A.A. Spence. 1975. Anaesthetic practice and pregnancy. 

Lancet 2: 807-809. 

Kotelchuck, M. and G. Parker. 1979. Woburn Health Data Analysis, 1969-1 979. Massachusetts 

Department of Health. (Cited in ATSDR, 1989) 

Laham, S. 1970. Studies on placental transfer: Trichloroethylene. Ind. Med. 39: 46-49. (Cited 


Land, P.E., E.L. Owen and H.W. Linde. 1979. Mouse sperm morphology following exposure 

to anesthetics during early spermatogenesis. Anesthesiology 5 1 : S259. 

Landrigan, P.J., G.F. Stein, J.R. Kominski, et al. 1987. Common-source community and 

industrial exposure to trichloroethylene. Arch. Environ. Health 42: 327-332. 

Malek, B., B. Kremarova and A. Rodova. 1979. An epidemiological study of hepatic tumor 

incidence in subjects working with trichloroethylene. 11. Negative result of retrospective 

investigations in dry cleaners. Pracov. Lek. 31: 124-126. (Cited in ATSDR, 1989) 

Maltoni, C., G. Lefemine and G. Cotti. 1986. Experimental Research on Trichloroethylene 

Carcinogenesis. C. Maltoni and M.A. Mehlman, Eds., Archives of Industrial Carcinogenesis 

Series, Vol. V. Princeton Scientific Publishing Co., Princeton, NJ, p. 393. (Cited in ATSDR, 

1989) 

Maltoni, C., G. Lefemine, G. Cotti, et al. 1988. Long-term carcinogenicity bioassays on 

trichloroethylene administered by inhalation to SpraguaDawley rats and Swiss and B6C3F, mice. 

Ann. N.Y. Ad. Sci. 534: 316-342. 

Manson, J.M., M. Murphy, N. Richdale, et al. 1984. Effkcts of oral exposure to trichloroethylene 

on female reproductive function. Toxicology 32: 229-242. 

Mazza, V. and A. Brancaccio. 1967. Characteristics of the formed elements of the blood and 

bone marrow in experimental trichloroethylene intoxication. Folia Med. 50: 3 18-324. (Cited in 

U.S. EPA, 1985) 

Milby, T.H. 1968. Chronic trichloroethylene intoxication. J. Occup. Med. 10: 252-254. 

NCI (National Cancer Institute). 1976. Carcinogenesis Bioassay of Trichloroethylene. CAS No. 

79-01-6. U.S. Department of Health, Eduction, and Welfare, National Institutes of Public Health, 

76-802. NCI-CG-TR-2. 

Nomiyama, K., H. Nomiyama and H. Ami. 1986. Reevaluation of subchronic toxicity of 

trichloroethylene. Toxicol. Lett. 3 l(Supp1.): 225. 

NTP (National Toxicology Program). 1982. Carcinogenesis Bioassay of Trichloroethylene in 

F344 Rats and B6C3F, Mice. CAS No. 79-01-6. U.S. Department of Health and Human Services, 

National Institutes of Health, Bethesda, MD. NTP 81-84, NIH Publ. 82-1799. 

18

NTP (National Toxicology Program). 1983. Carcinogenesis Bioassay for Trichloroethylene. U.S. 

Department of Health and Human Services, National Institutes of Health, Bethesda, MD. NTP 

243, NIH Publ. 83-01799. 

NTP (National Toxicology Program). 1985. Trichloroethylene: Reproduction and Fertility 

Assessment in CD-1 Mice When Administered in the Feed. U.S. Department of Health and 

Human Services, National Institutes of Health, Bethesda, MD. NTP-86-068. 

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Trichloroethylene (CAS No. 79-01-6) in F344 Ratsand B6C3F, Mice. U.S. Department of Health 

and Human Services, National Institutes of Health, Bethesda, MD. NTP TR 243. 

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Assessment in F344 Rats when Administered in the Feed. Final Report. U.S. Department of 

Health and Human Services, National Institutes of Health, Bethesda, MD. NTP-86-085. 

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(CAS No. 79-01-6) in Four Strains of Rats (ACI, August, Marshall, Osborne-Mendel) 

(Gavage Studies). U.S. Department of Health and Human Services, National Institutes of Health, 

Bethesda, MD. NTP TR 273. 

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Press, Boca Raton, FL, pp. 1 1 1-1 13. 

Paddle, G.M. 1983. Incidence of liver cancer and trichloroethylene manufacture: Joint study by 

industry and cancer registry. Br. Med. J. 286: 846. (Cited in U.S. EPA, 1985) 

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Massachusetts Department of Public Health. (Cited in ATSDR, 1989) 

Phoon, W.H., M.O.Y. Chan, V.S. Rajan, et al. 1984. Stevens-Johnson syndrome associated with 

occupational exposure to trichlorethylene. Contact Dermatitis 10: 270-276. (Cited in U.S. EPA, 

1985) 

Sanders, V.M., A.N. Tucker, K.L. White, Jr., et al. 1982. Humoral and cell-mediated immune 

status in mice exposed to trichloroethylene in drinking water. Toxicol. Appl. Phannacol. 62: 358- 

368. 

Schwetz, B.A., K.J. Leong and P.J. Gehring. 1975. The effect of maternally inhaled trichloroethylene, 

perchloroethylene, methylchloroform, and methylene chloride on embryonal and fetal 

development in mice and rats. Toxicol. Appl. Phannacol. 32: 84-96. 

Silverman, A.P. and H. Williams. 1975. Behavior of rats exposed to trichloroethylene vapors. 

Br. J. Ind. Med. 32: 308-315. (Cited in ATSDR, 1989) 

Smyth, H.F., C. Caqmter, C.S. Weil, et al. 1969. Range-finding toxicity data List VII. Am. 

Ind. Hyg. Assoc. J. 30: 470-476. 

19

Stewart, R.D., C.L. Hake and J.E. Peterson. 1974. "Degreasers' flush": Dermal response to 

trichloroethylene and ethanol. Arch. Environ. Health 29: 1-5. 

Stott, W.T., J.F. Quast and P.G. Watanabe. 1982. Pharmacokinetics and macromolecular 

interactions of trichloroethylene in mice and rats. Toxicol. Appl. Pharmacol. 62: 137-151. 

Tola, S., R. Vilhumen, E. Jarvinen, et al. 1980. A cohort study on workers exposed to trichlorethylene. 

J. Occup. Med. 22: 737-740. 

Tsumta, H. 1978. Percutaneous absorption of trichloroethylene in mice. Ind. Health 16: 145- 

148. (Cited in ATSDR, 1989; U.S. EPA, 1985) 

Tucker, A.N., V.M. Sanders, D.W. Barnes, et al. 1982. Toxicology of trichloroethylene in the 

mouse. Toxicol. Appl. Pharmacol. 62: 351-357. 

U.S. EPA. 1985. Health Assessment Document for Trichloroethylene. Final Report. Ofice of 

Health and Environmental Assessment, Environmental Criteria and Assessment Office, Research 

Triangle Park, NC. EPA/600/8-82/006F. 

U.S. EPA. 1987. Addendum to the Health Assessment Document for Trichloroethylene. 

Updated Carcinogenicity Assessment for Trichloroethylene. External Review Draft. Office of 

Health and Environmental Assessment, Office of Research and Development, Washington, DC. 

EPkV600f 8-82/006FA, PB 87-228045. 

U.S. EPA. 1988. Updated Health Effects Assessment for Trichloroethylene. Prepared by the 

Ofice of Health and Environmental Assessment Office, Cincinnati, OH, for the Office of 

Emergency and Remedial Response, Washington, DC. 

U.S. EPA. 1990. Trichloroethylene. Integrated Risk Information System (IRIS). Environmental 

Criteria and Assessment Ofice, Office of Health and Environmental Assessment, Cincinnati, OH. 

U.S. EPA. 1 992a. Trichloroethylene. Integrated Risk Information System (IRIS). Environmental 

Criteria and Assessment Office, Office of Health and Environmental Assessment, Cincinnati, 

OH. 

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(TCE) (CASRN 79-01-6), dated Dec. 14, 1992. 

Van Duuren, B.L., B.M. Goldschmidt, G. Lowengat, et al. 1979. Carcinogenicity of halogenated 

olefinic and aliphatic hydrocarbons in mice. J. Nat. Cancer Inst. 63: 1433-1439. 

Weast, R.C., J.A. Spadaro, R.O. Becker, et al. 1988-1989. Handbook of Chemistry and Physics, 

69th ed. CRC Press, Inc., Boca Raton, FL., pp. (B)127-128. 

WHO (World Health Organization). 1985. Environmental Health Criteria 50. Trichloroethylene. 

World Health Organization, Geneva, Switzerland. 

20

TOXICITY SUMMARY 

for 

VANADIUM AND VANADIUM COMPOUNDS 

December 1991 

Prepared by: 

Dennis M. Opresko, Ph.D. 






Prepared for: 




under Contract No. DE-ACO5-84OR2 1400 

.

This page intentionally le# blank


Vanadium is a metallic element that occurs in six oxidation states and numerous inorganic 

compounds. Some of the more important compounds are vanadium pentoxide (V,O,), sodium 

metavanadate (NaVO,), sodium orthovanadate (N%VO,), vanadyl sulfate (VOSO,), and 

ammonium vanadate (NH,VO,). Vanadium is used primarily as an alloying agent in steels and 

non-ferrous metals (ATSDR, 1990). Vanadium compounds are also used as catalysts and in 

chemical, ceramic or specialty applications. 

Vanadium compounds are poorly absorbed through the gastrointestinal system (0.5-2% 

of dietary amount) (NRCC, 1980; ICRP, 1960; Byrne and Kosta, 19781, but slightly more readily 

absorbed through the lungs (20-25%) (ICRP, 1960; Davies and Bennett, 1983). Absorbed 

vanadium is widely distributed in the body, but short-term localization occurs primarily in bone, 

kidneys, and liver (Vouk, 1979; Roshchin et al., 1980; Parker et al., 1980; Sharma et al., 1980; 

Wiegmann et al., 1982). In the body, vanadium can undergo changes in oxidation state 

(interconversion of vanadyl(+4) and vanadate (+5) forms) and it can also bind with blood protein 

‘(transferin) (Harris et al., 1984). Vanadium is excreted primarily in the feces following oral 

exposures and primarily in the urine following inhalation exposures (Tipton et al., 1969; ATSDR, 

1990). 

The toxicity of vanadium depends on its physico-chemical state; particularly on its valence 

state and solubility. Based on acute toxicity, pentavalent NH,VO, has been reported to be more 

than twice as toxic as trivalent VCl, and more than 6 times as toxic as divalent VI,. Pentavalent 

V,O, has been reported to be more than 5 times as toxic as trivalent V,O, (Roschin, 1967). In 

animals, acutely toxic oral doses cause vasoconstriction, diffuse desquamative enteritis, congestion 

and fatty degeneration of the liver, congestion and focal hemorrhages in the lungs and adrenal 

cortex (Gosselin et ai., 1984). Minimal effects seen after subchronic oral exposures to animals 

include diarrhea, altered renal function, and decreases in erythrocyte counts, hemogloblin, and 

hematocrit @omingo et al., 1985; Zaporowska and Wasilewski, 1990). In humans, intestinal 

cramps and diarrhea may occur following subchronic oral exposures. These studies indicate that 

for subchronic and chronic oral exposures the primary targets are the digestive system, kidneys, 

and blood. 

Reference Doses (RfD) for chronic oral exposures are: 0.007 mg/kg/day for vanadium; 

0.009 mg/kg/day for vanadium pentoxide; 0.02 mgikg/day for vanadyl sulfate; and 0.001 

mg/kg/day for sodium metavanadate (U.S. EPA, 1987, 1991qb). The subchronic RfDs for these 

compounds are the same as the chronic RfDs, except for sodium metavanadate, which is 0.01 

mg/kg/day (US. EPA, 1987, 1991qb). 

Inhalation exposures to vanadium and vanadium compounds result primarily in adverse 

effects to the respiratory system (Sax, 1984; ATSDR, 1990). In laboratory studies, minimal 

effects (throat irritation and coughing) occurred after an 8-hr exposure to 0.1 mg V/m3 (Zen and 

Berg, 1967). In studies on workers occupationally exposed to vanadium, the most common 

reported symptoms were: imtation of the respiratory tract, conjunctivitis, dermatitis, cough, 

bronchospasm, pulmonary congestion, and bronchitis (Symanski, 1939; Sjoberg, 1950,195 1,1955, 

1956; Vintinner et al., 1955; Lewis 1959; Tebrock and Machle, 1968; Roshchin, 1968; Kiviluoto 

1

et al., 1981b). Quantitative data are; however, insufficient to derive a subchronic or chronic 

inhalation Reference Concentration (RfC) for vanadium or vanadium compounds. 

There is little evidence that vanadium or vanadium compounds are reproductive toxins or 

teratogens. There is also no evidence that any vanadium compound is carcinogenic; however, 

very few adequate studies are available for evaluation. Vanadium has not been classified as to 

carcinogenicity by the U.S. EPA (1991a). 

2


Vanadium (V) is a metal that occurs in six oxidation states and numerous chemical forms. 

From a toxicological standpoint, the most important inorganic vanadium compounds are vanadium 

pentoxide (V,O,), sodium metavanadate (NaVO,), sodium orthovanadate (N%VO,), vanadyl sulfate 

(VOSO,), and ammonium vanadate (-NI-I,VO,) (ATSDR, 1990). 

About 97% of the total production of vanadium is used as an alloying agent in steels and 

non-ferrous metals such as copper, aluminum and titanium (ATSDR, 1990). Vanadium may also 

have applications as an intermetallic compound (V,Ga) for superconductor applications (Baroch, 

1983). Vanadium compounds are also used as catalysts or in chemical, ceramic or specialty 

applications (Rosenbaum, 1983). Minor uses include applications as color modifiers in mercuryvapor 

lamps, as driers in paints and varnish, and as corrosion inhibitors in flue-gas scrubbers 

(Rosenbaum, 1983). 



Absorption of vanadium into the body depends on the chemical composition of the compound 

containing the vanadium, as well as on the species exposed and the route of exposure. In humans, 

vanadium salts are poorly absorbed from the gastrointestinal tract (Curran and Burch, 1967). 

Estimates of the extent of gastrointestinal absorption of dietary vanadium are 0.5 to 2% (NRCC, 

1980; ICRP, 1960, 1981). In rats, gastrointestinal absorption of vanadium amounted to 2.6% 

following oral dosing with vanadium pentoxide or vanadium oxydichloride and 17.5% following 

oral dosing with sodium orthovanadate (Conklin et al., 1982; Sollenberger, 1981; Wiegmann et 

al., 1982). 

Because atmospheric vanadium would most likely be present in particulate form, 

deposition in the lungs will be greatest for particles in the submicron size range (Waters, 1977). 

In humans, a pulmonary retention value of 35% and a blood absorption value of 20% have been 

used to determine whole body burden of vanadium pavies and Bennett, 1983). ICRP (1960) 

estimated that 26% of soluble vanadium is absorbed through the lungs. Studies in rats have 

shown that intratracheally instilled vanadium compounds such as V,O, and VOCl, disappear 

rapidly from the lungs; Conklin et al. (1982) reported a 40% loss of V,O, in 1 hr and 90% after 

3 days; Oberg et al. (1978) reported a >50% loss of VOCl, in one day; Rhoads and Sanders 

(1985) reported a two-phase exponential loss model for V,O, with 72% of the dose cleared from 

the lungs in the first phase (tn = 11 min), 28% in the second phase (tH = 1.8 days), and Edel and 

Sabbioni (1988) reported 80-85% clearance of tetravalent and pentavalent forms of vanadium 

within 3 hr. 

Although it has been shown that vanadium (as aqueous solutions of vanadate salts) can 

be absorbed through the skin of experimental animals, uptake of vanadium through skin contact 

with airborne particulate matter is considered to be only a minor source of human exposure (NRC, 

1974). 

3


Absorbed vanadium is widely distributed in the body, but short-term localization occurs 

primarily in bone, kidneys, and liver, and possibly also in the spleen and lungs (Vouk, 1979; 

Roshchin et al., 1980; Parker et al., 1980; Sharma et al., 1980; Wiegmann et al., 1982). 

2.2.1. Human 

Concentrations of vanadium in human tissues have been reported to range from 0 to 12 

pg/g (Scanlon, 1975). On a wet weight basis, .concentrations of 19-140 ng/g in 

lung, 4.5-40 ng/g in liver, 30 ng/g in brain, 0.45-10 ng/g in muscle, 400 ng/g in 

lymph nodes, 200 ng/g in testes, 2.6-3.3 ng/g in kidney, and 3.0-3.2 ng/g in 

thyroid have been reported (Hamilton et al., 1972/73; Byrne and Kosta, 1978). In 

a study of workers at a metallurgic plant, the median vanadium concentration in 

the blood was 2.9 pg/L (Thurauf et al., 1979). In a study of workers in a 

ferroalloy plant, vanadium blood levels averaged 20.2 nmovL in nonexposed or low 

exposure workers, and 35.7 nmol/L in moderate and high exposure workers (Gylseth 

et al., 1979). Kiviluoto et al. (1981a) reported vanadium levels of 393 f 223 

nmol/L in serum of workers exposed to WAS of 0.03-0.77 mg V/m3. 

2.2.2. Animal 

Acute oral exposure to vanadium compounds results in rapid tissue distribution, 

particularly to bone (ATSDR, 1990). Intermediate exposures result in low levels in bone, kidneys, 

liver and lungs (ATSDR, 1990). Long-term dietary studies conducted on dogs revealed limited 

accumulation of vanadium in femoral epiphyses (1.2 to 1.5 ug/g) following 2.5 years on a diet 

containing 10 or 100 ppm vanadium added as vanadium pentoxide (Stokinger et al. unpublished, 

as reported in Stokinger, 1981). Uptake of vanadium was greater in the bones of rats than in 

bones of dogs exposed to the same dietary levels of vanadium. Tissue deposition of vanadium 

has been reported to be greater following dietary exposure to ammonium metavanadate than to 

vanadium pentoxide (Stokinger et al., 1981). 

In rats, inhalation exposure to vanadium pentoxide (0.5 mg Vim3, 6 hr daily, for 6 mo) 

resulted in deposition of vanadium primarily in lungs (30 pg V/g), kidneys (0.8 pg V/g), and 

spleen (0.6 vg V/g) (Stokinger et al., 1981). Intratracheal instillation of vanadium pentoxide in 

the same species resulted in rapid transport to the blood, liver, and bone (Conklin et al., 1982), 

and deposition of 12% of the dose in the skeleton (Rhoads and Sanders, 1985). Intramcheal 

studies with VOCl, also revealed rapid transport to blood, heart, spleen, liver, and kidneys, and 

relatively large deposition in the skeleton of rats (Oberg et al., 1978). 

23. METABOLISM 

In the body, vanadium can undergo changes in oxidation state and it can also fonn 

chemical complexes with blood proteins (ATSDR, 1990). Harris et al. (1984) followed the 

distribution of vanadium in blood cells and plasma of dogs injected i.v. with radiolabeled vanadyl 

chloride (+4 oxidation state) or ammonium vanadate (+5 oxidation state). A significant fraction 

of the vanadium was associated with red blood cells and 77% of the plasma vanadium was 

eventually bound to serum transferrin. Harris et al. (1984) noted that there is an interconversion 

4

of vanadyl and vanadate in the blood, probably with oxidation of the vanadyl transferrin complex 

taking place in the plasma, and reduction of vanadate to vanadyl ions occurring in red blood cells. 

Transfemn-bound vanadium may be exhanged with liver femtin (Harris et al., 1984; Chasteen 

et al., 1986). 



Excretion of vanadium depends on the exposure route and chemical form of the vanadium. 

Following oral administration of sodium metavanadate (12.5 mg/d for 12 days), 87.6% of the dose 

was recovered in the feces and the remainder (12.4%) in the urine (Proescher et al., 1917). The 

ratio of vanadium in urine to that in the diet was reported to be about 0.13 (Tipton et al., 1969). 

Following inhalation exposures to vanadium compounds, urinary levels can be quite high. 

Workers occupationally exposed to vanadium dust (0.5 mg/m3) had detectable levels of vanadium 

in their urine for up to 2 weeks after the exposure ended (Zenz et al., 1962). Workers exposed 

to 0.1-0.19 mg/m’ vanadium in a manufacturing plant had significantly higher urinary levels of 

vanadium (20.6 pg/L) than non-exposed workers (2.7 pa) (Orris et al. 1983). Vanadium 

concentrations of 37.8 pgL, median value (Thurauf et al., 1979), 46.7 pg/L, mean value (Lewis, 

1959), and 200-500 pa, range (Gul’ko, 1956) have been reported for urine samples from other 

occupationally exposed workers. In a study of workers in a ferroalloy plant, vanadium 

concentrations in urine when adjusted for creatinine excretion, averaged 3.6 nmoVmmol creatinine 

for nonexposed workers and 15.2 nmoVmmol creatinine for exposed workers (Gylseth et al., 

1979). Kiviluoto et al. (1981a) reported vanadium levels of 73 S O nmoVmmol of creatinine in 

urine of workers exposed to WAS of 0.03-0.77 mg V/m’. 

2.4.2. Animal 

Because vanadium is poorly absorbed through the gastrointestinal tract, a large percentage 

of an ingested dose will be excreted unabsorbed in the feces; Patterson et al. (1986) reported that 

in rats, 80% of a dose of ammonium metavanadate was excreted in the feces over a period of 6 

days. Of the absorbed vanadium, that fraction that is deposited in the liver is excreted rapidly, 

but that retained in bone is mobilized more slowly (Cum and Burch, 1967). Following 

inhalation exposure or intratracheal or intravenous injection, much of the absorbed vanadium is 

excreted in the urine (ATSDR, 1990). In rats, 3240% of an intratracheal or intravenous dose was 

excreted in the urine in the first 3-4 days (Sabbioni and Marafante, 1978; Conklin et al., 1982). 

Excretion of vanadium in the urine may continue for up to 6 mo after chronic exposure is 

discontinued (Curran, unpublished). 


The toxicity of vanadium depends on its physico-chemical state; particularly on its valence 

state and solubility. Pentavalent vanadium is generally considered to be the most toxic form, 

regardless of whether it functions as an anion or cation (NRC, 1974). Based on relative median 

lethal doses, pentavalent ammonium vanadate (NH,VO,) has been reported to be more than twice 

5

as toxic as trivalent vanadium trifluoride (VCl,) and more than 6 times as toxic as divalent 

vanadium diiodide (VI2). Similarly, the pentavalent vanadium pentoxide (V20,) was reported to 

be more than 5 times as toxic as the trivalent vanadium trioxide (V,O,). In in vitro tests on rabbit 

alveolar macrophages, V20, was more toxic than V20, which, in turn, was more toxic than VO, 

(Waters et al., 1974). 



3.1.1.1. Human 

Vanadium pentoxide and sodium metavanadate have a toxicity rating of 5, equivalent to 

a probable lethal oral dose in humans of 5-50 mgkg (Gosselin et al., 1984). The elemental 

metallic form is considered to be non-toxic. 

3.1.1.2. Animal 

Animals exposed to acutely toxic doses of vanadium compounds exhibit immediate 

distress, a hemorrhagic exudate from the nose, marked diarrhea, hindlimb paralysis, labored 

respiration, and convulsions that can lead to death (Gosselin et d., 1984). Pathologic effects 

include dibe desquamative enteritis and congestion of lungs, liver, kidneys, adrenal cortex, 

brain, spinal cord, and bone m mw (Gosselin et al., 1984). Fatty degeneration of lungs and liver 

and focal hemorrhages in the lungs and adrenal cortex may also occur (Gosselin et al., 1984). 

High concentrations of vanadium compounds may cause irreversible damage to the kidneys 

(Kumar and Corder, 1980). Vanadium compounds have also beem reported to be vasoconstricting 

agents affecting blood vessels of the lungs, spleen, kidneys, and intestine (Proescher et al., 1917; 

Erdmann et al., 1984). LD,, values for sodium metavanadate administered by gavage to rats and 

mice are 4 1 mg Vkg and 3 1 mg Vkg, respectively (ATSDR, 1990). 

3.1.2. Snbchronic Toxicity 

3.1.2.1. Human 

Volunteers given 0.47-1.3 mg V/kg/day orally as ammonium vanadyl tartrate for three 

months, developed intestinal cramping and diarrhea, but no hematological abnormalities, no 

changes in serum chemistry indicative of adverse liver effects (glutamic oxaloacetic transferase, 

cholesterol, triglyceride, or phospholipid levels), and no changes in urine chemistry indicative of 

adverse renal effects (albumin, hemoglobin, BUN, or formed elements) (Dimond et al., 1963). 

3.1.2.2. Animal 

Sodium metavanadate at a concentration of 50 ppm in the drinking water of rats for three 

months resulted in slight increases in blood urea and uric acid and mild histopathological lesions 

in kidneys (corticomedullar microhaemorrhagic foci) and spleen (hypertrophy and hyperplasia in 

the white pulp) (Doming0 et ai., 1985). The exposure was equivalent to a daily dose level of 6.56 

mg/kg/day or 2.74 mg V/kg/day. An exposure level of 10 ppm (1.32 mg/kg/day or 0.55 mg 

Vkg/day) was considered a NOAEL (US. EPA, 1987). The same compound added to the food 

6

of rats at levels of 25 and 50 ppm for 100 days had no effect on hemoglobin levels, but did cause 

dose-related decreases in growth as well as diarrhea at the highest dose (9.3 mg/kg/day) (Franke 

and Moxon, 1937). No other parameters of toxicity were evaluated. 

Sodium orthovanadate in the diet of rats for six months caused no changes in heart rate 

or blood pressure, but did induce vasoconstriction (Susic and Kentera, 1988). 

Ammonium vanadate (15 mg Vkg) in the diet of rats for 2 months resulted in increased 

right ventricular pressure and pulmonary hypertension (Susic and Kentera, 1986). The same 

compound administered in drinking water of rats (200 ppm vanadium) for two months resulted 

in decreased growth, decreased erythrocyte count, and reduced hemoglobin and hematocrit (Gorski 

and Zaporowska, 1983). Additional studies confirmed that vanadium in the drinking water of rats 

(300 ppm V for 4 weeks) caused a decrease in erythrocyte count and hemoglogin level 

(Zaporowska and Wasilewski, 1991). In addition, a relative increase in reticulocytes and 

polychromatophilic erythrocytes indicated an effect on erythrocyte maturation (Zaporowska and 

Wasilewski, 1991). 

Vanadium pentoxide in the diet of male rats for 103 days (25 ppm for 35 days followed 

by 100 ppm for 68 days or 50 ppm for 35 days followed by 150 ppm for 68 days) resulted in a 

decrease in cystine content in hair and significant reductions in RBC count and hemoglobin in the 

high-dose group (Mountain et al., 1953). 


3.13.1. Human 

Information on the chronic oral toxicity of vanadium to humans was not available. 

3.133. Animal 

A vanadyl sulfate concentration of 5 pg/mL in drinking water, plus a vanadium level of 

3.2 pg/g in the diet (4.1 mg Vkg total) of mice, was reported to cause no adverse effects over 

a lifetime exposure period (Schroeder and Balassa, 1967). In similar lifetime studies, rats and 

mice exhibited no adverse effects when exposed to 5 ppm vanadium (as vanadyl sulfate) in 

drinking water (Schroeder et ai., 1970; Schroeder and Mitchner, 1975). The estimated dose levels 

were 0.7 mg V/kg/day for rats and 0.9 mg Vkglday for mice. 

Vanadium pentoxide in the diet of rats at levels of 10 and 100 ppm for their entire 

lifetime resulted in no significant toxicological effects except for a reduction in hair cystine 

content (Stokinger et al., 1953). The exposure level of 10 ppm was equivalent to 0.9 mg/kg/day 

of vanadium pentoxide (US EPA, 1987). 

7



Information on the oral developmental and reproductive toxicity of vanadium to humans 



Exposure of male and female rats before mating, and of female rats during gestation and 

lactation to sodium metavanadate by gavage (maximum of 8.4 mg Vkglday) did not induce any 

adverse effects on fertility, reproduction, or parturition; however, doses of 4.2 mg Vkglday 

significantly reduced pup size and body weight at birth and 21 days later (Doming0 et al., 1986). 

Gavage doses of 8.4 mg V/kg/day, as sodium metavanadate, to pregnant rats on gestation days 

6-14 did not result in embryolethality, teratogenicity or significant visceral or skeletal 

abnormalities; however, there was an increase in facial and dorsal hemorrhages (Patemain et aI., 

1987). In a two-generation study, altered lung collagen metabolism was seen in fetuses of adult 

rats receiving 2.8 mg Vkg, as sodium metavanadate in drinking water (Kowalska et al., 1988). 


Separate subchronic and chronic oral reference doses have been derived for vanadium, 

vanadium pentoxide, vanadyl sulfate, and sodium metavanadate (US. EPA, 1987, 1991a). 

3.1.5.1. Subchronic 

Vanadium 

- 

ORAL RfD: 


UNCERTAMTY FACTOR: 100 

MODIFYlNG FACTOR NA 

NOAEL: 

0.7 mg/kg/day (rat), drinking water, lifetime 

PRINCIPAL STUDY: Schrocder et al., 1970 

COMMENTS: The NOAEL is derived from a lifetime single exposure level study in 

which rats were exposed to 5 ppm V, as vanadyl sulfate, in drinking water. The only 

reported effects were minor changes in serum chemistry. The Uncertainty Factor of 100 

is the product of a 10-fold uncertainty in extrapolating fiom laboratory animals to humans 

and a IO-fold uncertainty to protect sensitive individuals. 

Vanadium Dentoxide 

ORAL RfD: 

0.009 mg/kg/day (U.S. EPA, 1991b) 

UNCERTAMn FACTOR 100 


NOAEL: 

0.89 mgkglday 

8

PRINCIPAL STUDY: Stokinger et al., 1953 

COMMENTS: The NOAEL is derived from a study in which rats received 10 or 100 

pprn dietary vanadium pentoxide for 2.5 yr. The only change reported was a decrease in 

cystine levels in the hair of the exposed animals. The 10 ppm level was selected as a 

NOAEL. The Uncertainty Factor of 100 is the product of a 10-fold uncertainty in 

extrapolating from laboratory animals to humans and a 10-fold uncertainty to protect 

sensitive individuals. 

Vanadvl sulfate 

ORAL RfD: 

UNCERTAINTY FACTOR 


100 

MODIFYING FACTOR: NA 

NOAEL: 

2.24 mg/kg/day 

PRINCIPAL STUDY: Schroeder et al., 1970, as reported in U.S. EPA, 1987 

COMMENTS: The NOAEL is derived from a single exposure level study in which rats 

were exposed to 5 pprn V, as vanadyl sulfate, in drinking water for 2.5 yr for a lifetime. 

The only reported effects were minor changes in serum chemistry. The Uncertainty 

Factor of 100 is the product of a 10-fold uncertainty in extrapolating from laboratory 

animals to humans and a 10-fold uncertainty to protect sensitive individuals. 

Sodium metavanadate 

ORAL RfD: 

0.01 mg/lcg/day (U.S. EPA, 1987, 1991a) 



NOAEL: 


PRINCIPAL STUDY: Doming0 et al., 1985 

COMMENTS: The NOAEL is derived from a study in which rats were given 0, 5, 10 

and 50 ppm sodium metavanadate, in drinking water for 3 months. Impaired kidney 

function was seen at 50 ppm, and 10 ppm was considered a NOAEL. The Uncertainty 


animals to humans and a IO-fold uncertainty to protect sensitive individuals. 


Vanad in m 

ORAL RfD: 

0.007 mg/kg/day (U.S. EPA, 1987, 1991a) 

UNCERTAINTY FACTOR. 100 


NOAEL: 

0.7 mg/kg/day (rat), drinking water, lifetime 

9

PRINCIPAL STUDY: Schroeder et al., 1970 

COMMENTS: The NOAEL is derived from a lifetime single exposure level study in 

which rats were exposed to 5 ppm V, as vanadyl sulfate, in drinking water. The only 

reported effects were minor changes in serum chemistry. The Uncertainty Factor of 100 

is the product of a 10-fold uncertainty in extrapolating from laboratory animals to humans 

and a 1 O-fold uncertainty to protect sensitive individuals. 

Vanadium Dentoxide 

ORAL RfD: 

0.009 mg/kg/day (U.S. EPA, 1987, 1991b) 



NOAEL: 

0.89 mglkglday 

CONFIDENCE: 

Study: 

LOW 

Data Base: LOW 

RfD: Low 


PRINCIPAL STUDY: Stokinger et al., 1953 

COMMENTS: The NOAEL is derived from a study in which rats received 10 or 100 

ppm dietary vanadium pentoxide for 2.5 yr. The only change reported was a decrease in 

cystine levels in the hair of the exposed animals. The 10 ppm level was selected as a 

NOAEL. The Uncertainty Factor of 100 is the product of a I0-fold uncertainty in 

extrapolating from laboratory animals to humans and a 10-fold uncertainty to protect 

sensitive individuals. 

Vanadvl sulfate 

ORAL RfD: 

UNCERTAINTY FACTOR: 

0.02 mg/kg/day (U.S. EPA, 1987, 1991a) 

100 


NOAEL: 

224 mg/kg/day 

PRINCIPAL STUDY: Schroeder et al., 1970 

COMMENTS: The NOAEL is derived from a single exposure level study in which rats 

were exposed to 5 ppm V, as vanadyl sulfate, in drinking water for 2.5 yr for a lifetime. 

The only reported effects were minor changes in serum chemistry. The Uncertainty 

Factor of 100 is the product of a 10-fold uncertainty in extmpolating fiom laboratory 

animals to humans and a 10-fold uncertainty to protect sensitive individuals. 

Sodium metavanadate 

ORAL IUD: 0.001 rngntglday (US. EPA, 1987, 1991a) 

10



NOAEL: 


PRINCIPAL STUDY: Doming0 et al., 1985 

COMMENTS: The NOAEL is derived from a study in which rats were given 0, 5, 10 

and 50 ppm sodium metavanadate, in drinking water for 3 months. Impaired kidney 

function was seen at 50 ppm, and 10 ppm was considered a NOAEL. The Uncertainty 


animals to humans, a 10-fold uncertainty to extrapolate from a subchronic to chronic 

exposure, and a 1 O-fold uncertainty to protect sensitive individuals. 



3.2.1.1. Human 

In studies on humans, the acute toxic effects of inhaled vanadium were found to be limited 

to eye and respiratory tract irritation; there being no evidence of disturbances to the cardiovascular 

system, gastrointestinal tract, kidneys, blood, or CNS (Sax, 1984; ATSDR, 1990). Typical 

symptoms include coughing, wheezing, rhinonhea, sore throat and chest pain (ATSDR, 1990). 

There is usually a latency period of 1-6 days before effects appear (Lagerkvist et al., 1986). In 

severe cases bronchospasms and bronchitis, accompanied by wheezing and dyspnea may occur, 

and bronchopneumonia may result from very high exposures (Lagerkvist et al., 1986) 

NOSH (1977) reported that respiratory irritation from inhalation of vanadium-containing 

dusts or fumes occurred at concentrations ranging from 0.1 to 85 mg/m’. At a concentration of 

about 1.0 mg/m3, vanadium dust caused coughing and throat irritation (Zenz and Berg, 1967). 

At a level of 0.1 mg/m3, an 8-hr exposure to vanadium pentoxide (0.06 mg V/m’) caused only 

mucus formation which was cleared by slight coughing that lasted 3-4 days (Zenz and Berg, 

1967). A level of 0.06 mg V/m’ was considered a NOAEL for acute exposures by ATSDR 

( 1990). 

Lees (1980) reported that workers occupationally exposed (several hours per day for eight 

days) to vanadium-containing dust (as a component in fuel oil ash) exhibited significant decreases 

in several lung function tests including forced vital capacity, forced expiratory volume, and forced 

mid-expiratory flow. Lung functions returned to normal several weeks after the exposures ended. 

There is some evidence that workers exposed to vanadium compounds become sensitized 

such that there is increased severity and more rapid onset of respiratory symptoms after multiple 

exposures (Zenz and Berg, 1967; Zenz et al., 1962; Roshchin, 1968). 

3.2.1.2. Animal 

Two of four rabbits died following 7 hr exposure to 114 rng V/m3, as V,O,; the exposures 

resulted in tracheitis, pulmonary edema and bronchopneumonia (Sjoberg, 1950). 

11

Monkeys exposed to 2.8 mg V/m3, as V,O,, for 6 hr developed increased pulmonary 

resistance and had increased numbers of polymorphonuclear leucocytes in bronchoalveolar lavage 

fluid (Knecht et al., 1985). Exposure of rats to bismuth orthovanadate 6 hdday for 2 weeks 

resulted in increases in lung weight and increased accumulation of alveolar macrophages, lung 

lipids and type I1 epithelial cells (Lee and Gillies, 1986). Rabbits exposed to vanadium pentoxide 

dust showed no evidence of adverse effects on cardiovasular or gastrointestinal systems, blood, 

spleen or brain; but they did exhibit conjunctivitis and some degree of fatty degeneration in the 

liver and kidneys (Sjoberg, 1950). 


3.2.2.1. Human 

Information on the subchronic inhalation toxicity of vanadium and vanadium compounds to 

humans was not available. 

3.2.2.2. Animal 

Repeated inhalation of vanadium pentoxide (20-40 mg/m3, 1 hr/day, for several months) by 

rabbits resulted in chronic rhinitis and tracheitis, emphysema, patches of lung atelectasia, and 

bronchopneumonia (Sjoberg, 1950). Exposure of rabbits to vanadium trioxide aerosol (40-75 

mg/m3, 2 hdday, 9-12 months) resulted in sneezing, nasal discharge, dyspnea and tachypnea and 

sometimes bronchial asthma (Roshchin et al., 1964; Roshchin, 1967). Similar effects were seen 

in rabbits exposed under the same conditions to vanadium pentoxide concentrations of 8-1 8 mg/m’ 

or to vanadium carbide levels of 40-80 mg/m’, and also in rats exposed to vanadium pentoxide 

condensation aerosol (3-5 mg/m’, 2 hr/day, every second day for 3 months) and to vanadium 

pentoxide dust (10-40 mg/m3, 1 hr/day, for 4 months). 

Stokinger et al. (1953) reported that a concentration of 0.5 mg V/m3 as vanadium pentoxide 

dust, 6 hr/day for 6 months caused no adverse effects in rats, dogs, guinea pigs, and rabbits. 

Pazynich (1966) reported that albino rats exposed continuously for 70 days to 0.2 mg/m’ of 

vanadium pentoxide aerosol exhibited altered motor chronaxy of antagonistic muscles, decreased 

blood cholinesterase activity, reduced serum protein levels, including O-globulins, reduced 

oxyhemoglobin, and also pathological changes in the lungs (congestion, hemorrhages, bronchitis), 

the liver (central vein congestion, hemomhages, infihtes and degeneration), the kidneys 

(degeneration and necrosis of the epithelial cells of the convoluted tubules), and in the myocardial 

blood vessels (focal perivascular hemomhages). No adverse effects were seen in rats exposed to 

0.002 mg/m’. 

Sugiura (1978) exposed rats and mice to 1-2 mg/m3 of vanadium pentoxide 6 hdday for 3 

months. At concentrations up to 0.4 mg/m3, no adverse effects were seen. At higher 

concentrations, the rats had decreased growth rates and enlarged lungs; whereas. mice had 

thickened alvelolar walls and congested lungs. 


3.23.1. Human 

. 

12

Data on the effects of long term inhalation exposure to vanadium have been derived mainly 

from studies of workers occupationally exposed to vanadium pentoxide. The most frequently 

reported effects were imtation to the respiratory tract, conjunctivitis and dermatitis. Cough, 

bronchospasm, pulmonary congestion, and bronchitis are the most common symptoms, but rhinitis, 

pharyngitis, pneumosclerosis, asthma, and dyspnea have also been reported (Symanski, 1939; 

Sjoberg, 1950; Vintinner et ai., 1955; Lewis 1959; Tebrock and Machle, 1968; Kiviluoto et al., 

1981b; Sjoberg, 1956; Sjoberg, 1951, 1955; Roshchin, 1968). There is no clear evidence that 

chronic lung disease (emphysema, pneumoconiosis, fibrosis) results from long term exposure to 

vanadium compounds (NIOSH, 1977); however, it has been noted that cases of bronchial asthma 

and bronchitis have been reported with “sufficient fiequency to warrant concern for decreased 

ventilatory function, and possibly, a progressively decreasing ventilatory function” (NIOSH, 1977). 

Bronchiopneumonia may possibly be a secondary complication caused by the effects of vanadium 

on respiratory mucosa (Sjoberg, 1955). 

Evaluation of dose-response relationships from occupational exposure studies is difficult 

because of fluctuations in concentrations, lack of continuous monitoring, and potential exposure 

through routes other than inhalation. Generally, occupational exposures occur over wide 

concentration ranges, Le., 0.05-5.58 mg/m’ (Sjoberg, 1950), 0.02-3.2 mg V/m3 (Tebrock and 

Machle, 1968), 0.004-2.116 mg V/m’ in ore dust and 0.018-58.82 mg V/m3 in vanadium 

pentoxide dust (Vintenner et ai., 1955), and 0.012-2.3 mg V/m3 (time-weighted average exposures) 

for smelter workers (Kiviluoto et al., 1981a). Therefore, minimum effect levels are difficult to 

quantify. The lowest exposure levels at which there was an increased incidence of respiratory 

distress were those in the study of Lewis (1959) in which workers were exposed to vanadium 

pentoxide for an average duration of 2.5 years. In this study, vanadium concentrations in seven 

air samples ranged from 0.018-0.925 mg Vim’, but five of the measurements were 0.1-0.38 

mg/rp’. In another study, vanadium processing workers exposed to 0.1-0.3 mg/m3 had lowered 

serum cholesterol levels but no other adverse effects (Vintinner et al., 1955). 

Most investigators have reported that long tenn occcupational exposure to vanadium 

compounds did not result in any gastrointestinal symptoms or adverse effects to the hemopoietic 

system, kidneys, liver, or nervous sytem (Symanski, 1939; Sjoberg, 1956: Kiviluoto et al., 1981% 

198 1 b). However, some workers chronically exposed to vanadium dust have reported dizziness, 

depression, headache, or tremors of the fingers and a ms (Levy et al., 1984; Vintinner et al., 1955). 

From the available pre-1974 clinical, experimental, and occupational exposure data, IIEQ 

(1974) concluded that clinical signs of severe chronic intoxication (hemoptysis, pneumonia, 

hacking cough, chest pain, lesions of the nose, and des) occurred at vanadium pentoxide air 

concentrations of around 1000 pg/m’; clinical signs of subtle chronic intoxication (green tongue, 

cough, vascularization of the cornea, conjunctivitis, colic, respiratory tract imtation, mucus, and 

rhinorrhea) occurred at vanadium pentoxide concentrations of about 100 pg/m3 or less, and 

subclinical chronic intoxication resulting in metabolic disorders occurred at about 1-20 pg/m’. 

IIEQ (1974) considered reductions in body cystine levels (as measured in fingernails) to be a 

major subclinical effect of vanadium exposure. Other biochemical effects that may occur without 

clinical signs of toxicity include reductions in serum cholesterol, decreases in coenzyme A in liver 

and in coenzyme Q in mitochrondria and changes in activity of Na+-, K+-ATPase, Ca-ATPase, 

adenylate kinase, ribonuclease, phosphofiuctokinase, and glucoss6-phosphatase) (Lagerhist et 

al., 1986). 

13


Animal data indicate that chronic toxic effects on the respiratory system are similar to those 

seen in acute exposures. In addition, when the dose is sufficiently high or the exposure 

sufficiently long, systemic effects such as edema, hemorrhaging, and lesions can occur in the 

lungs, liver, and kidney. 

Rabbits chronically exposed to vanadium pentoxide dust showed no evidence of adverse 

effects on the cardiovasular or gastrointestinal systems, blood, spleen or brain; but they did 

develop conjunctivitis and had some fatty degeneration in the liver and kidneys (Sjoberg, 1950). 

Fatty changes with partial cell necrosis were seen in the liver and kidneys of rats and rabbits 

exposed to vanadium pentoxide, trioxide and chloride (10-70 mg/m’, 2 hr/day, 9-12 mo) 

(Roshchin, 1968). 



Infoxmation on the developmental and reproductive toxicity of vanadium and vanadium 

compounds following inhalation exposure was not available. 


Information on the developmental and reproductive toxicity of vanadium and vanadium 

compounds following inhalation exposure was not available. 

3.2.5. Reference Concentration 

A subchronic or chronic reference concentration for vanadium is not available at this time 

(U.S. EPA, 1991b). 

14



33.1.1. Human 

Stokinger et al. (1953) reported that a 10% solution of sodium metavanadate is a primary 

irritant to human skin. Saturated solutions of ammonium metavanadate (0.5%) and vanadium 

pentoxide (0.8% solution) did not irritate the skin. Sjoberg (1951) reported that several workers 

occupationally exposed to vanadium developed what appeared to be a contact dermatitis and that 

in one case, skin patch tests produced eczematous lesions indicative of an allergic reaction. 

Proescher et al. (1917) estimated that 30 mg of sodium tetravanadate, injected intravenously, 

would be a fatal dose to a 70-kg man. Signs and symptoms of toxicity following a single 

intravenous injection of 100 mg vanadium pentoxide include nausea, vomiting, salivation, 

lacrimation, loss of pulse, and albumin and cylindrical casts in urine (Lagerkvist et al., 1986). 


Administered to the eye of a rabbit, sodium orthovanadate caused a significant fall in 

intraocular pressure (Mittrag et al., 1984). The LD,, values for sodium metavanadate injected 

intrperitoneally is 0.1 1 mg Vkg in rats and 0.13 mg Vkg in mice (Chanh, 1965). 

33.2. Subchronic Toxicity 

333.1. Human 

Information on the subchronic toxicity of vanadium or vanadium compounds to humans by 

other routes of exposure was not available. 

333.2. Animal 

Fatty changes were seen in the liver of rats following subcutaneous injections of ammonium 

vanadate (1 mg Vkglday, for 30 days) (Kaku et al., 1971). 

333. Chronic Toxicity 

Information on the chronic toxicity of vanadium and vanadium compounds to humans or 

animals by other routes of exposure was not available. 



Information on the developmental and reproductive toxicity of vanadium or vanadium 

compounds to humans by other routes of exposure was not available. 

33.4.2. Animal 

1s

There is no clear evidence that vanadium compounds are teratogenic to laboratory animals; 

however, in one study, exposure of pregnant Syrian golden hamsters to ammonium metavanadate 

(0,0.47, 1.88, or 3.75 mg/kg injected i.p. on gestation days 5 through 10) resulted in a significant 

increase in fetal skeletal abnormalities (micrognathia, supernumerary ribs, and alternations in 

sternebra1 ossification) (Carlton et al., 1982). The number of malformed offspring was small, and 

there was no clear-cut dose/response relationship, thus, a definite assessment of teratogenicity was 

not possible. In this same study, there was also a decrease in the male-female fetal sex ratio, but 

no external and soft tissue anomalies. A delay in fetal skeletal ossification, but no implantation 

or teratogenic effects occurred in the offspring of mice injected with 0.15 mL of a 1 mM solution 

of vanadium pentoxide on day 8 of pregnancy (Wide, 1984). Exposure of female rats to 0.85 

mgkg of sodium metavanadate by subcutaneous injection on the 4th day of pregnancy resulted 

in an increase in preimplantation embryo mortality, but no teratogenic effects (Roshchin and 

Kazimov, 1980; Roshchin et al., 1980). However, in male rats dosed intraperitoneally (0.85 

mg/kg/day of sodium metavanadate for 20 days), spermatogenesis was altered, sperm motility and 

osmotic resistance was reduced, the number of dead spermatozoa increased, and morphological 

damage to the seminiferous epithelium was observed. There was also a decrease in fertilization 

of females mated to exposed males and an increase in preimplantation embryo mortality. 

In tests on pregnant rats, Hackett and Kelman (1983) found that vanadium accumulates in 

the placenta, preferentially concentrating in the membranes rather than in the fetus itself. 

3.4. TARGET ORGAIWCRITICAL EFFECTS 

Minimal effect levels and target organs may vary with the chemical form and oxidation state 

of the vanadium. 



1. Gastrointestinal system: Diadea has been reported in humans and animals receiving 

ammonium vanadyl tamate and sodium metavanadate, respectively. 

2. Kidney: Slight changes in renal function as suggested by increases in blood urea nitrogen 

and uric acid have been reported in animals exposed to sodium metavanadate. 

3. Blood: Decreases in erythrocytes, hemogloblin, or hematocrit have been reported in 

animals receiving ammonium vanadate or vanadium pentoxide. 


Other effects seen in animals chronically exposed to vanadium compounds include reduced 

growth rates in adults and fetuses (sodium metavanadate, ammonium vanadate), vasoconstriction 

(sodium orthovanadate), and facial and dorsal hemorrhages and altered lung collagen metabolism 

in fetuses (sodium metavanadatc). 

3.4.2. Inhalation Exposures 

16


Respiratory system: Exposure to vanadium dusts can result in respiratory tract irritation. 

Bronchospasms and bronchitis, accompanied by wheezing and dysnea may occur, and 

bronchopneumonia may result from very high and prolonged exposures. The mechanism of 

vanadium’s effect on the respiratory system is similar to that of other metals. Vanadium 

damages alveolar macrophages and affects lung clearance rates. 


1. Nervous System: Some workers chronically exposed to vanadium dust reported dizziness, 

depression, headache, or tremors of the fingers and arms. 

2. Liver and Kidney: Limited animal data suggest that chronic exposure may lead to liver 

and kidney abnormalities. 

Other effects seen in animals exposed to vanadium compounds include perivascular 

hemorrhages in myowdial vessels, altered muscle motor chronaxie, and changes in blood 

chemistry (vanadium pentoxide). 




Citing a progress report submitted to the National Cancer Institute, Sax (1981) lists the 

carcinogenicity of vanadium as questionable (no other data available). 


Kanisawa and Schroeder (1967) evaluated the carcinogenicity of vanadium in lifetime studies 

on Swiss mice. The test animals were given vanadyl sulfate in their drinking water (5 pg/mL 

water) and in their diet (3.2 pg/g feed) from the time they were 20-22 days old until death. 

NOSH (1 977) calculated that the total annual intake of vanadium in each animal would amount 

to 19.8 mg/100 g of body weight. There were no significant differences in the incidences of 

tumors (heart, lungs, kidneys, liver, spleen, and other organs were examined) between the exposed 

animals and the controls. Other studies using the same experimental procedures on both rats and 

mice also indicated that vanadium was not carcinogenic at a level of 5 pg vanadyl sulfate per mL 

of drinking water over a lifetime exposure (Schroeder and Balassa, 1967; Schroeder et al., 1970; 

Schroeder and Mitchner, 1975). 

Stoner et al. (1976) evaluated the potential of various metallic compounds to induce lung 

adenomas in strain A mice. In one test group, mice were given 24 i.p. injections of vanadium 

(In) 2,4pentanedione (total dose, 120, 60, or 24 mg/kg) over a 30-week period. The incidence 

of lung tumors was not significantly different from that of the controls. 

17

Several studies have suggested that vanadium exhibits anti-carcinogenic activity. Thompson 

et al. (1984) reported that vanadyl sulfate inhibited murine mammary carcinogenesis by 1- 

methyl-l-nitrosourea in rats, and Djordjevic and Wampler (1985) reported that several vanadium 

complexes have antitumor activity against L 12 10 murine leukemia. 

4.2. INHALATION EXPOSURES 


In a statistical study relating concentrations of air pollutants to mortality indices in Great 

Britain, Stocks (1960) found that together with arsenic and zinc, vanadium showed a weak 

correlation with lung cancer, and together with beryllium and molybdenum, showed correlations 

with other cancers in males. In a similar study conducted by Hickey et al. (1967), there was little 

correlation between lung cancer mortality and vanadium levels. 


Information on the carcinogenicity of vanadium to animals after inhalation exposure was not 

available. 


Information on the carcinogenicity of vanadium to humans or animals from other routes of 



The limited weight of evidence suggests that vanadium and vanadium compounds are not 

carcinogenic; however, few vanadium compounds have been adequately tested. Vanadium has 

not been classified as to carcinogenicity by the EPA. The NTP has approved vanadium pentoxide 

for carcinogenicity testing, but the results are yet not available (U.S. EPA, 1991b). 


Calculation of slope factors is not possible due to inadequate data. 

18

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radioactive vanadium (‘*VO,) in rats and effect of aluminum hydroxide. J. Toxicol. Environ. 

Health IO(2): 233-245. 

Zaporowska, H. and W. Wasilewski. 1991. Significance of reduced food and water consumption 

in rats intoxicated with vanadium. Comp. Biochem. Physiol. 99C (3): 349-352. 

Zenz, C. and B.A. Berg. 1967. Human responses to controlled vanadium pentoxide exposure. 

Arch. Environ. Health 14(5): 709-712. 

Zenz, C., J.P. Bartlett and W.H. Thiede. 1962. Acute vanadium pentoxide intoxica-tion. Arch. 

Environ. Health 5: 542. (Cited in NIOSH, 1977; Proctor and Hughes, 1978) 

26

Appendix L.9 

Historical Dataset


Appendix L.9 Historical Dataset 

MEDIA RAD RESULT VALIDATION 

ANALYTE CAS NUMBER SAMPLE ID DATE TYPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

WAG 1, S WU 38, MW327 

1,l ,l-Trichloroethane 


1,1,2-Trichloroethane 

1.1.2-Trichloroethane 

1,l -Dichloroethane 

1 ,l-Dichloroethane 



1.2-Dichloroethane 


Alkalinity 

Alkalinity 

Antimony 

Antimony, Dissolved 

Arsenic 

Arsenic, Dissohred 

Barium 

Barium, Dissolved 

Benzene 

Benzene 

Beryllium 

Beryllium. Dissolved 

Bromodichlaromethane 

Bromodichloromethane 

Cadmium 

Cadmium, Dissolved 

Calcium 

Calcium, Dissolved 

Carbon Tetrachloride 


Chloride 

Chloride 

Chloroform 

Chloroform 

Chromium 

Chromium, Dissolved 

Cobalt 

Cobalt, Dissolved 

Capper 

Copper, Dissolved 

Depth to Water 

Dssotved Oxygen 

Dissolved Solids 


Ethylbenzene 

Ethylbenzene 

Fluoride 

Fluoride 

Grass Alpha 

Gross Alpha 

Gross Beta 

Gross Beta 

tron 

Iron. Dissolved 

Lead 

Lead, Dissolved 

Magnesium 

Magnesium, Dissolved 

Manganese 

Manganese, Dissolved 

Mercury 

Mercury, Dissolved 

Nickel 

Nickel, Dissolved 

Nitrate as Nitrogen 


Potassium 

Potassium, Dissolved 

Radon 222 

Radon 222 

Selenium 

71-55-6 

71 -55-6 

79-00-5 

79-00-5 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

107-06-2 

107-06-2 

471-34-1 

47 1-34-1 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

71-43-2 

71 -43-2 

7440-41-7 

7440-41-7 

75-27-4 

75-27-4 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

56-23-5 

56-23-5 

16887-00-6 

16887-00-6 

67-66-3 

67-66-3 

7440-47-3 

7440-47-3 

7440-48-4 

7440-48-4 

7440-50-8 

7440-50-8 

DMI 

OXYGEN DIS 

SO266 

SO266 

100-41-4 

100-41-4 

16984-40-8 

16984-48-8 

12587-46-1 

12587-46-1 

12587-47-2 

12587-47-2 

7439-89-6 

7439 - 89 - 6 

7439-92-1 

7439-92-1 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

744062-0 

7440-02-0 

NITRATEASNIT 

N ITRATEASN IT 

7440-09-7 

7440-09-7 

RN222 

RN222 

778249-2 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

6696-95 

5573-95 

5573-95 

5573-95 

6696-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

6696-95 

5573-95 

5513-95 

5573-95 

6696-95 

5573-95 

07MAR1995 

26JUN1995 

07MAR1995 

26JUN1995 

07MAR1995 

26JUN1995 

07MAR1995 

26JUN1995 

07MAR1995 

26JUN1995 

07MAR1995 

26JUN1995 

07MAR1995 

07MARl995 

07MARl995 

07MAR1995 

07MARl995 

07MAR1995 

07MAR1995 

26JUN1995 

07MAR1995 

07MAR1995 

07MARl995 

26JUNl995 

07MAR1995 

07MAR 1995 

07MAR1995 

07MARl995 

07MAR1995 

26JUN1995 

07MAR1995 

26JUN1995 

07MAR1995 

26JUN1995 

07MARl995 

07MAR1995 

07MAR1995 

07MAR1995 

07MARl995 

07MAR1995 

07MAR1995 

O7MAR 1995 

07MARl995 

26JUN1995 

07MAR1995 

26JUN1995 

07MAR1995 

26JUN1995 

07MARl995 

26JUNl995 

07MAR1995 

26JUN1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MARI 995 

26JUN1995 

07MAR1995 

07MAR1995 

07MAR1995 

26JUN1995 

07MAR1995 

Page 1 of 176 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

< 

Q 

< 

Q 

U 

U 

< 

Q 

U 

U 

< 

< 

U 

U 

U 

U 

< 

< 

< 

< 

< 

< 

U 

U 

< 

Q 

c 

Q 

< 

Q 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

0501- 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

m9fl 

mglL 

mglL 

mglL 

mglL 

mg1L 

mg1L 

mglL 

uglL 

uglL 

mglL 

mg1L 

uglL 

ug1L 

mglL 

rngR 

WlL 

mglL 

uglL 

uglL 

wnmgfl 

ug1L 

uglL 

mglL 

mglL 

mglL 

mglL 

wlL 

mg/L 

Feet 

WlL 

mglL 

mgfl 

ug/L 

ugfl 

mglL 

rnglL 

pCilL 

pCiR 

pCVL 

pciR 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

w5 

rng/L 

mglL 

mgk 

mglL 

wfl 

mgk 

mglL 

mglL 

mglL 

pCilL 

pCi 

mgfl

L.9 (continued) 



Selenium, Dissolved 7782-49-2 5573-95 07MAR1995 WG O.OOE+OO a 0501- mg1L 

Silica 

Silica 

Silver 

Silver, Dissolved 

Sodium 

Sodium, Dissolved 

Specific conductance 








Sulfate 

Sulfate 

Technetium-99 

Technetium99 

Temperature 

Tetrachloroethene 


Toluene 

Toluene 

Total Organic Carbon 


Total Organic Carbon ' 






Trans-l,2-Dichloroethene 

Trans-1.2-Dichloroethene 



Turbidity 

Turbidity 

Uranium 

Uranium 

Uranium, Dissolved 


Vinyl Chloride 


Xylene 

Xylene 

Zinc 

Zinc, Dissolved 

cis-I .2-dichloroethene 

cis-I ,2-dichloroethene 

PH 

PH 

PH 

PH 

WAG 1 SWU 38. MW28 

1.1 .I-Trichloroethane 

1 ,I,I-Trichloroethane 

1 .I,2-Trichloroethane 

1 .I.2-Trichloroethane 

1 .I-Dichloroethane 

1 ,I-Dichloroethane 

1 .I-Dichloroethene 


I .2-Dichloroethane 

1,2-Dchloroethane 

Alkalinity 

Alkalinity 

Antimony 


Arsenic 

Arsenic. Dissolved 

Barium 

7631-86-9 

7631-86-9 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

12143-45-2 

12143-45-2 

14133-76-7 

14133-76-7 

SO835 

127-18-4 

127-18-4 

108-88-3 

108-88-3 

7440-44-0 

744044-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

744044-0 

156-60-5 

156-60-5 

79-01-6 

79-01-6 

SO278 

SO278 

7440-61-1 

7440-61-1 

DIS U 

DIS U 

75-01-4 

75-01-4 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

156-59-2 

156-59-2 

SO296 

so296 

so296 

so296 

7 1 -55-6 

7 1-55-6 

79-00-5 

79-00-5 

75-34-3 

75-34-3 

75-35-4 

7535-4 

107-06-2 

107-06-2 

471-34-1 

471-34-1 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-39-3 

5573-95 

6 6 9 6 - 9 5 

5573-95 

5573-95 

5573-95 

5573-95 

5573-95 

5574-95 

5575-95 

5576-95 

6696-95 

6697-95 

6698-95 

6699-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

5574-95 

5575-95 

5576-95 

6696-95 

6697-95 

6698-95 

6699-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

6696-95 

5573-95 

5573-95 

5573-95 

6696-95 

5573-95 

5574-95 

5575-95 

5576-95 

5577-95 

6700-95 

5577-95 

6700-95 

5577-95 

6700-95 

5577-95 

6700-95 

5577-95 

6700-95 

5577-95 

6700-95 

5577-95 

5577-95 

5577-95 

5577-95 

5577-95 

07MAR1995 

26JUN1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

26JUN1995 

26JUN1995 

26JUN1995 

26JUN1995 

07MAR1995 

26JUN1995 

07MAR1995 

26JUN1995 

07MAR1995 

07MAR1995 

26JUN1995 

07MAR1995 

26JUN1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

26JUNl995 

26JUNl995 

26JUN1995 

26JUN1995 

07MARl995 

26JUNl995 

07MAR1995 

26JUN1995 

07MAR1995 

26JUNl995 

07MARI 995 

26JUN1995 

07MARI 995 

26JUNl995 

07MARl995 

26JUNl995 

07MARI 995 

26JUNl995 

07MAR1995 

07MAR1995 

07MAR1995 

26JUN1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

27MAR1995 

22JUN1995 

27MAR1995 

22JUN1995 

27MAR1995 

22JUN1995 

27MAR1995 

22JUNl995 

27MAR1995 

22JUN1995 

27MAR1995 

22JUN1995 

27MAR1995 

27MAR1995 

27MAR1995 

27MAR1995 

27W1995 

Page 2 of 176 

1.30E+01 

2.00E+01 

O.OOE+OO 

O.OOE+OO 

1.40E+01 

1.30E+01 

2.04E+02 

2.03E+02 

2.03E+02 

2.03E+02 

2.1 1E+02 

2.10E+02 

2.10E+02 

2.10E+02 

5.00E+00 

5.00E+00 

O.OOE+OO O.OOE+OO 

O.OOE+OO O.OOE+OO 

5.90E+01 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

l.OOE+OO 

I .00E+00 

1 .OOE+W 

1.00E+00 

1.00E+00 

1.00E+00 

1.00E+00 

l.OOE+OO 

5.00E+00 

5.00E+00 

1.00E+00 

1.00E+00 

2.00E+00 

2.00E+00 

O.OOE+OO 

0.00E+00 

0.00E+00 

O.OOE+OO 

l.OOE+OI 

1.00E+01 

1 .WE+Ol 

l.OOE+OI 

0.00E+00 

0.00E+00 

5.00E+00 

5.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

< 

< 

< 

< 

U 

U 

U 

U 

< 

< 

< 

< 

< 

c 

c 

< 

U 

U 

U 

U 

< 

< 

Q 

Q 

U 

U 

U 

U 

< 

< 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

< 

Q 

< 

0 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

a 

a 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

umhoslcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhodcm 

umhodcm 

umhoslcm 

umhoslcm 

mglL 

mglL 

pCiL 

pCilL 

F 

uglL 

uglL 

0gIL 

uglL 

mg1L 

mg1L 

mg1L 

mglL 

mg/L 

mglL 

mglL 

mglL 

uglL 

ug1L 

ug/L 

uglL 

NTU 

NTU 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

uglL 

uglL 

mg1L 

mglL 

uglL 

uglL 

su 

su 

su 

su 

ugfl 

uglL 

uglL 

uglL 

ugk 

uglL 

uglL 

UgR 

ugR 

ugfl 

mgk 

mgR 

mgR 

WlL 

mg/L 

msn 

mgk



ANALME CAS NUMBER SAMPLE ID DATE TYPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Barium, Dissolved 7440-39-3 5577-95 27MAR1995 WG O.OOE+OO 

N 

mglL 

Benzene 

Benzene 

71-43-2 

71 -43-2 

5577-95 

6700-95 

27MAR1995 

22JUN1995 

WG 

WG 

5.00E+00 

5.00E+00 

U 

U 

N 

N 

uglL 

uglL 

Beryllium 

7440-41-7 

5577-95 27MAR1995 WG 0.00E+00 

< 

N 

mgfl 

Beryllium, Dissolved 

7440-41-7 

5577-95 27MAR1995 WG O.OOE+OO 

< 

N 

mglL 



Cadmium 

75-27-4 

75-27-4 

7440-43-9 

5577-95 

6700-95 

5577-95 

27MAR1995 

22JUN1995 

27MAR1995 

WG 

WG 

WG 

5.00€+00 

5.00€+00 

O.OOE+OO 

U 

U 

c 

N 

N 

N 

uglL 

uglL 

mglL 


7440-43-9 

5577-95 27MAR1995 WG O.OOE+OO 

Q 

mglL 

Calcium 

7440-70-2 

5577-95 27MAR1995 WG 1 .5OE+O1 

N 

mglL 


7440-70-2 

5577-95 27MAR1995 WG 1.60E+01 

N WlL 


56 - 23 - 5 

5577-95 27MAR1995 WG 5.00E+00 

U 

N 

uglL 


Chloride 

Chloride 

Chloroform 

Chloroform 

Chromium 


56-23-5 

16887-00-6 

16887-00-6 

67-66-3 

67-66-3 

7440-47-3 

7440-47-3 

6700-95 

5577-95 

6700-95 

5577-95 

6700-95 

5577-95 

5577-95 

22JUN1995 

27MAR1995 

22JUN1995 

27MAR1995 

22JUN1995 

27MARl995 

27MAR1995 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

5.00€+00 

1.90E+01 

1.90€+01 

5.00€+00 

5.00E+00 

O.OOE+OO 

O.OOE+OO 

U 

U 

U 

C 

< 

N 

N 

N 

N 

N 

N 

N 

uglL 

mglL 

mglL 

ug1L 

ug/L 

mglL 

mglL 

Coban 

7440-48-4 

5577-95 27MAR1995 WG O.OOE+OO 

< 

N 

mglL 

Cobalt. Dissolved 

7440-40-4 

5577-95 27MAR1995 w O.M)E+OO 

< 

N 

mglL 

Copper 



Dissolved Oxygen 



Ethylbenzene 

Ethylbenzene 

7440-50-8 

7440-50-8 

D W 

OXYGEN DIS 

SO266 

SO266 

100-41-4 

100-41-4 

5577-95 

5577-95 

5577-95 

5577-95 

5577-95 

6700-95 

5577-95 

6700-95 

27MAR 1995 

27MARl995 

27MAR1995 

27MAR1995 

27MAR1995 

22 JUNl995 

27MAR1995 

22JUN1995 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

0.00E+00 

O.OOE+OO 


4.00€+00 

1.23E+02 

1.06€+02 

5.00E+00 

5.00E+00 

< 

< 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

Feet 

mg1L 

mg/L 

mglL 

uglL 

ug1L 

Fluoride 

Fluoride 

1690448-8 

16984-48-8 

5577-95 

6700-95 

27MARl995 

22JUN1995 

WG 

WG 

O.OOE+OO 

O.OOE+OO 

N 

N 

mgfl 

mglL 

Gross Alpha 

12507-46-1 

5577-95 27MAR1995 WG l.OOE+OO 8.00E-01 

N 

pCYL 

Gross Alpha 

Gross Beta 

12507-46-1 

12507-47-2 

6700-95 

5577-95 

22JUN1995 

27MAR1995 

WG 

WG 

2.00E+00 5.00E-01 

8.00€+00 3.00€+00 

N 

N 

pCiL 

pCiL 

Gross Beta 

12587-47-2 

6700-95 22JUN1995 WG 1.40E+01 l.OOE+OO 

N 

pCiL 

Iron 

7439-09-6 

5577-95 27MAR1995 w 1.00E+00 

N 

mglL 

Iron, Dissolved 

7439 - 09 - 6 

5577-95 27MAR1995 WG O.OOE+OO 

< 

N 

mgfl 

Lead 


Magnesium 


7439-92-1 

7439-92-1 

7439-954 

7439-95-4 

5577-95 

5577-95 

5577-95 

5577-95 

27MAR1995 

27MARl995 

27MARl995 

27MARl995 

WG 

WG 

WG 

WG 

O.OOE+OO 

O.OOE+OO 

6.00€+00 

7.00E+00 

< 

Q 

N 

N 

N 

mglL 

mglL 

mgA 

mglL 

Manganese 


Mercury 


Nickel 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7440-02-0 

5577-95 

5577-95 

5577-95 

5577-95 

5577-95 

27MARl995 

27MAR1995 

27MAR1995 

27MAR 1995 

27MARl995 

WG 

WG 

WG 

WG 

WG 

2.00E+00 

2.00E+00 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

N 

N 

N 

N 

N 

mglL 

mgfl 

mglL 

mglL 

mglL 


7440-02-0 

5577-95 27MAR1995 WG O.OOE+OO 

N 

mgfl 


NITRATEASNIT 5577-95 27MARl995 w l.OOE+OO 

N 

mgfl 


N ITRATEAS N IT 6700-95 22JUN1995 WG l.OOE+OO 

N 

mglL 

Potassium 


Radon 222 

Radon 222 

Selenium 

Selenium, Dissolved 

7440-09-7 

7440-09-7 

RN222 

RN222 

7702-49-2 

7782-49-2 

5577-95 

5577-95 

5577-95 

6700-95 

5577-95 

5577-95 

27MAR1995 

27MAR1995 

27MAR1995 

22JUNl995 

27MAR1995 

27MAR1995 

WG 

WG 

WG 

WG 

WG 

WG 

l.lOE+Ol 

O.OOE+OO 

4.63E+02 6.70E+01 

9.48E+03 1.24E+03 

O.OOE+OO 

0.00E+00 

c 

Q 

N 

N 

N 

N 

N 

mgk 

mgfl 

pCiL 

pCiL 

mgfl 

mglL 

Silica 

Silica 

7631-86-9 

7631 -86-9 

5577-95 

6700-95 

27MAR1995 

22JUN1995 

WG 

WG 

1.90E+01 

1.70E+01 

N 

N 

rng1L 

mglL 

Silver 

7440-22-4 

5577-95 27MAR1995 WG O.WE+OO 

< 

N 

mglL 

Silver. Dissolved 

7440-22-4 

5577-95 27MAR1995 w O.OOE+OO 

< 

N 

mglL 

Sodium 

7440-23-5 

5577-95 27MAR1995 w 1.40E+01 

N 

mglL 


7440-23-5 

5577-95 27MAR1995 WG 1.50E+01 

B 

N 

mglL 

Specific conductance SO145 

5577-95 27MARl995 w 2.22E+02 

N umhoslcm 


5570-95 27MARl995 WG 2.20E+02 

N umhodcm 


5579-95 27MAR1995 WG 2.17E+02 

N umhoslcm 


5500-95 27MAR1995 w 2.16E+02 

N umhodcm 


6700-95 22JUN1995 w 2.15E+02 

N umhoslcm 




Sulfate 

Sulfate 

SO145 

SO145 

SO145 

12143-45-2 

12143-45-2 

6701-95 

6702-95 

6703-95 

5577-95 

6700-95 

22JUN1995 

22JUN1995 

22JUN1995 

27MAR1995 

22JUN1995 

WG 

WG 

WG 

WG 

WG 

2.14E+02 

2.13E+02 

2.13E+02 

5.00E+00 

5.00E+00 

< 

< 

N 

N 

N 

N 

N 

umhodcm 

umhoslcm 

umhoslcm 

mglL 

mgfl 

Technetium-99 

14133-76-7 

5577-95 27MAR1995 WG l.lOE+Ol 1.80E+01 

N 

pci5 

Page 3 of 176



ANALYE CAS NUMBER SAMPLE ID DATE TYPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Technetium-99 14133-76-7 6700-95 22JUN1995 WG O.OOE+OO O.OOE+OO N pCilL 

Temperature 



Toluene 

Toluene 













Turbidity 

Turbidity 

Uranium 

Uranium 





Xylene 

Xylene 

Zinc 

Zinc. Dissolved 

cis-1.2dichloroethene 

cis-1.2-dichloroethene 

PH 

PH 

PH 

PH 

WAG 1. SWU 38, MW329 

1.1,l-Trichloroethane 

1 ,l,l-Trichloroethane 


1 .I .2-Trichloroethane 

1 .l -Dichloroethane 

1,l-Dichloroethane 


1 .l-Dichloroethene 



Alkalinity 

Alkalinity 

Antimony 


Arsenic 

Arsenic. Dissolved 

Barium 


Benzene 

Benzene 

Beryllium 

Beryllium. Dissolved 


Bromodichloromet hane 

Cadmium 


Calcium 




Chbride 

Chloride 

Chbroform 

Chloroform 

Chromium 

SO835 

127-18-4 

127-18-4 

108-88-3 

108-88-3 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

744044-0 

156-60-5 

156-60-5 

79-01 -6 

79-01-6 

SO278 

SO278 

7440-61 -1 

7440-61-1 

DIS U 

DIS U 

75-014 

75-01-4 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

156-59-2 

156-59-2 

SO296 

SO296 

SO296 

SO296 

71-55-6 

71-516 

79-00-5 

79-00-5 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

107-06-2 

107-06-2 

471-34-1 

471-34-1 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

71-43-2 

71-43-2 

744041 -7 

7440-41-7 

75-27-4 

75-27-4 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

56-23-5 

56-23-5 

16887-00-6 

16887-00-6 

67-66-3 

67-663 

7440-47-3 

5577-95 

5577-95 

6700-95 

5577-95 

6700-95 

5577-95 

5578-95 

5579-95 

5580-95 

6700-95 

6701-95 

6702-95 

6703-95 

5577-95 

6700-95 

5577-95 

6700-95 

5577-95 

6700-95 

5577-95 

6700-95 

5577-95 

6700-95 

5577-95 

6700-95 

5577-95 

6700-95 

5577-95 

5577-95 

5577-95 

6700-95 

5577-95 

5578-95 

5579-95 

5580-95 

5581 -95 

6704-95 

5581-95 

6704-95 

5581-95 

6704-95 

5581-95 

6704-95 

5581 -95 

6704-95 

5581 -95 

6704-95 

5581-95 

5581-95 

5581 -95 

5581 -95 

5581 -95 

5581 -95 

5581-95 

6704-95 

5581-95 

5581 -95 

5581-95 

6704-95 

5581 -95 

5581 -95 

55ai-95 

5581 -95 

5581-95 

6704-95 

5581-95 

6704-95 

5581-95 

6704-95 

5581 -95 

27MAR1995 

27MAR1995 

22JUN1995 

27MAR1995 

22JUNl995 

27MAR1995 

27MAR1995 

27MAR1995 

27MAR1995 

22JUNl995 

22JUN1995 

22JUN1995 

22JUN1995 

27MAR1995 

22JUN1995 

27MAR1995 

22JUN1995 

27MAR1995 

22JUNl995 

27MAR1995 

22JUNl995 

27MAR1995 

22JUN1995 

27MAR1995 

22 JUN 1995 

27MAR1995 

22JUN1995 

27MAR1995 

27MAR1995 

27MAR1995 

22JUN1995 

27MAR1995 

27MAR1995 

27MAR1995 

27MAR1995 

27MAR1995 

22JUN1995 

27MAR1995 

22JUNl995 

27MAR1995 

22JUNl995 

27MAR1995 

22JUN1995 

27MAR1995 

22JUN1995 

27MAR1995 

22JUNl995 

27MARl995 

27MAR1995 

27MAR1995 

27MAR1995 

27MAR1995 

27MAR1995 

27MARl995 

22JUN1995 

27MAR1995 

27MAR1995 

27MAR1995 

22JUN1995 

27MAR1995 

27MAR1995 

27MAR1995 

27MAR1995 

27MAR1995 

22JUNl995 

27MAR1995 

22JUNl995 

27MAR1995 

22JUNl995 

27MAR1995 

Page 4 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

w 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

6.00E+01 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

1 .OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

5.00E+00 

5.00E+00 

l.OOE+OO 

1 .WE+OO 

9.00E+00 

3.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

l.OOE+Ol 

l.OOE+OI 

l.OOE+Ol 

l.OOE+Ol 

0.00E+00 

0.00E+00 

5.00E+00 

5.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

6.10E+01 

6.60E+01 

O.WE+OO 

O.WE+OO 

O.WE+W 

O.WE+W 

0.00E+00 

0.00E+00 

5.WE+00 

5.00€+00 

0.00E+00 

O.OOE+W 

5.00E+00 

5.00€+00 

0.00E+00 

O.WE+W 

4.70E+Ol 


5.00€+00 

5.WE+00 

1.66E+02 

1.73E+02 

5.00E+00 

5.00E+00 

0.00E+00 

N 

U 

N 

U 

N 

U 

N 

U 

N 

< N 

c 

N 

c 

N 

< N 

< N 

< N 

c 

N 

c 

N 

U 

N 

U 

N 

UX 

N 

U 

N 

N 

N 

c 

N 

< N 

Q 

Q 

Q 

Q 

U 

N 

U 

N 

U 

N 

U 

N 

< N 

Q 

U 

N 

U 

N 

N 

N 

N 

N 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

c 

Q 

c 

Q 

U 

U 

U 

U 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

F 

uglL 

uglL 

uglL 

ugfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

uglL 

uglL 

N N 

NTU 

rnglL 

mglL 

mglL 

mglL 

ug1L 

uglL 

wfl 

ugfl 

WlL 

mglL 

uglL 

uglL 

su 

su 

su 

su 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

wfl 

uglL 

ug1L 

WlL 

mgfl 

mglL 

mglL 

mgk 

mglL 

mglL 

W L 

uglL 

uglL 

mgR 

msn 

uglL 

ugk 

mglL 

mglL 

mgfl 

mgfl 

ugfl 

uglL 

mglL 

mglL 

ugfl 

uglL 

msn




Chromium, Dissolved 7440-47-3 5581-95 27MAR1995 WG O.OOE+OO C N mglL 

Coball 

Coball, Dissolved 

Copper 




Dissolved Solis 


Ethylbenzene 

Ethylbenzene 

Fluoride 

Fluoride 

Gross Alpha 

Gross Alpha 

Gross Beta 

Gross Beta 

Iron 


Lead 


Magnesium 


Manganese 


Mercury 


Nickel 




Potassium 


Radon 222 

Radon 222 

Selenium 


Silica 

Silica 

Silver 


Sodium 





SpecifG conductance 




Specifc conductance 

Sulfate 

Sulfate 

Technetium99 

Technetium-99 

Temperature 



Toluene 

Toluene 









Trans-I .2-Dichloroethene 

Trans-I .Z-Dichloroethene 



7440-484 

7440-48-4 

7440-50-8 

7440-50-8 

DTW 

OXYGEN DIS 

SO266 

SO266 

100-41-4 

100-41-4 

16984-48-8 

16984-48-8 

I 2587-46-1 

12587-46-1 

12587-47-2 

I 2587-47-2 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7440-02-0 

7440-02-0 


N ITRATEAS NIT 

7440-09-7 

7440-09-7 

RN222 

RN222 

7782-49-2 

7782-49-2 

7631-86-9 

7631-86-9 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

12143-45-2 

12143-45-2 

14133-76-7 

14133-76-7 

so835 

127-18-4 

127-18-4 

108-88-3 

I 08-88-3 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

156-60-5 

156-60-5 

79-01-6 

79-01-6 

5581-95 

5581 -9s 

5581 -95 

5581-95 

5581-95 

5581-95 

5581-9s 

6704-95 

5581 -95 

6704-95 

5581 -9s 

6704-95 

5581-95 

6704-95 

5581-95 

6704-95 

5581-95 

5581-9s 

5581-95 

5581-95 

5581-95 

5581-95 

5581-95 

5581-95 

5581-95 

5581 -9s 

5581-95 

5581-95 

5581 -95 

6704-95 

5581-95 

5581 -95 

5581-95 

6704-95 

5581-95 

5581-95 

5581-95 

6704-95 

5581 -95 

5581-95 

5581-95 

5581-95 

5581 -95 

5582-95 

5583-95 

5584-95 

6704-95 

6705-95 

6706-95 

6707-95 

5581 -95 

6704-95 

5581-95 

6704-95 

5581 -95 

5581-95 

6704-95 

5581 -95 

6704-95 

5581-9s 

5582-95 

5583-95 

5584-95 

6704-95 

6705-95 

6706-95 

6707-95 

5581-95 

6704-95 

5581-95 

6704-95 

27MAR 1995 

27MAR1995 

27MAR1995 

27MAR 1995 

27MAR1995 

27MAR 1995 

27MAR1995 

22JUN1995 

27MARl995 

22JUN1995 

27MAR1995 

22JUN1995 

27MAR1995 

22JUN1995 

27MAR1995 

22JUN1995 

27MAR 1995 

27MAR1995 

27MAR1995 

27MAR1995 

27MAR1995 

27MAR1995 

27MAR1995 

27MARl995 

27MAR1995 

27MAR1995 

27MAR1995 

27MAR1995 

27MARI 995 

22JUN1995 

27MAR1995 

27MARl995 

27MARl995 

22JUN1995 

27MAR1995 

27MAR1995 

27MARl995 

22JUNl995 

27MAR1995 

27MARl995 

27MAR1995 

27MAR1995 

27MAR1995 

27MAR1995 

27MAR1995 

27MAR1995 

22JUN1995 

22JUN1995 

22JUN1995 

22 JUNl995 

27MAR1995 

22JUNl995 

27MAR1995 

22JUN1995 

27MAR1995 

27MAR1995 

22JUN1995 

27MAR1995 

22JUN1995 

27MAR1995 

27MAR1995 

27MAR1995 

27MAR1995 

22JUN1995 

22JUNl995 

22JUN1995 

22JUN1995 

27MAR1995 

22JUNl995 

27MARl995 

22JUN1995 

Page 5 of 176 

WG 

w 

w 

WG 

w 

w 

WG 

w 

w 

WG 

w 

w 

w 

w 

w 

w 

w 

WG 

w 

w 

w 

w 

w 

WG 

WG 

w 

WG 

WG 

w 

w 

WG 

WG 

w 

w 

w 

w 

w 

w 

w 

w 

w 

w.3 

WG 

w 

w 

WG 

w 

w 

w.3 

w 

w 

w 

w 

w 

w 

w 

WG 

w 

w 

w 

w 

WG 

WG 

w 

WG 

w 

w 

WG 

w 

w 

w 

< 

< 

C 

C 

U 

U 

C 

C 

< 

< 

Q 

c 

Q 

c: 

< 

c: 

c: 

< 

Q 

< 

Q 

< 

< 

B 

c 

C 

U 

U 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

Feet 

mglL 

mglL 

mglL 

uglL 

uglL 

mglL 

mglL 

pCYL 

pCi/L 

pCfL 

pCi/L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

WlL 

mgfl 

mglL 

mglL 

mglL 

mdL 

mglL 

mglL 

pCVL 

pCilL 

mglL 

mglL 

mg1L 

mglL 

mg1L 

mglL 

WlL 

mg/L 

umhoslcm 

umhoslcm 

umhoslcrn 

umhoslcrn 

umhoslcm 

umhoslcm 

umhos/crn 

umhoslcm 

WlL 

mglL 

pCVL 

pCVL 

F 

ugfl 

uglL 

ug1L 

uglL 

mglL 

rnglL 

mglL 

mglL 

mgk 

mglL 

mglL 

mgfl 

uglL 

ug1L 

ugk 

wfl




Turbidity SO278 5581-95 27MAR1995 WG 6.00E+00 N 

NTU 

Turbidity 

SO278 

6704-95 22JUN1995 

3.00€+00 

N 

N N 

Uranium 

7440-61-1 

5581-95 27MAR1995 0.00€+00 

< N 

mg/L 

Uranium 

7440-61 -1 

670495 22JUN1995 

O.WE+OO 

< N 

mglL 


DIS U 

5581-95 27MAR1995 0.00 E+OO 

Q 

Q 

mglL 


DIS U 

6704-95 22JUN1995 

O.OOE+OO 

Q 

Q 

mglL 


75-01-4 

5581-95 27MAR1995 1 .OOE+Ol 

U 

N 

uglL 


75-01-4 

6704-95 22JUN1995 

l.OOE+Ol 

U 

N 

uglL 

Xylene 

1330-20-7 

5581-95 27MAR 1995 

l.OOE+Ol 

U 

N 

uglL 

Xylene 

1330-20-7 

6704-95 22JUN1995 

l.OOE+Ol 

U 

N 

uglL 

Zinc 

7440-66-6 

5581-95 27MAR1995 O.OOE+OO 

< N 

mglL 



7440-66-6 

156-59-2 

5581-95 

5581-95 

27MAR1995 

27MAR1995 

O.OOE+OO 

5.00€+00 

Q 

U 

N 

mglL 

uglL 

cis-1.2-dichloroethene 156-59-2 

6704-95 22JUN1995 

5.00E+00 

U 

N 

ug1L 

PH 

SO296 

5581 -95 27MAR1995 6.00E+00 

N su 

PH 

SO296 

5582-95 27MAR1995 6.00E+00 

N su 

PH 

SO296 

5583-95 27MAR1995 6.00E+W 

N su 

PH 

SO296 

5584-95 27MARl995 

6.00E+00 

N su 

WAG 1, SWU 100, MWjfO 

1.1 ,I-Trichloroethane 


1.1,2-Trichloroethane 

1,1,2-TrichIoroethane 


1 .l-Dichloroethane 



1 .Z-Dichloroethane 

1,2-DichIoroethane 

Alkalinity 

Alkalinity 

Antimony 

Antimony. Dissolved 

Arsenic 

Arsenic, Dissolved 

Barium 


Benzene 

Benzene 

Beryllium 




Cadmium 


Calcium 




Chloride 

Chloride 

Chloroform 

Chloroform 

Chromium 


Cobalt 


Copper 






Ethylbenzene 

Ethylbenzene 

Fluoride 

Fluoride 

71-55-6 

71-55-6 

79-00-5 

79-00-5 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

107-06-2 

107-06-2 

471-34-1 

471-34-1 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

71-43-2 

71-43-2 

7440-41 -7 

7440-41 -7 

75-27-4 

75-27-4 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

56-23-5 

56-23-5 

16887-00-6 

16887-00-6 

67-66-3 

67-66-3 

7440-47-3 

7440-47-3 

7440-48-4 

7440-48-4 

7440-50-8 

7440-50-8 

DlW 

OXYGEN DIS 

SO266 

SO266 

100-41-4 

100-41-4 

16984-488 

1698448-8 

5585-95 

6708-95 

5585-95 

67oa95 

5585-95 

6708-95 

5585-95 

67oa95 

5585-95 

6708-95 

5585-95 

6708-95 

5585-95 

5585-95 

5585-95 

5585-95 

5585-95 

5585-95 

5585-95 

6708-95 

5585-95 

5585-95 

5585-95 

6708-95 

5585-95 

5585-95 

5585-95 

5585-95 

5585-95 

6708-95 

5585-95 

6706-95 

5585-95 

6708-95 

5585-95 

5585-95 

5585-95 

5585-95 

5585-95 

5585-95 

5585-95 

5585-95 

5585-95 

6708-95 

5585-95 

670895 

5585-95 

6708-95 

07MARl995 

26JUN1995 

07MAR1995 

26JUN1995 

07MAR1995 

26JUN1995 

07MARl995 

26JUN1995 

07MAR1995 

26JUN1995 

07MAR1995 

26JUN1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR 1995 

O7MAR 1995 

07MAR1995 

07MAR1995 

26JUNl995 

07MAR1995 

07MARl995 

07MAR1995 

26JUNl995 

07MAR1995 

07MARI 995 

07MAR1995 

07MAR1995 

07MAR 1995 

26JUN1995 

07MAR1995 

26JUNl995 

07MAR1995 

26JUN1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

26JUNl995 

07MARl995 

26JUNl995 

07MAR1995 

26JUN1995 

5.00E+00 

5.00E+00 

5.00E+00 

5.00€+00 

5.00E+00 

5.00€+00 

5.00E+00 

5.WE+00 

5.00E+00 

S.WE+OO 

1.22€+02 

1.32E+02 

O.OOE+OO 

0.00E+00 

0.00E+00 

0.00E+00 

1 .WE+00 

l.OOE+OO 

5.00E+00 

5.00E+00 

0.00E+00 

O.WE+OO 

5.00E+00 

5.00E+00 

O.WE+OO 

O.WE+W 

2.90E+Ol 

3.20E+01 

5.00E+00 

5.00€+00 

2.10E+01 

1.90E+01 

5.00E+00 

5.WE+W 

O.WE+OO 

O.OOE+OO 

0.WE+00 

O.OOE+OO 

O.WE+OO 

O.WE+OO 

4.90E+OI 

l.OOE+OO 

1.74E+02 

1.92€+02 

5.00E+W 

5.00E+W 

O.WE+W 

O.WE+W 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

c 

Q 

c 

Q 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

uglL 

uglL 

uglL 

uglL 

ug1L 

uglL 

uglL 

uglL 

uglL 

mg/L 

mglL 

mg/L 

mglL 

mglL 

mg/L 

mglL 

mglL 

ug1L 

uglL 

mglL 

mg/L 

ugfl 

uglL 

mglL 

rnglL 

mg/L 

WlL 

ugfl 

ugk 

mglL 

mglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mgn 

mglL 

WlL 

Feet 

mg/L 

W/L 

mg1L 

ugR 

uglL 

mgk 

wfl 

Gross Alpha 

12587-46-1 

5585-95 07MAR1995 2.00E+W 9.00E-01 

N 

pciL 

Gross Alpha 

12587-46-1 

6708-95 26JUN1995 

4.00E+W 9.00E-01 

N 

pciL 

Gross Beta 

Gross Beta 

Iron 

12587-47-2 

1258747-2 

7439-89-6 

5585-95 

6708-95 

5585-95 

07MAR1995 

26JUN1995 

07MAR1995 

8.WE+W 4.00€+00 

7.00E+00 1.00E+00 

5.00E+00 

N 

N 

N 

pCi 

pCi 

mgR 

Page 6 of 176




Iron, Dissolved 7439-89-6 5585-95 07MAR1995 WG O.OOE+OO 

< 

N 

mg1L 

Lead 


Magnesium 


Manganese 


Mercury 

7439-92-1 

7439-92-1 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-97-6 

5585-95 

5585-95 

5585-95 

5585-95 

5585-95 

5585-95 

5585-95 

07MAR1995 

07MAR1995 

07MAR 1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MARl995 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

< 

c 

c 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 


7439-97-6 

5585-95 07MAR1995 WG 

Q 

N 

mglL 

Nickel 

7440-02-0 

5585-95 07MAR 1995 WG 

c 

N 

mglL 




Potassium 


Radon 222 

Radon 222 

Selenium 


Silica 

Silica 

Silver 


Sodium 










Sulfate 

Sulfate 

Technetium-99 

Technetium99 

Temperature 



Toluene 

7440-02-0 


NITRATEASNIT 

7440-09-7 

7440-09-7 

RN222 

RN222 

7782-49-2 

7782-49-2 

7631-86-9 

7631 -86-9 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

12143-45-2 

12143-45-2 

14133-76-7 

14133-76-7 

SO835 

127-18-4 

127-18-4 

10~8-3 

5585-95 

5585-95 

6708-95 

5585-95 

5585-95 

5585-95 

6708-95 

5585-95 

5585-95 

5585-95 

6708-95 

5585-95 

5585-95 

5585-95 

5585-95 

5585-95 

5586-95 

5587-95 

5588-95 

6708-95 

6709-95 

6710-95 

6711-95 

5585-95 

6708-95 

5585-95 

6708-95 

5585-95 

5585-95 

6708-95 

558595 

07MAR1995 

07MAR1995 

26JUN1995 

07MAR 1995 

07MARl995 

07MAR1995 

26JUN1995 

07MAR1995 

07MAR1995 

07MAR1995 

26JUN1995 

07MAR1995 

07MAR1995 

07MARl995 

O7MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

07MAR1995 

26JUN1995 

26JUNl995 

26JUN1995 

26JUN1995 

07MAR 1995 

26JUN1995 

07MAR1995 

26JUN1995 

07MAR1995 

07MAR1995 

26JUN1995 

07MAR1995 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

Q 

c 

c 

< 

Q 

c 

Q 

c 

< 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mg1L 

pCVL 

pCVL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

umhoslcm 

umhodcm 

umhoslcm 

umhodcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhoslcm 

mgfl 

mglL 

pCVL 

pCVL 

F 

uglL 

uglL 

uglL 

Toluene 











Tfichloroethene 

Trichloroet hene 

108-88-3 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

156-60-5 

156-60-5 

79-01-6 

79-01 -6 

6708-95 

5585-95 

5586-95 

5587-95 

5588-95 

6708-95 

6709-95 

6710-95 

6711-95 

5585-95 

6708-95 

5585-95 

6708-95 

26JUN1995 

07MAR1995 

07MARl995 

07MAR1995 

07MAR1995 

26JUN1995 

26JUN1995 

26JUNl995 

26JUN1995 

07MAR1995 

26JUNl995 

07MAR1995 

26JUN1995 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

U 

c 

c 

< 

< 

c 

c 

c 

c 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

uglL 

mglL 

mglL 

mglL 

rnglL 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

uglL 

uglL 

Turbidity 

Turbidity 

Uranium 

Uranium 


SO278 

SO278 

7440-61 -1 

7440-61 -1 

DIS U 

5585-95 

6708-95 

5585-95 

6708-95 

5585-95 

07MAR1995 

26JUNl995 

07MAR1995 

26JUN1995 

07MAR1995 

WG 

WG 

WG 

WG 

WG 

< 

c 

Q 

N 

N 

N 

N 

Q 

NTU 

NTU 

mglL 

mglL 

mglL 

Uranium. Dissolved 

DIS U 

6708-95 26JUN1995 WG 

Q 

Q 

mglL 


75-014 

5585-95 07MAR1995 WG 

U 

N 

uglL 


75-01-4 

6708-95 26JUN1995 WG 

U 

N 

ugfl 

Xylene 

1330-20-7 

5585-95 07MAR1995 WG 

U 

N wfl 

Xylene 

1330-20-7 

6708-95 26JUN1995 WG 

U 

N 

uglL 

Zinc 

7440-66-6 

5585-95 07MAR1995 WG 

c 

N 

mglL 

Zinc. Dissotved 

7440-66-6 

5585-95 07MAR1995 WG 

c 

N 

mglL 


5585-95 07MAR1995 WG 

U 

N 

uglL 

cis-1.2dichloroethene 156-59-2 

6708-95 26JUN1995 WG 

U 

N 

uglL 

PH 

so296 

5585-95 07MAR1995 WG 

N su 

PH 

SO296 

5586-95 07MAR1995 WG 

N su 

PH 

so296 

5587-95 07MAR1995 WG 

N su 

PH 

so296 

5588-95 07MAR1995 WG 

N su 

Page 7 of 176



WAG 1, SWU 136, MW25 

1 ,I,I-Trichloroethane 

1 ,I.I-Trichloroethane 









Alkalinity 

Alkalinity 

Antimony 


Arsenic 


Barium 


Benzene 

Benzene 

Beryllium 




Cadmium 


Calcium 




Chloride 

Chloride 

Chloroform 

Chloroform 

Chromium 


Coban 


Copper 






Ethylbenzene 

Ethylbenzene 

Fluoride 

Fluoride 

Gross Alpha 

Gross Alpha 

Gross Beta 

Gross Beta 

Iron 


Lead 


Magnesium 


Manganese 


Mercury 

71 -55-6 

71-55-6 

79-00-5 

79-00-5 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

107-06-2 

107-06-2 

471-34-1 

471-34-1 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

71 -43-2 

71-43-2 

7440-41 -7 

7440-41 -7 

75-27-4 

75-27-4 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

5623-5 

56-23-5 

16887-00-6 

16887-00-6 

67-66-3 

67-66-3 

7440-47-3 

7440-47-3 

7440-48-4 

7440-48-4 

7440-50-8 

7440-50-8 

DTW 

OXYGEN DIS 

SO266 

SO266 

100-41-4 

100-41 -4 

16984-48-8 

16984-48-8 

12587-46-1 

12587-46-1 

12587-47-2 

12587-47-2 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-97-6 

5565-95 

6688-95 

5565-95 

6688-95 

5565-95 

6688 - 95 

5565 - 95 

6688-95 

5565-95 

6688-95 

5565-95 

6688-95 

5565-95 

5565-95 

5565-95 

5565-95 

5565-95 

5565-95 

5565-95 

6688-95 

5565-95 

5565-95 

5565-95 

6688-95 

5565-95 

5565-95 

5565-95 

5565-95 

5565-95 

6688-95 

5565-95 

6688-95 

5565-95 

6688-95 

5565-95 

5565-95 

5565-95 

5565-95 

5565-95 

5565-95 

5565-95 

5565-95 

5565-95 

6688-95 

5565-95 

6688-95 

5565-95 

6688-95 

5565-95 

6688-95 

5565-95 

668695 

5565-95 

5565-95 

5565-95 

5565-95 

5565-95 

5565-95 

5565-95 

5565-95 

5565-95 

06MARl995 

26JUN1995 

06MAR1995 

26JUN1995 

O6MARI 995 

26JUN1995 

O6MAR1 995 

26JUN1995 

06MAR1995 

26JUN1995 

OMARl995 

26JUN1995 

06MARI 995 

06MARl995 

06MAR1995 

06MAR1995 

06MAR1995 

06MARI 995 

06MAR1995 

26JUN1995 

O6MAR1 995 

06MAR1995 

06MARI 995 

26JUN1995 

06MAR1995 

-1995 

06MAR1995 

06MARl995 

06MAR1995 

26JUN1995 

06MARl995 

26JUNl995 

06MARl995 

26JUN1995 

06MAR1995 

06MAR1995 

06MARI 995 

06MAR1995 

06MAR1995 

06MARl995 

06MAR1995 

06MAR1995 

06MAR1995 

26JUN1995 

06MARl995 

26JUNI 995 

06MAR1995 

26JUN1995 

06MAR1995 

26JUNl995 

06MAR1995 

26JUNl995 

06MAR1995 

06MARl995 

-1995 

06MARl995 

06MAR1995 

-1995 

-1995 

06MARl995 

06MAR 1995 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

< 

Q 

< 

0 

U 

U 

< 

< 

U 

U 

< 

< 

U 

U 

U 

U 

< 

< 

< 

< 

< 

< 

U 

U 

< 

< 

< 

< 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ug1L 

uglL 

uglL 

uglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

mglL 

mglL 

uglL 

uglL 

mg/L 

mg/L 

mg/L 

mglL 

uglL 

uglL 

mg/L 

mglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mg1L 

Feet 

mglL 

mgfl 

mglL 

uglL 

uglL 

mglL 

mglL 

pCiL 

pCilL 

pCiL 

pCi 

mglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

mg/L 

mglL 

mgfl 


7439-97-6 

5565-95 -1995 WG 

Q 

N 

mgfl 

Nickel 

7440-02-0 

5565-95 -1995 WG 

< 

N wfl 




Potassium 

Potassium. Dissolved 

Radon 222 

Radon 222 

Selenium 

7440-02-0 

NITRATEASNIT 

NITRATEASNIT 

7440-09-7 

7440-09-7 

RN222 

RN222 

7782-49-2 

5565-95 

5565-95 

6688-95 

556595 

556595 

556595 

6688-95 

5565-95 

-1995 

06MAR1995 

26JUNl995 

06MAR1995 

-1995 

-1995 

26JUN1995 

06MARl995 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

< 

< 

c 

c 

N 

N 

N 

N 

N 

N 

N 

N 

mgfl 

mglL 

mgfl 

mglL 

mgfl 

pCilL 

pciR 

mgfl 

Page 8 of 176




Selenium, Dissolved 7782-49-2 5565-95 06MAR1995 WG O.OOE+OO Q N 

Silica 

Silica 

Silver 


Sodium 



Specific conduclance 







Sulfate 

Sulfate 

Technetium-99 

Technetium-99 

Temperature 



Toluene 

Toluene 









Trans-I ,Z-Dichloroethene 

Trans-I ,2-Dichloroethene 


Trichbroelhene 

Turbidity 

Turbidity 

Uranium 

Uranium 


Uranium. Dissolved 



Xylene 

Xylene 

Zinc 




PH 

PH 

PH 

PH 

WAG 1. SWU 136, MW326 



1 .I ,2-Trichloroethane 




I .I-Dichloroethene 



1,2-Dichloroelhane 

Alkalinity 

Alkalinity 

Antimony 


Arsenic 


Barium 

7631-86-9 

7631-86-9 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

12143-45-2 

12143-45-2 

14133-76-7 

14133-76-7 

SO835 

127-10-4 

127-184 

100-88-3 

108-88-3 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

156-60-5 

156-60-5 

79-01-6 

79-01-6 

SO278 

SO278 

7440-61 -1 

7440-61 -1 

DIS U 

DIS U 

75-01-4 

75-01-4 

1330-20-7 

1330-20-7 

7440 - 66 - 6 

7440-66-6 

156-59-2 

156-59-2 

SO296 

SO296 

SO296 

SO296 

71-55-6 

71-55-6 

79-00-5 

79-00-5 

75-34-3 

75-34-3 

75-354 

75-3w 

107-06-2 

107-06-2 

471-34-1 

471-34-1 

7440-36-0 

7440-36-0 

7440-36-2 

7440-30-2 

7440-39-3 

5565-95 

6688-95 

5565 - 95 

5565-95 

5565-95 

5565-95 

5565-95 

5566-95 

5567-95 

5568-95 

6688-95 

6689-95 

6690-95 

6691-95 

5565-95 

6688-95 

5565-95 

6680-95 

5565-95 

5565-95 

6688-95 

5565-95 

6688-95 

5565-95 

5566-95 

5567-95 

5568-95 

6688-95 

6689-95 

6690-95 

6691-95 

5565-95 

6688-95 

5565-95 

6688-95 

5565-95 

6688-95 

5565-95 

6688-95 

5565-95 

6688-95 

5565-95 

6688-95 

5565-95 

6688-95 

5565-95 

5565-95 

5565-95 

6688-95 

5565-95 

5566-95 

5567-95 

5568-95 

5569-95 

6692-95 

5569-95 

6692-95 

5569-95 

6692-95 

5569-95 

6692-95 

5569-95 

6692-95 

5569-95 

6692-95 

5569-95 

5569-95 

5569-95 

5569-95 

5569-95 

06MAR1995 

26JUN1995 

06MAR1995 

06MAR1995 

06MAR1995 

O6MAR 1995 

O6MAR1 995 

06MAR1995 

06MAR1995 

06MAR1995 

26JUN1995 

26JUN1995 

26JUN1995 

26JUNl995 

O6MAR 1995 

26JUN1995 

O6MAR1 995 

26JUN1995 

06MAR1995 

06MAR 1995 

26JUNl995 

06MAR1995 

26JUN1995 

06MAR1995 

06MAR1995 

06MAR1995 

O6MAR1 995 

26JUN1995 

26JUN1995 

26JUN1995 

26JUN1995 

06MAR1995 

26JUNl995 

06MAR1995 

26JUNl995 

06MAR1995 

26JUN1995 

06MARl995 

26JUN1995 

MAR1 995 

26JUN1995 

06MAR1995 

26JUN1995 

06MAR1995 

26JUN1995 

06MAR1995 

06MAR1995 

06MAR1995 

26JUN1995 

06MARl995 

06MARl995 

06MAR1995 

06MAR1995 

06MARl995 

26JUN1995 

06MAR1995 

26JUN1995 

06MARl995 

26JUN1995 

06MAR1995 

26JUN1995 

06MAR1995 

26JUNl995 

06MAR1995 

2 6JUN 1995 

06MAR1995 

06MARl995 

06MAR1995 

06MARl995 

06MAR1995 

Page 9 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

wc, 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

wc, 

WG 

WG 

WG 

wc, 

WG 

WG 

WG 

WG 

WG 

< 

Q 

< 

c 

< 

< 

U 

U 

< 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

4 

Q 

c 

Q 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Q 

Q 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

umhoslcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhodcm 

umhoslcm 

umhoslcm 

mglL 

mglL 

pCi/L 

pCilL 

F 

uglL 

uglL 

uglL 

uglL 

mglL 

mglL 

WlL 

mg1L 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

uglL 

uglL 

NTU 

NTU 

WlL 

WlL 

mglL 

WlL 

uglL 

uglL 

uglL 

ug1L 

mglL 

mglL 

uglL 

uglL 

su 

su 

su 

su 

uglL 

uglL 

uglL 

ug1L 

uglL 

uglL 

ugfl 

ugfl 

uglL 

uglL 

wfl 

WlL 

mgfl 

mg5 

mgfl 

mgfl 

Wfl



ANALME CAS NUMBER SAMPLE ID DATE WPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Barium, Dissolved 7440-39-3 5569-95 06MAR1995 WG O.OOE+OO 

N 

mg1L 

Benzene 

Benzene 

Beryllium 




Cadmium 


Calcium 




Chloride 

Chloride 

Chloroform 

71 -43-2 

71-43-2 

7440-41 -7 

7440-41 -7 

75-27-4 

75-27-4 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

56-23-5 

56-23-5 

16887-00-6 

16887-00-6 

67-66-3 

5569-95 

6692-95 

5569-95 

5569-95 

5569-95 

6692-95 

5569-95 

5569-95 

5569 - 95 

5569 - 95 

5569 - 95 

6692-95 

5569-95 

6692-95 

5569-95 

06MAR1995 

26JUN1995 

06MAR1995 

06MAR1995 

06MAR1995 

26JUN1995 

06MAR1995 

06MAR1995 

06MARl995 

06MARl995 

06MAR1995 

26JUN1995 

06MAR1995 

26JUN1995 

O6MAR 1995 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

U 

U 

c 

< 

U 

U 

c 

C 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

uglL 

uglL 

mglL 

mglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

mglL 

mglL 

uglL 

Chloroform 

67-66-3 

6692-95 26JUN1995 WG 

U 

N 

uglL 

Chromium 

7440-47-3 

5569-95 06MAR 1995 WG 

< 

N 

mglL 

Chromium, Dissolved 7440-47-3 

5569-95 06MARI 995 w 

< 

N 

mglL 

Coban 


Copper 






Ethylbenzene 

7440-48-4 

7440-48-4 

7440-50-8 

7440-50-8 

DTW 

OXYGEN DIS 

SO266 

SO266 

100-41-4 

5569-95 

5569-95 

5569 - 95 

5569-95 

5569-95 

5569-95 

5569-95 

6692-95 

5569-95 

06MAR1995 

06MAR1995 

06MAR1995 

WMAR1995 

WMAR 1995 

06MAR1995 

06MAR1995 

26JUN1995 

WAR1995 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

C 

C 

< 

C 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

rnglL 

mg1L 

rnglL 

mglL 

Feet 

mglL 

mglL 

mgfl 

uglL 

Ethylbenzene 

Fluoride 

Fluoride 

Gross Alpha 

Gross Alpha 

Gross Beta 

Gross Beta 

Iron 


Lead 


Magnesium 


Manganese 

100-41-4 

i 6984-48-8 

16984-46-8 

12587-46-1 

12587-46-1 

12587-47-2 

12587-47-2 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-95-4 

7439-95-4 

7439-96-5 

6692-95 

5569-95 

6692-95 

5569-95 

6692-95 

5569-95 

6692-95 

5569-95 

5569-95 

5569-95 

5569-95 

5569-95 

5569-95 

5569-95 

26JUN1995 

06MAR1995 

26JUN1995 

06MAR1995 

26JUN1995 

06MARI995 

26JUN1995 

06MAR1995 

06MAR1995 

06MAR1995 

06MARl995 

06MAR1995 

06MARI 995 

06MARI 995 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

uglL 

mglL 

mglL 

pCilL 

pCilL 

pCiL 

pCilL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mg1L 

Manganese, Dissolved 7439-96-5 

5569-95 06MARI995 WG 

N 

mglL 

Mercury 

7439-97-6 

5569-95 06MARl995 w 

N 

mglL 


Nickel 




Potassium 


Radon 222 

Radon 222 

Selenium 


Silica 

Silica 

Silver 


7439-97-6 

7440-02-0 

7440-02-0 

N ITRAEASN IT 


7440-09-7 

7440-09-7 

RN222 

RN222 

7782-49-2 

7782-49-2 

7631 -86-9 

7631-86-9 

7440-22-4 

7440-22-4 

5569-95 

5569-95 

5569-95 

5569-95 

6692-95 

5569-95 

5569-95 

5569-95 

6692-95 

5569-95 

5569-95 

5569-95 

6692-95 

5569-95 

5569-95 

06MAR1995 

06MAR1995 

06MARl995 

06MAR1995 

26JUN 1995 

06MAR1995 

06MAR1995 

06MAR1995 

26JUN1995 

06MARl995 

06MARl995 

06MAR1995 

26JUNl995 

06MAR1995 

06MAR1995 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

CS 

Q 

< 

Q 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

WlL 

mglL 

mglL 

WlL 

mglL 

mg1L 

pCiL 

pCiR 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

Sodium 


7440-23-5 

7440-23-5 

5569-95 

5569-95 

06MAR 1995 

WAR1995 

WG 

WG 

N 

N 

mglL 

mg1L 


5569-95 06MAR1995 WG 

N umhodcm 


5570-95 06MARl995 WG 

N umhoslcm 


5571-95 06MARl995 w 

N umhos/cm 


5572-95 06MAR1995 w 

N umhoslcm 





SO145 

SO145 

SO145 

SO145 

6692-95 

6693-95 

6694-95 

6695-95 

26JUN1995 

26JUNl995 

26JUNl995 

26JUNl995 

WG 

WG 

WG 

WG 

N 

N 

N 

N 

umhoslcm 

umhoslcm 

umhodcm 

umhodcm 

Sulfate 

1214345-2 

5569-95 06MAR1995 WG 

< 

N wfl 

Sulfate 

1214345-2 

6692-95 26JUN1995 w 

< 

N 

mg1L 

Technetium99 

14133-767 

5569-95 06MAR1995 WG 

N 

pci5 

Page 10 of 176




Technetium-99 14133-76-7 6692-95 26JUN1995 WG 2.00E+00 1.20E+01 N DCUL 

Temperature 

SO835 

5569-95 O6MAR 1995 WG 

N 

F 



Toluene 

Toluene 












Turbidity 

Turbidity 

Uranium 

Uranium 





Xylene 

127-18-4 

127-18-4 

108-88-3 

108-88-3 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

156-60-5 

156-60-5 

79-01-6 

79-01-6 

SO278 

SO278 

7440-61 -1 

7440-61 -1 

DIS U 

DIS U 

75-01-4 

75-01-4 

1330-20-7 

5569-95 

6692-95 

5569-95 

6692-95 

5569-95 

5570-95 

5571-95 

5572-95 

6692-95 

6693-95 

6694-95 

5569-95 

6692-95 

5569-95 

6692-95 

5569-95 

6692-95 

5569-95 

6692-95 

5569-95 

6692-95 

5569-95 

6692-95 

5569-95 

06MAR1995 

26JUN1995 

06MAR1995 

26JUN1995 

O6MAR 1995 

06MAR1995 

06MAR1995 

06MAR1995 

26JUNl995 

26JUN1995 

26JUN1995 

06MAR1995 

26JUN1995 

06MAR1995 

26JUN1995 

06MARl995 

26JUN1995 

06MAR1995 

26JUN1995 

06MARl995 

26JUN1995 

06MAR1995 

26JUNl995 

06MARl995 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

U 

U 

U 

U 

< 

< 

< 

< 

< 

< 

< 

U 

U 

< 

< 

Q 

Q 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Q 

Q 

N 

N 

N 

uglL 

uglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

ug1L 

ug1L 

ugk 

uglL 

NTU 

N N 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

ugfl 

Xylene 

1330-20-7 

6692-95 26JUNl995 WG 

U 

N 

ugfl 

Zinc 

7440-66-6 

5569-95 06MAR1995 WG 

< N 

WlL 


7440-66-6 

5569-95 06MAR1995 WG 

< N 

mgk 

ck-1.2-dichloroethene 156-59-2 

5569-95 06MARl995 WG 

U 

N 

ugn 


6692-95 26JUN1995 WG 

U 

N 

ugk 

PH 

so296 

5569-95 06MAR1995 WG 

N su 

PH 

SO296 

5570-95 06MAR1995 WG 

N su 

PH 

SO296 

5571-95 06MAR1995 WG 

N su 

PH 

SO296 

5572-95 06MAR1995 nG 

N su 

WAG 7, Sv\IMU 8, C746K-1 





1 ,l-Dchloroethane 


1020-92 

1140-92 

1329-92 

1474-92 

1621-92 

1793-92 

< 

< 

< 

uglL 

uglL 

uglL 

1 ,l-Dchloroethane 



1 .l-Dchloroethane 






1 .I -Dichloroethene 

1 ,l-Dichloroethene 









. 1 .l-Dchloroethene 

Aluminurn 

Aluminum 

Aluminum 

Aluminurn 

Aluminurn 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-354 

75-354 

75-354 

75-354 

75-35-4 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

1934-92 

2098-92 

393-92 

516-92 

628-92 

697-92 

852-92 

1020-92 

1140-92 

1329-92 

1474-92 

1621-92 

1793-92 

1934-92 

2098-92 

393-92 

516-92 

628-92 

697-92 

852-92 

1020-92 

1072-93 

1140-92 

1202-93 

1202-94 

1329-92 

1346-93 

1376-94 

1474-92 

1546-93 

04MAYl992 

01 JUNl992 

06 JULl992 

03AUGl992 

31AUG1992 

070CT1992 

03NOV1992 

01 DEC1992 

30JANl992 

16FEB1992 

05MAR1992 

12MARl992 

01 APR1992 

04MAY 1992 

01 JUN1992 

06JUL1992 

03AUG1992 

3lAUG 1992 

070CT1992 

03NOV1992 

01 DECl992 

3OJANl992 

16FEB1992 

MAR1 992 

12MARl992 

01 APRl992 

04MAY 1992 

16JUL1993 

01 JUNl992 

05AUG1993 

05MAY1994 

06JUL1992 

02SEP1993 

03JUN1994 

03AUGl992 

050CTl993 

Page 11 of 176 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

< 

< 

< 

< 

< 

< 

UJ 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

UJ 

< 

< 

< 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

ugfl 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ugA 

uglL 

ug1L 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ugR 

uglL 

uglL 

uglL 

uglL 

uglL 

mg1L 

mglL 

mglL 

mgk 

mglL 

mglL 

WlL 

WlL 

mglL 

mg1L




Aluminum 7429-90-5 161 2-94 OlJUL1994 WS O.OOE+OO N mglL 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7~0-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

1621 -92 

17-94 

1793-92 

1836-93 

1918-94 

1934-92 

2098-92 

21 21 -94 

2152-93 

2 1 8-95 

241 1-94 

2689-94 

2859-94 

286-94 

393-92 

435-95 

505-94 

5511-92 

619-93 

18-95 

628-92 

631 -95 

634-93 

697-92 

785-95 

800-93 

852-92 

899-94 

1020-92 

1140-92 

1329-92 

1474-92 

162 1-92 

1793-92 

1934-92 

393-92 

551 1-92 

619-93 

697-92 

1020-92 

1072-93 

2098-92 

628-92 

852-92 

1140-92 

1202-93 

1202-94 

1329-92 

1346-93 

1376-94 

1474-92 

1546-93 

1612-94 

1621-92 

17-94 

1793-92 

1836-93 

1934-92 

2121-94 

2152-93 

218-95 

241 1-94 

2689-94 

2859-94 

286-94 

393-92 

435-95 

505-94 

18-95 

1918-94 

2098-92 

31 AUGl992 

05JANl994 

070CT1992 

05JAN1995 

04NOV1993 

05AUG1994 

03NOV1992 

01DEC1992 

02SEPl994 

10DEC1993 

03FEBl995 

070CT1994 

04NOV1994 

02DECl994 

04FEB1994 

3OJANl992 

03MAR1995 

03MAR1994 

19AUG1992 

05MAY 1993 

05MARl992 

05APRl995 

05MAY1993 

12MAR1992 

03MAY 1995 

02JUN1993 

01 APR1992 

08APR1994 

OWY 

1992 

OlJUNl992 

06JUL1992 

03AUG1992 

3lAUGl992 

070CT1992 

03NOV1992 

01 DECl992 

3OJANl992 

19AUGl992 

M Y 

1993 

osMAR1992 

12MAR1992 

01 APR 1992 

04MAY 1992 

16JUL1993 

01 JUN1992 

05AUG1993 

WAY 

1994 

06JUL1992 

02SEPl993 

03JUN1994 

03AUGl992 

050CT1993 

01 JULl994 

31AUG1992 

05JAN1994 

070CT1992 

WAN1 995 

04NOVl993 

05AUG1994 

03NOV1992 

01 DEC1992 

02SEPl994 

10DECl993 

03FEB1995 

070CT1994 

04NOV1994 

02DECl994 

04FEB1994 

3OJAN1992 

ow1995 

ow1994 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

1 .OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

O.OOE+OO 

1.00E+00 

O.OOE+OO 

l.OOE+OO 

3.20E+01 

O.OOE+OO 

l.OOE+OO 

O.WE+OO 

l.OOE+OO 

O.OOE+OO 

O.OOE+OO 

l.OOE+OO 

1.00E+00 

1.00E+00 

O.OOE+OO 

l.OOE+OO 

1.00E+00 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

0.00E+00 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+W 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

0.00E+00 

0.00E+00 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

0 .OOE+ 00 

0.00E+00 

0.00E+00 

O.M)E+OO 

0.00E+00 

O.OOE+W 

0.00E+00 

O.OOE+W 

0.00E+00 

C 

< 




Arsenic 7440-38-2 5511-92 19AUG1992 WS O.OOE+OO < N mglL 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440 - 38 - 2 

7440-38-2 

7 4 4 0 - 3 8 - 2 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440 - 39 - 3 

7440-39-3 

7 4 4 0 - 3 9 - 3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7 44 0 - 3 9 - 3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440- 39 - 3 

71-43-2 

7143-2 

71-43-2 

71-43-2 

71 -43-2 

71-43-2 

7143-2 

7 I 43-2 

71-43-2 

71-43-2 

7143-2 

71-43-2 

71-43-2 

7440-41-7 

7440-41-7 

7440-41-7 

744041-7 

7440-41-1 

7440-41-7 

7440-41 -7 

7440-41 -7 

7440-41-7 

7440-41-7 

619-93 

628-92 

631-95 

634-93 

697-92 

785-95 

800-93 

852-92 

899-94 

1020-92 

1072-93 

1140-92 

1202-93 

1202-94 

1329-92 

1346-93 

1376-94 

1474-92 

1546-93 

1612-94 

1621-92 

17-94 

1793-92 

18-95 

1836-93 

1918-94 

1934-92 

2098-92 

21 21 -94 

2152-93 

218-95 

2411-94 

2689-94 

2859-94 

286-94 

393-92 

435-95 

505-94 

5511-92 

619-93 

628-92 

631 -95 

634-93 

697-92 

705-95 

800-93 

852-92 

899-94 

1020-92 

1140-92 

1329-92 

1474-92 

1621 -92 

1793-92 

1934-92 

2098-92 

393-92 

516-92 

628-92 

697-92 

852-92 

1020-92 

1140-92 

1329-92 

1474-92 

1621-92 

1793-92 

1934-92 

2098-92 

393-92 

5511-92 

O5MAY 1993 

05MAR1992 

05APR1 995 

EMAY 1993 

12MAR 1 992 

O3MAY 1995 

02JUN1993 

01 APRl992 

08APR1994 

04MAY 1992 

16JUL1993 

01JUN1992 

05AUG1993 

O5MAY 1994 

06JUL1992 

O2SEP1993 

03JUN1994 

03AUG1992 

OSOCTI 993 

01 JUL1994 

3lAUGl992 

05JAN1994 

070CT1992 

05JAN1995 

04NOV1993 

05AUG1994 

03NOV1992 

OlDEC1992 

O2SEPl 994 

lODEC1993 

03FE61995 

070CT1994 

04NOV1994 

02DEC1994 

04FE61994 

30JAN1992 

03MAR1995 

03MARl994 

19AUGI 992 

05MAY1993 

OWARI 992 

05APR1995 

05MAY 1993 

12MARl992 

03MAY 1995 

02JUN1993 

01 APR 1992 

08APR1994 

04MAY1992 

01JUN1992 

06JUL1992 

03AUGl992 

3lAUGl992 

070CTI 992 

03NOV1992 

01DECl992 

30JAN1992 

16FEB1992 

05MAR1992 

12MAR1992 

01 APR 1992 

04MAY 1 992 

01JUNl992 

06JULI 992 

03AUG1992 

3lAUG 1992 

070CT1992 

03NOV1992 

01DEC1992 

3WAN1992 

19AUG 1992 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

< N 

< N 

< N 

< N 

< N 



ANAL'fTE CAS NUMBER SAMPLE ID DATE TYPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Beryllium 7440-41 -7 619-93 O5MAY1993 WS O.OOE+OO 

c 

N 

mglL 

Beryllium 

Beryllium 

Beryllium 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

7440-41-7 

7440-41-7 

7440-41 -7 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

628-92 

697-92 

852-92 

1020-92 

1140-92 

1329-92 

1474-92 

O5MAR1 992 

12MARl992 

01 APRl992 

04MAY 1992 

01 JUN1992 

06JULl992 

03AUG1992 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

c 

c 

c 

c 

c 

c 

c 

N 

N 

N 

NT 

N 

N 

N 

mglL 

mglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

7440-69-9 

7440 - 69 - 9 

7440-69-9 

7440-69-9 

7440-69-9 

1621-92 

1793-92 

1934-92 

2098-92 

393-92 

31 AUGl992 

070CT1992 

03NOV1992 

OlDEC1992 

3OJANl992 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

c 

c 

c 

c 

c 

N 

N 

N 

N 

N 

mglL 

WlL 

WlL 

mg1L 

mg/L 

Bismuth 

7440-69-9 

5511-92 

19AUGl992 

0.00E+00 

c 

N 

mglL 

Bismuth 

7440 - 69 - 9 

619-93 O5MAY 1993 O.OOE+OO 

< 

N 

mglL 

Bismuth 

Bismuth 

Bismuth 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

7440 - 69 - 9 

7440-69-9 

7440 - 69 - 9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

744043-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

628-92 

697-92 

852-92 

1020-92 

1072-93 

1140-92 

1202-93 

1202-94 

1329-92 

1346-93 

1376-94 

1474-92 

1546-93 

1612-94 

1621-92 

17-94 

1793-92 

18-95 

1836-93 

1918-94 

1934-92 

2098-92 

2121 -94 

2152-93 

216-95 

2411-94 

2689-94 

2859-94 

286-94 

393-92 

435-95 

505-94 

O5MARl 992 

12MAR1992 

01APR1992 

04MAY1992 

16JUL1993 

01JUN1992 

05AUG1993 

O5MAY 1994 

06JULl992 

02SEP1993 

03JUN1994 

03AUG1992 

050CT1993 

01 JUL1994 

3IAUG1992 

osJAN1994 

070CT1992 

05JANI 995 

04NOV1993 

05AUGl994 

03NOV1992 

OlDECl992 

02SEPl994 

10DEC1993 

03FEB1995 

070CT1994 

04NOV1994 

02DEC1994 

04FEBl994 

30JAN1992 

03MAR1995 

03MARI994 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+W 

O.WE+OO 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+W 

O.WE+W 

O.WE+W 

O.WE+W 

O.WE+W 

O.OOE+OO 

O.WE+OO 

O.WE+OO 

O.OOE+OO 

O.OOE+W 

O.OOE+OO 

c 

c 

c 

c 

c 

c 

c 

< 

c 

c 

< 

c 

c 

< 

c 

c 

< 

U 

c 

c 

c 

c 

c 

< 

c 

c 

c 

U 

c 

< 

U 

c 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

WlL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

WlL 

mgk 

mglL 

mglL 

WlL 

wlL 

mglL 

mglL 

mg5 

mgfl 

mglL 

WIlL 

WlL 

mglL 

mgfl 

mgfl 

mgk 

Cadmium 

7440-43-9 

5511-92 

19AUGl992 O.OOE+W 

c 

N 

mglL 

Cadmium 

7440-43-9 

619-93 05MAY1993 O.WE+W 

c 

N wfl 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

628-92 

631-95 

634-93 

697-92 

785-95 

800-93 

852-92 

899-94 

954-95 

05MARl992 

05APRl995 

05MAY1993 

12MAR1992 

03MAYl995 

02JUN1993 

01APRI992 

08APRl994 

01 JUNl995 

O.OOE+OO 

O.WE+W 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+W 

O.OOE+W 

O.OOE+OO 

O.WE+OO 

c 

U 

c 

c 

c 

c 

c 

< 

c 

N 

N 

N 

N 

N 

N 

N 

N 

N 

wlL 

mgfl 

mgk 

mglL 

wlL 

mglL 

mglL 

mglL 

mglL 

Calcium 

7440-70-2 

1020-92 04MAY 1992 

1.70E+OI 

NT wR 

Calcium 

7440-70-2 

1140-92 01 JUN1992 

2.10E+01 

N w5 

Calcium 

7440-70-2 

1329-92 06JUL1992 

2.00E+01 

N w5 

Calcium 

7440-70-2 

1474-92 03AUGl992 

2.00E+OI 

N 

mglL 

Calcium 

7440-70-2 

1621-92 31AUG1992 

1.80E+01 

N 

mglL 

Calcium 

7440-70-2 

1793-92 070CT1992 

1.60E+01 

N wk 

Calcium 

7440-70-2 

1934-92 03NOV1992 

1.80E+01 

N wk 

Calcium 

7440-70-2 

2098-92 01 DECl992 

l.JOE+Ol 

N 

m95 

Calcium 

7440-70-2 

393-92 3OJAN1992 I .25E+02 

N wR 

Calcium 

7440-70-2 

5511-92 19AUGI 992 

2.60E+01 

N wfl 

Calcium 

Calcium 

Calcium 

Calcium 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

619-93 

628-92 

697-92 

852-92 

MMAY 1993 

05MAR1992 

12MAR1992 

01 APRI 992 

l.lOE+Ol 

1.50E+01 

I .30E+Ol 

1.00E+01 

N 

N 

N 

N 

mg5 

mglL 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws



ANALWE CAS NUMBER SAMPLE ID DATE TYPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Chloride 16887-00-6 393-92 30JAN1992 WS 1.40E+01 N mg1L 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Cobalt 

Cobalt 

Cobalt 

Cobal 

Cobalt 

Cobalt 

Cobalt 

Cobalt 

Coban 

Cobalt 

Coban 

Cobal 

Cobalt 

Cobalt 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Dibromochloromethane 


Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Copper 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-484 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-484 

7440-48-4 

7440-48-4 

7440-484 

7440-484 

7440-48-4 

7440-48-4 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

124-48-1 

OXYGEN DIS 

100-41-4 

100-41-4 

10041-4 

100-41-4 

100-414 

100-41-4 

1020-92 

1072-93 

1 140-92 

1202-93 

1202-94 

1329-92 

1346-93 

1376-94 

1474-92 

1546-93 

1612-94 

162 1-92 

17-94 

18-95 

1836-93 

1918-94 

1934-92 

2098-92 

2 152-93 

241 1-94 

2689-94 

2859-94 

393-92 

1793-92 

2121-94 

286-94 

505-94 

5511-92 

619-93 

634-93 

697-92 

800-93 

852-92 

899-94 

1020-92 

1140-92 

1329-92 

1474-92 

1621 

-92 

1793-92 

1934-92 

2098-92 

393-92 

619-93 

697-92 

852-92 

1020-92 

1140-92 

1329-92 

1474-92 

1621 

-92 

1793-92 

1934-92 

393-92 

5511-92 

619-93 

628-92 

852-92 

1020-92 

393-92 

1020-92 

628-92 

5511-92 

628-92 

2098-92 

697-92 

1140-92 

1329-92 

1474-92 

1621-92 

1793-92 

MAY1992 

16JUL1993 

01JUN1992 

05AUG1993 

05MAY 1994 

06JUL1992 

02SEP1993 

03JUNl994 

03AUG1992 

050CT1993 

01 JUL1994 

31AUG1992 

05JAN1994 

070CT1992 

05JAN1995 

04NOV1993 

05AUG1994 

03NOV1992 

01DEC1992 

02SEPl994 

10DEC1993 

070CT1994 

04NOV1994 

02DECl994 

04FEB1994 

30JAN1992 

03MARl994 

19AUG 1992 

05MAY1993 

05MAR1992 

05MAY1993 

12MARl992 

02JUNl993 

01 APR1992 

08APRl994 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUGl992 

3lAUG1992 

070CT1992 

03NOV1992 

01DEC1992 

30JAN1992 

19AUGl992 

05MAY1993 

O5MARl992 

12MARl992 

01 APRl992 

WAY1992 

OlJUN1992 

06JUL1992 

03AUG1992 

3lAUG 1992 

070CT1992 

03NOV1992 

01 DEC1992 

30JAN 1992 

19AUG1992 

M Y 

1993 

05MAR1992 

12MAR1992 

01 APR1992 

Q4MAY1992 

3OJAN1992 

WAY1992 

01 JUN1992 

06JUL1992 

03AUGl992 

3lAUGl992 

070CT1992 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

0.WE+00 

0.00E+00 

0.00E+00 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.WE+W 

O.OOE+OO 

O.OOE+W 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.WE+OO 

O.OOE+OO 

O.OOE+W 

O.OOE+W 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+W 

O.WE+OO 

0.00E+00 

O.OOE+OO 

O.WE+W 

O.WE+OO 

O.WE+OO 

0.00E+00 

0.00E+W 

O.WE+W 

O.WE+OO 

O.OOE+OO 

O.OOE+W 

O.WE+OO 

O.WE+OO 

O.WE+OO 

0.00€+00 

O.WE+W 

O.OOE+W 

O.OOE+OO 

O.WE+OO 

O.WE+OO 

O.OOE+00 

O.OOE+W 

O.WE+W 

O.WE+W 

5.WE+00 

1.20€+01 

5.00E+W 

5.WE+00 

5.00E+W 

5.00€+00 

5.WE+00 

5.00E+00 

c 

< 

< 

c 

< 

< 

c 

< 

< 

c 

< 

< 

< 

c 

U 

< 

< 

< 

c 

c 

< 

< 

c 

U 

< 

< 

c 

< 

< 

c 

c 

< 

< 

< 

c 

c 

< 

< 

c 

< 

< 

< 

c 

< 

c 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

c 

< 

c 

< 

< 

c 

< 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

NT 

N 

N 

N 

N 

N 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mg1L 

mglL 

w/L 

mglL 

mglL 

mglL 

mglL 

mg1L 

mg1L 

mgn 

mg1L 

mglL 

WlL 

mglL 

mgk 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

W L 

mglL 

mglL 

ugA 

mglL 

uglL 

uglL 

ugR 

uglL 

ugk 

uglL 

Page 15 of 176




Ethylbenzene 100-41-4 1934-92 03NOV1992 WS 5.00E+00 < N ug1L 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Fluoride 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCNS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCtMS Scan 

GCMS Scan 

GCMS Scan 

GCNS Scan 

GCNS Scan 

Gamma Activity 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

100-41-4 

100-41-4 

100-41-4 

100-41-4 

100-41-4 

100-41-4 

16984-48-8 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCNS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCNS SCAN 

GCNS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GAMMA 

1258746-1 

I 2587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

I 2587-46-1 

12587 -46- 1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

I 2587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

im7-47-2 

125a7-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

2098-92 

393-92 

516-92 

628-92 

697-92 

852-92 

393-92 

1072-93 

1145-95 

1202-93 

1202-94 

1376-94 

1546-93 

1612-94 

17-94 

i a95 

1836-93 

1918-94 

21 21 -94 

2152-93 

218-95 

2411-94 

2689-94 

2859-94 

286-94 

435-95 

505-94 

631-95 

785-95 

899-94 

954-95 

393-92 

1072-93 

1145-95 

1202-93 

1202-94 

1346-93 

1376-94 

1546-93 

1612-94 

17-94 

18-95 

1836-93 

igia94 

2121-94 

2152-93 

218-95 

2411-94 

2689-94 

2859-94 

286-94 

393-92 

435-95 

505-94 

6165-92 

631-95 

785-95 

800-93 

899-94 

954-95 

1072-93 

1145-95 

1202-93 

1202-94 

1346-93 

1376-94 

1546-93 

1612-94 

17-94 

18% 

1836-93 

01DEC1992 

30JAN1992 

16FEB1992 

05MAR1992 

12MAR1992 

01 APRl992 

3OJANl992 

16JULl993 

06JUL1995 

OSAUGl993 

OJMAY 1994 

03JUN1994 

050CT1993 

01 JULl994 

05JAN1994 

O5JANl995 

04NOV1993 

05AUG1994 

02SEP1994 

10DEC1993 

03FEB1995 

070CT1994 

04NOV1994 

O2DECl 994 

04FEB1994 

O3MARl995 

03MAR1994 

05APR1995 

03MAY 1995 

08APRI 994 

OlJUNl995 

3WAN1992 

16JUL1993 

06JUL1995 

05AUG1993 

[HMAY 1994 

02SEP1993 

OUUN1994 

050CT1993 

OlJUL1994 

05JAN1994 

WAN1995 

04NOV1993 

05AUG1994 

02SEP1994 

10DEC1993 

03FEB1995 

070CT1994 

MNOV1994 

02DEC1994 

MFEB1994 

3WAN1992 

03MARl995 

OW1994 

11 NOV1992 

05APR1995 

03MAYl995 

02JUNl993 

WAPR1994 

01 JUNl995 

16JULl993 

06JULl995 

05AUGl993 

05MAYl994 

02SEP1993 

OUUNl994 

050CT1993 

OlJULl994 

WAN1994 

WAN1995 

04NOVl993 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

0.00E+00 

0.00E+00 

O.WE+OO 

1.00E+00 0.00€+00 

1.00E+00 2.00E-01 

1.00E+00 3.00E-01 


-5.00E+00 2.60E+00 

O.OOE+OO 8.00E-01 

-l.OOE+OO 5.00E-01 

l.OOE+OO 8.00E-01 

-3.OOE+00 1.90E+00 

1 .00E+00 6.00E-01 

2.00E+00 7.00E-01 

O.OOE+OO 7.00E-01 

2.00E+00 l.IOE+OO 

-l.OOE+OO 5.00E-01 

1.00E+00 6.00E-01 

1.00€+00 8.00E-01 

1.00E+00 7.00E-01 

1.00€+00 6.00E-01 

0.00€+00 5.00E-01 

-2.WE+00 

l.OOE+W 5.00E-01 

O.OOE+OO 6.00E-01 


1.00€+00 8.00E-01 

l.WE+W 8.00E-01 

-1.00E+00 O.OOE+OO 

I.WE+W 6.00E-01 

1.00E+00 7.00E-01 

5.00E+00 l.OOE+OO 

6.00E+00 1.00E+00 

6.00E+00 1.00E+00 

7.00€+00 4.00E+00 

l.lOE+Ol 2.00E+00 

9.00E+00 4.00E+00 

5.00E+00 1 .OOE+OO 

1.40E+OI 4.00E+00 

4.00E+00 l.OOE+OO 

3.WE+00 1.00E+00 

8.00E+00 1.00E+00 

< N 

c 

N 

UJ 

N 

c 

N 

< N 

< N 

N 

V 

V 

Q 

V 

V 

V 

N 

V FIELD 

V 0712- 

V 

V 

N 

V 

V 

N 

V 

V 

N 

V 

N 

V 

N 

V 

N 

V 

N 

V 

V 

V 

V 

Q 

X 

Q 

V 

V 

Q 

N 

N 

N 

N 

N 

N 

N 

N 

uglL 

uglL 

uglL 

uglL 

uglL 

ug1L 

mglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

pCVL 

pCVL 

pCVL 

pCiL 

pCiL 

pCVL 

pCilL 

pCVL 

pCVL 

pciR 

pCVL 

pCVL 

pCVL 

pCVL 

pciR 

pCVL 

pCVL 

pcik 

pciiL 

pCiL 

pCVL 

pCVL 

pCiL 

pCVL 

pCiL 

pCilL 

pCiL 

pCiL 

pCiL 

pcin 

pCVL 

pcik 

pCi 

pcik 

pCilL 

pcin 

pCi 

pCilL 

pCi 

pCi




Gross Beta 12587-47-2 1918-94 05AUG1994 WS 1.00E+01 3.00E+00 PCllL 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Hardness as CaC03 









Hardness as ChC03 









Hardness as CaCO3 







Hexavalent Chromium 






Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

CAC03HARDNES 

CACOJHARDNES 

CAC03HARDNES 

CACOJHARDNES 

CACOJHARDNES 

CAC03HARDNES 

CACOJHARDNES 

CAC03HARDNES 

CAC03HARDNES 

CACO3HARDNES 

CACOJHARDNES 

CACO3HARDNES 

CAC03HARDNES 

CACOJHARDNES 

CACOBHARDNES 

CAC03HARDNES 

CAC03HARDNES 

CAC03HARDNES 

CACOJHARDNES 

CACOBHARDNES 

CACOJHARDNES 

CACOJHARDNES 

CACOJHARDNES 

CACOJHARDNES 

CACO3HARDNES 

18540-29-9 

18540-29-9 

18540-29-9 

18540-29-9 

18540-29-9 

18540-29-9 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7 4 3 9 - 8 9 - 6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

2121 -94 

2152-93 

218-95 

2411-94 

2689-94 

2859-94 

286-94 

393-92 

435-95 

505-94 

6165-92 

631-95 

785-95 

800-93 

899-94 

954-95 

1072-93 

1202-93 

1202-94 

1346-93 

1376-94 

1546-93 

1612-94 

17-94 

18-95 

1836-93 

1918-94 

2121-94 

2152-93 

218-95 

2411-94 

2689-94 

2859-94 

286-94 

435-95 

505-94 

631-95 

785-95 

800-93 

899-94 

954-95 

18-95 

218-95 

435-95 

631-95 

785-95 

954-95 

1020-92 

1072-93 

1140-92 

1202-93 

1202-94 

1329-92 

1346-93 

1376-94 

1474-92 

1546-93 

1612-94 

1621 -92 

17-94 

1793-92 

i 8-95 

1836-93 

1918-94 

1934-92 

2098-92 

2121-94 

2152-93 

218-95 

2411-94 

2689-94 

OZSEPl994 

10DEC1993 

03FEB1995 

070CT1994 

04NOV1994 

02DEC1994 

04FEB1994 

3OJANl992 

03MAR1995 

O3MAR 1 994 

1 1 NOVl992 

05APR1995 

03MAY 1995 

02JUN1993 

08APRl994 

01JUN1995 

16JUL1993 

05AUG1993 

05MAY 1994 

02SEP1993 

03JUN1994 

050CT1993 

OlJULl994 

OSJANI 994 

05JANl995 

04NOV1993 

05AUG1994 

02SEP1994 

10DEC1993 

03FEB1995 

070CT1994 

04NOV1994 

02DEC1994 

04FEB1994 

03MAR1995 

03MAR1994 

05APR1995 

03MAY1995 

O2JUNl 993 

08APR1994 

01JUN1995 

05JAN 1995 

03FEB1995 

03MARl995 

05APRl995 

03MAYl995 

01JUNl995 

04MAY1992 

16JUL1993 

01 JUN1992 

OSAUGl993 

(HMAY 1994 

06JUL1992 

02SEP1993 

OUUNl994 

03AUG1992 

050CT1993 

OlJUL1994 

3lAUGl992 

05JAN1994 

070CT1992 

WAN1 995 

04NOV1993 

05AUGl994 

03NOV1992 

01DEC1992 

02SEP1994 

10DEC1993 

03FEB1995 

070CT1994 

04NOV1994 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

9.00E+00 2.00E+00 


2.00E+00 l.OOE+OO 

7.00E+00 2.00E+00 

5.00E+00 1.00E+00 


3.00E+00 l.OOE+OO 

-l.OOE+OO 

2.00E+00 l.OOE+OO 

5.00E+00 2.00E+00 

l.OOE+OO 

2.00E+00 O.OOE+OO 

3.00E+00 1 .OOE+OO 

2.00E+00 O.OOE+OO 

6.00E+00 2.00E+00 

2.00E+00 O.OOE+OO 

7.50E+01 

8.00E+01 

5.00E+01 

8.60E+01 

6.60E+01 


6.60E+01 

5.20E+01 

6.20E+01 

5.60E+01 

6.20E+01 

6.20E+01 



6.80E+01 

7.20E+01 

5.60E+01 

5.20E+01 

5.60E+01 

5.20E+01 

5.20E+01 

3.80E+01 

7.70E+01 



O.WE+OO 

O.OOE+W 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.OOE+OO 

O.WE+OO 

O.OOE+OO 

l.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.OOE+OO 

O.WE+OO 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+W 

0.00E+00 

O.WE+OO 

O.WE+W 

O.WE+OO 

O.WE+OO 

l.WE+W 

l.WE+W 

O.WE+W 

O.OOE+OO 

< 

< 

< 

N 

N 

N 

N 

N 

N 

X 

X 

X 

X 

N 

X 

X 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

pCilL 

pCilL 

pCi/L 

pCilL 

pCilL 

pCVL 

pCilL 

pCilL 

pCVL 

pCilL 

pCilL 

pCilL 

pCiL 

pCilL 

pCilL 

pCilL 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mglL CaCO3 

mglL CaCO3 

mglL CaCO3 

mglL CaC03 

mglL CaC03 

mglL CaCO3 

mglL CaCO3 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mglL CaCO3 

mglL CaC03 

mg/L CaC03 

mglL CaCO3 

mg/L CaC03 

mglL CaC03 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

WlL 

mglL 

mg/L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

WIlL 

mglL




7439-89-6 2859-94 02DEC1994 WS 0,00E+00 mglL 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Magnesium 

Magnesium 

Magnesium 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-92-1 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-95-4 

7439-95-4 

7439-954 

7439-93-2 

286-94 

393-92 

435-95 

505-94 

551 1-92 

619-93 

628-92 

631 -95 

634-93 

697-92 

785-95 

800-93 

852-92 

899-94 

1020-92 

1072-93 

11 40-92 

1202-93 

1329-92 

1346-93 

1202-94 

1376-94 

1474-92 

1546-93 

1621-92 

161 2-94 

17-94 

1793-92 

18-95 

1836-93 

1918-94 

1934-92 

2098-92 

2121-94 

2152-93 

218-95 

241 1-94 

2689-94 

2859-94 

286-94 

393-92 

435-95 

505-94 

5511-92 

619-93 

631-95 

634-93 

697-92 

800-93 

852-92 

899-94 

954-95 

1020-92 

1140-92 

1329-92 

1474-92 

1621 

-92 

1793-92 

1934-92 

2098-92 

393-92 

619-93 

628-92 

785-95 

5511-92 

628-92 

697-92 

852-92 

1020-92 

1072-93 

1 140-92 

04FEB1994 

3OJANl992 

O3MAR1995 

03MARl994 

19AUG1992 

05MAY 1993 

05MAR1992 

05APR1995 

05MAY 1993 

12MAR1992 

03MAYl995 

02JUN1993 

01 APRl992 

08APR1994 

04MAY 1992 

16JULl993 

01JUN1992 

OSAUG1993 

05MAY1994 

06JUL1992 

02SEP1993 

03JUNl994 

03AUG1992 

050CTl993 

01 JULl994 

31AUGl992 

05JAN1994 

070CT1992 

05JAN1995 

MNOV1993 

OSAUG1994 

03NOVl992 

01DEC1992 

02SEPl994 

lODECl993 

03FEB1995 

070CT1994 

MNOV1994 

02DEC1994 

MFEB1994 

30JAN1992 

03MARl995 

03MAR1994 

19AUGl992 

osMAY1993 

osMAR1992 

05APR1995 

05MAY1993 

lZMARl992 

03MAYl995 

02JUN1993 

01APRl992 

08APR1994 

01JUN1995 

04MAY 1992 

01JUN1992 

06JULl992 

03AUGl992 

31AUG1992 

070CT1992 

03NOV1992 

OlDECl992 

WAN 1 992 

19AUGl992 

05MAY1993 

05MAR1992 

12MAR1992 

OlAPR1992 

04MAY1992 

16JULl993 

01JUNl992 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

l.OOE+OO 

2.41 E+02 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

l.OOE+OO 

O.OOE+OO 

O.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

O.OOE+OO 

1.00E+00 

l.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

0.00E+00 

O.WE+OO 

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0.00€+00 

0.00E+00 

0.00E+00 

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O.WE+OO 

0.00E+00 

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O.OOE+W 

0.00E+00 

O.WE+W 

O.OOE+W 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+W 

0.00E+00 

O.OOE+W 

O.WE+OO 

0.00E+00 

O.WE+OO 

O.OOE+OO 

0.00E+00 

0.00E+00 

O.M)E+OO 

O.WE+W 

O.M)E+OO 

0.00E+W 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+W 

O.WE+W 

0.00E+W 

O.WE+W 

0.00E+00 

0.00E+00 

O.OOE+OO 

0.00E+00 

0.00E+00 

O.OOE+OO 

0.00E+00 

0.00E+00 

O.WE+W 

O.WE+OO 

0.00E+00 

3.00€+00 



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N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

m& 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mgfl 

mgfl 

mglL 

mgfl 

mgfl 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mgfl 

mgfl 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mgfl 

mglL 

mgfl 

mglL 

mgfl 

mgfl 

mgfl 

mgfl 

mgfl 

mgfl 

mgfl 

mgfl 

mglL 

mgfl 

msR 

mgfl 

Page 18 of 176



ANALYlE CAS NUMBER SAMPLE ID DATE TYPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Magnesium 7439-95-4 1202-93 OSAUG1993 WS 4.00E+00 N 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7 4 3 9 - 9 5 -4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7 4 3 9 - 95 -4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7 4 3 9 - 96 - 5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

1202-94 

1329-92 

1346-93 

1376-94 

1474-92 

1546-93 

1612-94 

1621-92 

17-94 

1793-92 

18-95 

1836-93 

1918-94 

1934-92 

2098-92 

21 21 -94 

2152-93 

218-95 

2411-94 

2689-94 

2859-94 

286-94 

393-92 

435-95 

505-94 

5511-92 

619-93 

628-92 

631-95 

634-93 

697-92 

785-95 

800-93 

852-92 

899-94 

1020-92 

1072-93 

1140-92 

1202-93 

1202-94 

1329-92 

1346-93 

1376-94 

1474-92 

1546-93 

1612-94 

1621-92 

17-94 

1793-92 

1 a95 

1836-93 

1918-94 

1934-92 

2098-92 

2121-94 

2152-93 

21895 

2421-94 

2689-94 

2859-94 

286-94 

393-92 

435-95 

505-94 

5511-92 

619-93 

62892 

631-95 

634-93 

697-92 

785-95 

OSMAY 1994 

06JUL1992 

02SEP1993 

03JUN1994 

03AUG1992 

050CT1993 

01 JUL1994 

31AUG1992 

O5JAN 1994 

070CT1992 

05JAN1995 

04NOV1993 

OSAUGI 994 

03NOV1992 

01DEC1992 

02SEPl994 

10DEC1993 

03FEBl995 

070CT1994 

04NOV1994 

02DECl994 

04FEB1994 

30JAN1992 

03MARl995 

03MAR1994 

19AUGl992 

05MAY1993 

05MAR1992 

05APR1995 

O5MAY 1993 

12MARl992 

03MAY 1995 

02JUN1993 

01 APRI 992 

08APR1994 

04MAY 1992 

16JULl993 

01JUN1992 

05AUG 1993 

05MAYI 994 

oGJUL1992 

02SEP1993 

03JUNl994 

03AUG1992 

050CT1993 

01 JULl994 

31AUG1992 

05JAN1994 

070CT1992 

%JAN1995 

04NOV1993 

OSAUG1994 

03NOV1992 

01 DEC1992 

02SEP1994 

10DEC1993 

03FEB1995 

070CT1994 

04NOV1994 

02DEC1994 

04FEB1994 

3OJANl992 

03MAR1995 

03MARl994 

19AUGl992 

05MAY1993 

05MAR1992 

05APRI995 

05MAY 1993 

12MAR1992 

03MAY 1995 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

3.OOE+00 





3.00E+00 



3.00E+00 

3.00E+00 



3.00E+00 


3.00E+00 


3.00E+00 

3.00E+00 


4.00E+OO 


3.00E+00 

6.90E+01 

3.00E+00 

3.00E+00 

5.00E+00 

3.00E+00 

3.OOE+00 


3.OOE+00 

3.00E+00 

3.OOE+00 

4.00E+W 

2.WE+W 

3.OOE+00 

O.WE+W 

O.OOE+OO 

O.OOE+W 

O.OOE+W 

O.OOE+OO 

O.OOE+OO 

1.00E+00 

O.OOE+OO 

O.WE+W 

O.WE+OO 

O.WE+OO 

O.OOE+W 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+W 

O.OOE+OO 

O.WE+OO 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.WE+OO 

O.OOE+W 

O.OOE+OO 

3.70E+O 1 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+W 

O.WE+W 

O.WE+W 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mgfl 

mg1L 

mg1L 

mglL 

mg/L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mg1L 

mglL 

WlL 

mglL 

mglL 

mgfl 

mgfl 

mglL 

mglL 

mglL 

mgfl 

mgfl 

mglL 

mglL 

mgfl 

mgfl 

mglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mgfl 

mglL 

WlL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL




Manganese 7439-96-5 800-93 02JUN1993 WS O.OOE+OO N mglL 

Manganese 

Manganese 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 


Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

75-09-2 

7439-98-7 

7439-98-7 

7439-98-7 

7439-97-6 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-90-7 

7439-98-7 

7439-98-7 

7439-98-7 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

852-92 

899-94 

1140-92 

1329-92 

1474-92 

1546-93 

1621 -92 

1793-92 

1934-92 

2098-92 

393-92 

551 1-92 

619-93 

697-92 

852-92 

1020-92 

1 140-92 

1329-92 

1474-92 

162 1-92 

1793-92 

2098-92 

393-92 

5511-92 

619-93 

697-92 

852-92 

1020-92 

1072-93 

1140-92 

1202-93 

1020-92 

628-92 

1346-93 

1934-92 

628-92 

1202-94 

1329-92 

1346-93 

1376-94 

1474-92 

1546-93 

1612-94 

1621-92 

17-94 

1793-92 

18-95 

1836-93 

1934-92 

2098-92 

2121-94 

2152-93 

241 1-94 

2689-94 

1918-94 

218-95 

2859-94 

286-94 

393-92 

435-95 

505-94 

551 1-92 

619-93 

631-95 

634-93 

697-92 

785-95 

800-93 

852-92 

899-94 

628-92 

01 APRl992 

08APR1994 

04MAY 1992 

OlJUN1992 

06JULl992 

03AUG1992 

050CT1993 

31AUG1992 

070CT1992 

03NOV1992 

01 DECl992 

30JAN1992 

19AUG1992 

OWAY 1993 

0WAR1992 

12MARl992 

01APR1992 

02SEP1993 

04MAY1992 

01JUN1992 

06JULl992 

03AUG1992 

31 AUGl992 

070CT1992 

03NOV1992 

01 DEC1992 

30JAN1992 

19AUG1992 

05MAY 1993 

OSMAR 1992 

12MAR1992 

01 APR1992 

04MAY 1992 

16JULl993 

01JUN1992 

05AUGl993 

WAY 

1994 

06JUL1992 

O2SEP1993 

03JUN1994 

03AUGl992 

050CTl993 

OlJULl994 

3lAUGl992 

WAN1 994 

070CT1992 

05JANl995 

04NOV1993 

05AUG1994 

03NOV1992 

01 DEC1992 

02SEP1994 

lODEC1993 

03FEB1995 

070CT1994 

04NOV1994 

02DECl994 

04FEBl994 

3OJANl992 

03MARl995 

O3MARl994 

19AUGl992 

OSMAY1993 

OSMAR1992 

05APR1995 

OSMAY 1993 

12MARl992 

03MAY 1995 

02JUN1993 

01APR1992 

08APRl994 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

3.00E+00 

O.OOE+OO 

O.OOE+OO 

O.WE+W 

O.OOE+OO 

O.OOE+W 

O.OOE+OO 

O.WE+OO 

O.WE+W 

O.WE+OO 

O.OOE+W 

O.OOE+OO 

O.OOE+W 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.WE+W 

O.OOE+OO 

O.WE+W 

O.WE+OO 

O.WE+OO 

O.WE+OO 

0 .OOE+ 00 

O.WE+OO 

O.OOE+W 

O.WE+OO 

0.00E+00 

O.WE+OO 

O.WE+W 

O.OOE+W 

5.WE+W 

O.WE+W 

O.OOE+OO 

O.WE+OO 

O.WE+W 

O.WE+W 

O.WE+W 

O.WE+W 

O.WE+OO 

O.WE+W 

O.OOE+W 

O.WE+W 

O.WE+W 

0.00E+W 

O.WE+W 

0.00E+W 

O.WE+OO 

O.OOE+OO 

O.WE+W 

O.WE+W 

O.WE+W 

< 

< 

< 

< 

< 

< 

C 

C 

< 

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UJ 

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< 

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< 

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< 

< 

< 

< 

< 

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< 

< 

< 

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< 

< 

< 

< 

< 

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< 

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UJ 

< 

< 

< 

< 

< 

< 

< 

< 

< 

e 

< 

< 

< 

e 

e 

e 

< 

c 

< 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Page 20 of 176




Niobium 7440-03-1 1020-92 04MAYl992 WS 0.00€+00 C NT mg1L 

Niobium 

7440-03-1 

1140-92 

01JUN1992 ws 

C 

N 

mglL 

Niobium 

7440-03-1 

1329-92 06JUL1992 ws 

< N 

mglL 

Niobium 

7440-03-1 

1474-92 03AUG1992 ws 

< N 

mglL 

Niobium 

7440-03-1 

1621 -92 31AUG1992 ws 

c 

N 

mglL 

Niobium 

7440-03-1 

1793-92 070CT1992 ws 

< N 

mglL 

Niobium 

7440-03-1 

1934-92 03NOV1992 ws 

< N 

mglL 

Niobium 

7440-03-1 

2098-92 01 DECl992 ws 

C 

N 

mglL 

Niobium 

7440-03-1 

393-92 30JANI 992 ws 

< N 

mglL 

Niobium 

7440-03-1 

5511-92 19AUG1992 ws 

< N 

mg1L 

Niobium 

7440-03-1 

619-93 05MAY1993 ws 

< N 

mglL 

Niobium 

7440-03-1 

628-92 OSMAR1992 ws 

C 

N 

mglL 

Niobium 

7440-03-1 

697-92 12MARl992 ws 

< N 

mglL 

Niobium 

7440-03-1 

852-92 OlAPR1992 ws 

< N 

mglL 


N ITRATEAS N IT 

393-92 3OJAN1992 ws 

C 

N 

mglL 

Oil and Grease 

SO227 

393-92 30JAN1992 ws 

< N 

mglL 

PCB 

1336-36-3 

17-94 05JANl994 ws 

< N 

uglL 

PCB 

1336-36-3 

1860-92 190CT1992 ws 

C 

N 

uglL 

PCB 

1336-36-3 

1934-92 03NOV1992 ws 

< N 

uglL 

PCB 

1336-36-3 

393-92 3OJAN 1992 ws 

< N 

uglL 

Phosphorus (P) 

7723-14-0 

1020-92 04MAY 1992 ws 

< NT mglL 


7723-14-0 

1140-92 

01 JUN1992 ws 

C 

N 

mglL 


7723-14-0 

1329-92 06JUL1992 ws 

C 

N 

mglL 


7723-14-0 

1474-92 03AUG1992 ws 

< N 

mglL 


7723-14-0 

1621-92 31 AUG 1992 ws 

N 

mgn 


7723-14-0 

1793-92 07OCT1992 ws 

C 

N 

mglL 


7723-14-0 

193492 03NOVI 992 ws 

C 

N 

mglL 


7723-14-0 

2098-92 OlDEC1992 ws 

N 

mglL 


7723-14-0 

393-92 3OJAN1992 ws 

< N 

mglL 


7723-14-0 

5511-92 

19AUGl992 ws 

C 

N 

mglL 


7723-14-0 

619-93 05MAY1993 ws 

< N 

mglL 


7723-14-0 

628-92 osMAR1992 ws 

< N 

mg1L 


7723-14-0 

697-92 12MAR1992 ws 

< N 

mglL 


7723-14-0 

852-92 01APR1992 ws 

C 

N 

mgk 

Potassium 

7440-09-7 

1020-92 04MAY1992 ws 

NT mglL 

Potassium 

7440-09-7 

1072-93 16JUL1993 ws 

N 

mglL 

Potassium 

7440-09-7 

I1 40-92 01 JUN1992 ws 

N 

mglL 

Potassium 

7440-09-7 

1202-93 05AUGl993 ws 

N 

mglL 

Potassium 

7440-09-7 

1202-94 OSMAY 1994 ws 

< 

N 

mgk 

Potassium 

7440-09-7 

1329-92 06JUL1992 ws 

N 

mglL 

Potassium 

7440-09-7 

1346-93 02SEPl993 ws 

N 

mglL 

Potassium 

7440-09-7 

1376-94 03JUN1994 ws 

N 

mglL 

Potassium 

7440-09-7 

147492 03AUGl992 ws 

N 

mglL 

Potassium 

7440-09-7 

1546-93 050CT1993 ws 

N 

mglL 

Potassium 

7440-09-7 

1612-94 OlJULl994 ws 

N 

mglL 

Potassium 

7440-09-7 

1621-92 3lAUGl992 ws 

N 

mgn 

Potassium 

7440-09-7 

17-94 05JAN1994 ws 

C 

N 

mglL 

Potassium 

7440-09-7 

1793-92 070CTI 992 ws 

N 

mgk 

Potassium 

7440-09-7 

18-95 05JAN1995 ws 

N 

mg1L 

Potassium 

7440-09-7 

1836-93 04NOV1993 ws 

N 

mglL 

Potassium 

7440-09-7 

1918-94 OSAUG1994 ws 

N 

mg1L 

Potassium 

7440-09-7 

1934-92 03NOV1992 ws 

N 

mglL 

Potassium 

7440-09-7 

2098-92 01 DEC1992 ws 

J 

N 

mglL 

Potassium 

7440-09-7 

2121 -94 02SEP1994 ws 

N 

mglL 

Potassium 

7440-09-7 

2152-93 1 ODECl993 ws 

< 

N 

mglL 

Potassium 

7440-09-7 , 218-95 03FEB1995 ws 

N 

mglL 

Potassium 

7440-09-7 

2411-94 

070CT1994 ws 

N 

mglL 

Potassium 

7440-09-7 

2689-94 04NOV1994 ws 

N 

mglL 

Potassium 

7440-09-7 

2859-94 02DEC1994 ws 

N 

WlL 

Potassium 

7440-09-7 

286-94 04FEB1994 ws 

< 

N 

mglL 

Potassium 

7440-09-7 

393-92 3OJAN1992 ws 

N 

WlL 

Potassium 

7440-09-7 

435-95 03MAR1995 ws 

N 

mg/L 

Potassium 

7440-09-7 

505-94 03MAR1994 ws 

C 

N 

mglL 

Potassium 

7440-09-7 

5511-92 

19AUGl992 ws 

N 

mglL 

Potassium 

7440-09-7 

619-93 05MAY1993 ws 

N 

mglL 

Potassium 

7440-09-7 

628-92 05MAR1992 ws 

N 

mglL 

Potassium 

7440-09-7 

631-95 05APR1995 ws 

N 

mglL 

Potassium 

7440-09-7 

634-93 OWAY 1993 ws 

N 

mglL 

Potassium 

7440-09-7 

697-92 12MAR1992 ws 

N 

mgk 

Potassium 

7440-09-7 

785-95 03MAY 1995 ws 

N 

WlL 

Potassium 

7440-09-7 

800-93 02JUN1993 ws 

N 

WlL 

Potassium 

7440-09-7 

852-92 01 APR1992 ws 

< 

N 

WlL 

Page 21 of 176




Potassium 7440-09-7 899-94 00APR1994 WS 2.00E+00 < N malL 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Beta 

Rad Beta 

Rad Beta 

Rad Beta 

Rad Beta 

Rad Beta 

Rad Beta 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Selenium 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Sileon 

Silicon 

Sillcon 

Sikon 

Sillcon 

Sillcon 

Silicon 

Sillcon 

Silicon 

Silicon 

Silmn 

Silicon 

Silicon 

Silicon 

S ilicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Sillcon 

Silicon 

Silicon 

Silver 

Silver 

Silver 

12587-46-1 

12507-46-1 

12507-46-1 

12507-46-1 

12507-46-1 

12587-46-1 

12507-46-1 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

7440-10-8 

7440-10-0 

7440- 10-0 

7440-10-8 

7440-10-0 

7440-18-8 

7440-10-8 

7440-10-0 

7440-10-0 

7440-10-0 

7440-10-0 

7440-18-0 

7440-18-8 

7440-18-8 

7702-49-2 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-22-4 

7440-22-4 

7440-22-4 

1145-95 

210-95 

435-95 

631 -95 

705-95 

800-93 

954-95 

1145-95 

218-95 

435-95 

631-95 

785-95 

800-93 

954-95 

1020-92 

1140-92 

1329-92 

1474-92 

1621-92 

1793-92 

1934-92 

2098-92 

393-92 

5511-92 

619-93 

620-92 

697-92 

852-92 

393-92 

1020-92 

1072-93 

1140-92 

1202-93 

1202-94 

1329-92 

1346-93 

1376-94 

1474-92 

1546-93 

1612-94 

1621 -92 

17-94 

1793-92 

18-95 

1836-93 

igiaw 

1934-92 

2098-92 

21 21 -94 

2152-93 

218-95 

2411-94 

2689-94 

2859-94 

286-94 

393-92 

435-95 

505-94 

5511-92 

619-93 

628-92 

631-95 

634-93 

697-92 

785-95 

800-93 

852-92 

899-94 

1020-92 

1140-92 

1329-92 

06JUL1995 

03FEB1995 

03MARl995 

05APRl995 

03MAY 1995 

02 JUNl993 

01JUN1995 

06JUL1995 

03FEB1995 

03MAR1995 

05APR1995 

03MAY 1995 

OZJUN1993 

01JUN1995 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUG1992 

3lAUGl992 

070CT1992 

03NOV1992 

01DEC1992 

3OJANl992 

19AUG1992 

05MAYl993 

05MAR1992 

12MAR1992 

01APR1992 

3OJAN1992 

04MAY 1992 

16JUL1993 

01 JUN1992 

05AUG1993 

05MAY 1994 

06JUL1992 

02SEP1993 

03JUN1994 

O3AUG 1992 

050CT1993 

01 JUL1994 

3lAUGl992 

05JAN1994 

070CT1992 

05JANl995 

04NOV1993 

05AUGl994 

03NOV1992 

01 DEC1992 

02SEPl994 

10DEC1993 

03FEB1995 

070CT1994 

04NOVl994 

02DECl994 

04FEBl994 

3OJAN1992 

ow1995 

03MAR1994 

19AUGl992 

05MAY1993 

05MARl992 

OSAPR 1995 

05MAY 1993 

12MAR1992 

03MAY 1 995 

02JUNl993 

01APR1992 

00APRl994 

04MAY1992 

OlJUNl992 

06JUL1992 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

c 

N 

< N 

< N 

< N 

< NT 

c 

N 

< N 

< N 

< N 

< N 

< N 

< N 

c 

N 

< N 

< N 

< N 

< N 

.z N 

< N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

< 

X 

J 

J 

J 

B 

J 

< 

< 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N




Silver 7440-22-4 1474-92 03AUG1992 WS O.OOE+OO < N mg1L 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 






Specifl conductance 








Specib conductance 









7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

1621 -92 

1793-92 

1934-92 

2098-92 

393-92 

5511-92 

619-93 

628-92 

697-92 

852-92 

1020-92 

1072-93 

1140-92 

1202-93 

1202-94 

1329-92 

1346-93 

1376-94 

1474-92 

1546-93 

1612-94 

1621-92 

17-94 

1793-92 

18-95 

1836-93 

1918-94 

1934-92 

2098-92 

21 21 -94 

2152-93 

218-95 

2411-94 

2689-94 

2859-94 

286-94 

393-92 

435-95 

505-94 

5511-92 

619-93 

628-92 

631-95 

634-93 

697-92 

785-95 

800-93 

852-92 

899-94 

1072-93 

1145-95 

1202-93 

1202-94 

1346-93 

1376-94 

1546-93 

1612-94 

17-94 

18-95 

1836-93 

1918-94 

2121-94 

2152-93 

218-95 

2411-94 

2689-94 

2859-94 

286-94 

435-95 

505-94 

631-95 

3lAUGl992 

070CT1992 

03NOV1992 

01DEC1992 

3OJANl992 

19AUG 1992 

OSMAY 1993 

O5MAR 1992 

1 ZMAR1992 

01 APRl992 

MMAY 1992 

16JUL1993 

01 JUNl992 

05AUG1993 

OSMAY 1994 

06JUL1992 

02SEP1993 

03JUN1994 

03AUG1992 

050CT1993 

OlJULl994 

3lAUGl992 

05JAN1994 

07OCT1992 

OSJAN1995 

04NOV1993 

05AUG1994 

03NOV1992 

OlDEC1992 

02SEP1994 

10DEC1993 

03FEBl995 

070CT1994 

04NOVl994 

02DECl994 

04FEB1994 

30JAN1992 

O3MAR 1995 

03MARl994 

19AUG1992 

WAY 1993 

05MAR1992 

OSAPR1995 

05MAY1993 

I ZMAR 1992 

03MAY1995 

OZJUNl993 

01 APRI 992 

O8APR 1994 

16JULl993 

06JUL1995 

OSAUG1993 

OSMAY 1994 

02SEP1993 

03JUNl994 

050CT1993 

01 JUL1994 

WAN1994 

WAN1995 

04NOV1993 

OSAUG1994 

02SEP1994 

lODEC1993 

03FEBl995 

070CT1994 

04NOV1994 

02DEC1994 

04FEB1994 

03MAR1995 

03MAR1994 

OSAPRl995 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

1.80E+01 

1.50E+01 

2.50E+01 

1.80€+01 

l.lOE+01 

3.20E+01 

2.30E+01 

2.10E+01 

2.1 OE+01 

1.00E+01 

2.50E+01 

1.80E+01 

1.70E+01 

1.40E+01 

2.70E+01 

2.3OE+01 

2.50E+01 

2.20E+01 

1.50E+01 

2.40E+01 

1.00E+01 

l.ZOE+Ol 

3.00E+01 

2.70E+01 

1.50E+01 

1.20E+01 

5.00E+01 

1,40E+01 

l.lOE+Ol 

3.40E+01 

6.00E+00 

1.7OE+OI 

2.10E+01 

6.00€+00 

1.30E+01 

8.00E+W 

1.80E+01 

8.00E+00 

8.00E+00 

2.17E+02 

1.22E+02 

2.44E+02 

I .65E+02 

2.72E+02 

2.45E+02 

1.70E+02 

2.41E+02 

2.01E+02 

2.74E+02 

2.38E+02 

2.62E+02 

2.7 1 E+02 

1.48€+02 

1.63E+02 

3.10E+02 

2.81€+02 

1.98E+02 

1.69€+02 

1.77E+02 

1.66€+02 

2.18E+02 

< N 

< N 

< N 

< N 

< N 

< N 

C 

N 

< N 

< N 

< N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

J 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

B 

N 

N 

N 

J 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mg/L 

mglL 

mglL 

mg1L 

mg1L 

mglL 

mglL 

mglL 

mglL 

mg1L 

mg1L 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

WlL 

mglL 

mg/L 

mglL 

mglL 

msn. 

mglL 

mglL 

mglL 

m9R 

WlL 

mglL 

mgR 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mg/L 

mglL 

mglL 

mg/L 

umhodcm 

umhodcm 

umhoslcm 

umhodcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhodcm 

umhoslcrn 

umhodcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhodcm 

umhodcm 

umhodcm 

umhoslcm 

umhoslcm 

umhodcm 

umhodcm 

umhoslcm 

umhodcm




Specific conductance SO145 785-95 03MAY1995 WS 1.23E+02 N umhoslcm 




Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Sulfate 

Sulfate 

Sulfate 

Sulfate 

Sulfate 

TOX 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Technetium-99 

Technetium99 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

SO145 

SO145 

SO145 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

12143-45-2 

12143-45-2 

12143-45-2 

12143-45-2 

12143-45-2 

TOX. 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

14133-76-7 

14133-76-7 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

800-93 

899-94 

954-95 

1020-92 

1072-93 

1140-92 

1202-93 

1202-94 

1329-92 

1346-93 

1376-94 

1474-92 

1546-93 

1612-94 

1621 -92 

17-94 

1793-92 

18-95 

1836-93 

1918-94 

1934-92 

2098-92 

21 21 -94 

2152-93 

21a-95 

2411-94 

2689-94 

2859-94 

286-94 

393-92 

435-95 

505-94 

5511-92 

619-93 

626-92 

631-95 

634-93 

697-92 

785-95 

800-93 

852-92 

899-94 

1140-92 

1329-92 

1474-92 

1621-92 

393-92 

393-92 

1020-92 

1140-92 

1329-92 

1474-92 

1621-92 

1793-92 

1934-92 

393-92 

5511-92 

619-93 

628-92 

697-92 

852-92 

393-92 

6165-92 

1020-92 

1140-92 

1329-92 

1474-92 

1621-92 

1793-92 

1934-92 

2098-92 

02JUN1993 

08APR1994 

01JUN1995 

04MAY 1992 

26JUL1993 

01JUN1992 

05AUG1993 

05MAY 1994 

06JULl992 

02SEP1993 

OUUN1994 

03AUG 1992 

050CT1993 

OlJUL1994 

31AUG1992 

05JANl994 

070CT1992 

05JAN1995 

04NOV1993 

05AUG1994 

03NOV1992 

01 DECI 992 

02SEP1994 

10DEC1993 

03FEB1995 

070CT1994 

04NOV1994 

O2DECl994 

04FEB1994 

3OJAN1992 

03MARI 995 

03MARl994 

19AUG1992 

05MAY 1993 

05MARl992 

OSAPR1995 

OSMAY 1993 

12MARl992 

03MAY1995 

O2JUN 1993 

OlAPR1992 

08APRl994 

01 JUNl992 

06JUL1992 

03AUG1992 

31AUG1992 

3OJAN1992 

3OJAN1992 

04MAY1992 

OlJUN1992 

06JUL1992 

03AUG1992 

31 AUGI 992 

070CT1992 

03NOV1992 

30JAN1992 

19AUG1992 

05MAY 1993 

05MAR1992 

12MAR1992 

01APR1992 

3OJAN1992 

1 I NOVI 992 

04MAY 1992 

01 JUN1992 

06JUL1992 

03AUG1992 

3lAUGl992 

070CT1992 

03NOV1992 

01DECl992 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N




Thallium 7440-28-0 393-92 3OJAN1992 WS O.OOE+OO N 

mg1L 

Thallium , 

7440-28-0 

5511-92 19AUG1992 ws 

N 

mg1L 

Thallium 

7440-28-0 

619-93 

05MAY 1993 ws 

N 

mglL 

Thallium 

7440-28-0 

628-92 05MARl992 ws 

N 

mglL 

Thallium 

7440-28-0 

697-92 12MAR1992 ws 

N 

mglL 

Thallium 

7440-28-0 

852-92 01APRl992 ws 

N 

mglL 

Thorium 

7440-29-1 

1020-92 04MAY1992 ws 

NT mg1L 

Thorium 

7440-29-1 

1140-92 01JUN1992 ws 

N 

mglL 

Thorium 

7440-29-1 

1329-92 06JUL1992 ws 

N 

mglL 

Thorium 

7440-29-1 

1474-92 03AUG1992 ws 

N 

mglL 

Thorium 

7440-29-1 

1621 -92 31 AUG 1992 ws 

N 

mglL 

Thorium 

7440-29-1 

1793-92 070CT1992 ws 

N 

mglL 

Thorium 

7440-29-1 

1934-92 03NOVl 992 ws 

N 

mg1L 

Thorium 

7440-29-1 

2098-92 01 DEC1992 ws 

N 

mglL 

Thorium 

7440-29-1 

393-92 3OJANl992 ws 

N 

mglL 

Thorium 

7440-29-1 

5511-92 

19AUG1992 ws 

N 

mglL 

Thorium 

7440-29-1 

619-93 05MAY1993 ws 

N 

mglL 

Thorium 

7440-29-1 

628-92 05MAR1992 ws 

N 

mglL 

Thorium 

7440-29-1 

697-92 12MAR1992 ws 

N 

mglL 

Thorium 

7440-29-1 

852-92 01 APRl992 ws 

N 

mglL 

Tin 

7440-31-5 

1020-92 04MAY1992 ws 

NT mg/L 

Tin 

7440-31 -5 

1140-92 01JUN1992 ws 

N 

mglL 

Tin 

7440-31-5 

1329-92 06JUL1992 ws 

N 

mglL 

Tin 

7440-31-5 

1474-92 03AUG1992 ws 

N 

mglL 

Tin 

7440-31-5 

1621-92 31AUGl992 ws 

N 

mglL 

Tin 

7440-31-5 

1793-92 070CT1992 ws 

N 

mglL 

Tin 

7440-31-5 

1934-92 03NOV1992 ws 

N 

mglL 

Tin 

7440-31-5 

2098-92 01DEC1992 ws 

N 

mglL 

Tin 

7440-31-5 

393-92 30JAN1992 ws 

N 

mglL 

Tin 

7440-31 -5 

5511-92 

19AUG1992 ws 

N 

Tin 

7440-31 -5 

619-93 05MAY 1993 ws 

N 

mgk 

Tin 

7440-31-5 

628-92 05MAR1992 ws 

N 

mg1L 

Tin 

7440-31-5 

697-92 12MAR1992 ws 

N 

mglL 

Tin 

7440-31-5 

852-92 01 APRI 992 ws 

N 

mglL 

Titanium 

7440-32-6 

1020-92 04MAY1992 ws 

NT WlL 

Titanium 

7440-32-6 

1140-92 OlJUN1992 ws 

N 

mglL 

Titanium 

7440-32-6 

1329-92 06JUL1992 ws 

N 

mglL 

Titanium 

7440-32-6 

1474-92 03AUG 1992 ws 

N 

mglL 

Titanium 

7440-32-6 

1621-92 

31AUG1992 ws 

N 

mg1L 

Titanium 

7440-32-6 

1793-92 070CT1992 ws 

N 

mglL 

Titanium 

7440-32-6 

1934-92 03NOV1992 ws 

N 

mglL 

Titanium 

7440-32-6 

2098-92 01DECl992 ws 

N 

rnglL 

Titanium 

7440-32-6 

393-92 3OJANl992 ws 

N 

mglL 

Titanium 

7440-32-6 

5511-92 

19AUGl992 ws 

N 

mglL 

Titanium 

7440-32-6 

619-93 

05MAY1993 ws 

N 

mglL 

Titanium 

7440-32-6 

628-92 05MAR1992 ws 

N 

mglL 

Titanium 

7440-32-6 

697-92 12MAR1992 ws 

N 

mglL 

Titanium 

7440-32-6 

852-92 01 APRl992 ws 

N 

mglL 

Toluene 

108-88-3 

1020-92 WAY1992 ws 

NT 

uglL 

Toluene 

108-88-3 

1140-92 01JUN1992 ws 

N 

ug/L 

Toluene I 08-88-3 

1329-92 06JUL1992 ws 

N 

uglL 


1474-92 03AUG1992 ws 

N 

uglL 

Toluene 

108-88-3 

1621-92 31AUG1992 ws 

N 

uglL 


1793-92 070CT1992 ws 

N 

uglL 

Toluene 

108-88-3 

1934-92 03NOV1992 ws 

N 

ugR 


2098-92 01 DECl992 ws 

N 

uglL 

Toluene 

108-88-3 

393-92 30JAN1992 ws 

N 

uglL 

Toluene 

108-88-3 

516-92 16FEB1992 ws 

N 

uglL 

Toluene 

ioaaa-3 

628-92 O5MARl 992 ws 

N 

uglL 


697-92 12MAR1992 ws 

N 

uglL 

Toluene 

ioa-88-3 

852-92 01 APRI 992 ws 

N 

uglL 

Total Organic Carbon 7440-44-0 

393-92 3OJAN1992 ws 

N 

mglL 

Trans-I .2-Dichloroethene 156-60-5 

1140-92 OlJUN1992 ws 

N 

uglL 

Trans-I .2-Dichloroethene 15660-5 

1329-92 06JULI 992 ws 

N 

uglL 


1474-92 03AUGl992 ws 

N 

uglL 

Trans-I ,2-Dichloroethene 15660-5 

1621-92 3lAUG1992 ws 

N 

uglL 


1793-92 07OCT1992 ws 

N 

uglL 


1934-92 03NOV1992 ws 

N 

uglL 


mga-92 01 DEC1992 ws 

N wn 

Trans-I ,2-Dichloroethene 156-60-5 

393-92 3OJAN1992 ws 

N 

uglL 


51692 I6FEB1 992 ws 

N 

uglL 


628-92 05MAR1992 ws 

N 

IIglL 

Page 25 of 176



Trans-1.2-Dichloroethene 156-60-5 697-92 12MAR1992 WS 5.00E+00 < N uglL 


79-01-6 

1020-92 04MAY 1992 ws 1 .OOE+OO 

C 

NT 

uglL 


79-01-6 

1140-92 

01JUN1992 ws l.OOE+OO 

< 

N 

uglL 


79-01-6 

1329-92 06JUL1992 ws l.OOE+OO 

C 

N 

uglL 


79-01-6 

1474-92 O3AUG 1992 ws l.OOE+OO 

C 

N 

uglL 


79-01-6 

1621-92 3lAUGl992 ws l.OOE+OO 

< 

N 

uglL 


79-01 -6 

1793-92 070CT1992 ws l.OOE+OO 

C 

N 

uglL 


79-01 -6 

1934-92 03NOV1992 ws l.OOE+OO 

c 

N 

ug/L 


79-01 -6 

2098-92 01 DEC1992 ws l.OOE+OO 

< 

N 

ug1L 


79-01-6 

393-92 3OJANl992 ws l.OOE+OO 

< 

N 

uglL 


79-01-6 

516-92 16FEBl992 ws 1.00E+03 

UJ 

N 

ug1L 


79-01-6 

628-92 05MAR1992 ws l.OOE+OO 

< 

N 

uglL 


79-01-6 

697-92 12MAR1992 ws l.OOE+OO 

C 

N 

uglL 


79-01-6 

852-92 01APR1992 ws 1.00E+00 

C 

N 

ug1L 

Tungsten 

7440-33-7 

1020-92 MMAY 1992 ws O.OOE+OO 

C 

NT mglL 

Tungsten 

7440-33-7 

1140-92 

01JUN1992 ws 0.00E+00 

< 

N 

mglL 

Tungsten 

7440-33-7 

1329-92 06JUL1992 ws O.OOE+OO 

C 

N 

mglL 

Tungsten 

7440-33-7 

1474-92 03AUG1992 ws 0.00E+00 

< 

N 

mglL 

Tungsten 

7440-33-7 

1621-92 31AUG1992 ws O.OOE+W 

C 

N 

mglL 

Tungsten 

7440-33-7 

1793-92 070CT1992 ws O.OOE+OO 

< 

N 

mglL 

Tungsten 

7440-33-7 

1934-92 03NOV1992 ws O.WE+Ml 

C 

N 

mglL 

Tungsten 

7440-33-7 

2098-92 01DEC1992 ws O.OOE+W 

N 

mglL 

Tungsten 

7440-33-7 

5511-92 19AUG1992 ws O.OOE+OO 

C 

N 

mglL 

Tungsten 

7440-33-7 

619-93 O5MAY 1993 ws O.WE+OO 

c 

N 

mglL 

Tungsten 

7440-33-7 

628-92 05MAR 1992 ws O.OOE+OO 

C 

N 

mglL 

Tungsten 

7440-33-7 

697-92 12MARl992 ws O.OOE+W 

< 

N 

mglL 

Tungsten 

7440-33-7 

852-92 01 APRI 992 ws O.OOE+W 

< 

N 

mg1L 

Uranium 

7440-61 -1 

1020-92 04MAY 1992 ws O.WE+OO 

C 

NT mgR 

Uranium 

7440-61 -1 

1072-93 16JUL1993 ws O.WE+W 

c 

N 

mglL 

Uranium 

7440-61 -1 

1140-92 

01JUN1992 ws O.OOE+W 

c 

N 

mglL 

Uranium 

7440-61 -1 

1202-93 05AUG1993 ws O.WE+OO 

c 

N 

mglL 

Uranium 

7440-61-1 

1202-94 OSMAY 1994 ws O.WE+OO 

N 

mglL 

Uranium 

7440-61-1 

1329-92 06JUL1992 ws O.WE+W 

C 

N 

mglL 

Uranium 

7440-61 -1 

134693 02SEP1993 ws O.WE+OO 

C 

N 

mglL 

Uranium 

7440-61 -1 

1376-94 03JUN1994 ws O.OOE+OO 

C 

N 

mgk 

Uranium 

7440-61-1 

1474-92 03AUGl992 ws O.WE+OO 

< 

NT mglL 

Uranium 

7440-61 -1 

1546-93 050CTl993 ws O.WE+W 

< 

N 

mg1L 

Uranium 

7440-61-1 

1612-94 01 JUL1994 ws O.OOE+OO 

C 

N mga 

Uranium 

7440-61-1 

1621-92 

3lAUG 1992 ws O.OOE+OO 

< 

N 

mglL 

Uranium 

7440-61-1 

17-94 05JAN1994 ws O.WE+W 

c 

N 

mgk 

Uranium 

7440-61-1 

1793-92 070CT1992 ws O.WE+W 

C 

N 

mglL 

Uranium 

7440-61 -1 

18-95 WAN1995 ws O.OOE+OO 

< 

N 

mglL 

Uranium 

7440-61-1 

183693 MNOV1993 ws O.OOE+OO 

< 

N 

mglL 

Uranium 

7440-61 -1 

1918-94 OSAUG1994 ws O.WE+W 

< 

N 

mglL 

Uranium 

7440-61-1 

1934-92 03NOV1992 ws O.OOE+W 

< 

N 

mg/L 

Uranium 

7440-61-1 

2098-92 01DEC1992 ws O.OOE+W 

C 

N 

mgfl 

Uranium 

7440-61-1 

2121-94 OZSEPl994 ws O.WE+W 

c 

N 

mglL 

Uranium 

7440-61 -1 

2152-93 lODEC1993 ws O.WE+W 

c 

N 

mgfl 

Uranium 

7440-61 -1 

21895 03FEBl995 ws O.WE+W 

C 

N 

mg/L 

Uranium 

7440-61 -1 

2411-94 070CT1994 ws O.WE+W 

c 

N 

mg/L 

Uranium 

7440-61-1 

2689-94 MNOV1994 ws O.WE+W 

C 

N 

mglL 

Uranium 

7440-61-1 

2859-94 02DEC1994 ws O.WE+W 

c 

N 

mglL 

Uranium 

7440-61 -1 

286-94 MFEB1994 ws O.OOE+OO 

C 

N 

mglL 

Uranium 

7440-61 -1 

393-92 30JAN1992 ws O.WE+W 

C 

N 

mglL 

Uranium 

7440-61-1 

435-95 03MARl 995 ws O.OOE+W 

< 

N 

mglL 

Uranium 

7440-61 -1 

505-94 03MAR1994 ws O.OOE+OO 

c 

N 

mglL 

Uranium 

7440-61 -1 

516-92 16FEB1992 ws O.OOE+OO 

N 

mglL 

Uranium 

7440-61 -1 

5511-92 

19AUG1992 ws O.OOE+OO 

C 

N 

mglL 

Uranium 

7440-61 -1 

6165-92 llNOV1992 ws O.WE+OO 

c 

N 

mglL 

Uranium 

7440-61-1 

619-93 OSMAY 1993 ws O.WE+OO 

c 

N 

mg/L 

Uranium 

7440-61-1 

628-92 05MAR1992 ws O.WE+W 

C 

N 

mglL 

Uranium 

7440-61 -1 

631-95 05APR1995 ws O.WE+W 

c 

N 

mglL 

Uranium 

7440-61 -1 

697-92 12MAR1992 ws O.WE+W 

c 

N mgn 

Uranium 

7440-61-1 

785-95 03MAYl995 ws O.WE+W 

c 

N mgR 

Uranium 

7440-61-1 

800-93 02JUN1993 ws O.WE+W 

c 

N 

mgfl 

Uranium 

7440-61 -1 

852-92 OIAPR1992 ws O.WE+OO 

c 

N 

mg/L 

Uranium 

7440-61-1 

899-94 08APR1994 ws O.WE+W 

c 

N 

mglL 

Uranium 

7440-61 -1 

95495 OlJUNl995 ws O.WE+OO 

c 

N 

mgfl 

Vanadium 

7440-62-2 

1020-92 04MAY 1992 ws O.WE+W 

c 

NT mgfl 

Vanadium 

7440-62-2 

1140-92 

01JUNl992 ws O.OOE+OO 

C 

N 

mglL 

Vanadium 

7440-62-2 

1329-92 06JUL1992 ws O.WE+W 

c 

N 

mglL 

Vanadium 

7440-62-2 

1474-92 03AUGl992 ws O.WE+W 

c 

N 

mgfl 

Page 26 of 176




Vanadium 7440-62-2 1621 -92 31AUGl992 WS O.OOE+OO < N mglL 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

so296 

SO296 

1330-20-7 

7440-66-6 

7440-67-7 

1934-92 

2098-92 

393-92 

551 1-92 

619-93 

628-92 

697-92 

852-92 

1020-92 

11 40-92 

1329-92 

1474-92 

1621-92 

1793-92 

2098-92 

393-92 

516-92 

628-92 

697-92 

1020-92 

1140-92 

1329-92 

147492 

162 1-92 

1793-92 

1934-92 

2098-92 

393-92 

61 9-93 

628-92 

852-92 

1020-92 

1 140-92 

1329-92 

1621-92 

1934-92 

2098-92 

393-92 

551 1-92 

61 9-93 

628-92 

697-92 

852-92 

1020-92 

1064-92 

1072-93 

1093-92 

1140-92 

1 145-95 

1192-92 

1202-93 

1202-94 

1219-92 

126492 

1306-92 

1934-92 

852-92 

5511-92 

697-92 

1474-92 

1793-92 

1 108-92 

1329-92 

1346-93 

1366-92 

1376-94 

1415-92 

1474-92 

1546-93 

1441 

-92 

1500-92 

03NOV1992 

01 DEC1992 

30JAN1992 

19AUG1992 

O5MAY 1993 

O5MAR1992 

12MAR1992 

01 APRl992 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

01DEC1992 

30JANI 992 

16FEB1992 

OSMAR1992 

12MARl992 

01APR1992 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUGl992 

31AUG1992 

070CT1992 

03NOV1992 

OlDEC1992 

30JAN1992 

19AUG1992 

O5MAY 1993 

05MAR1992 

12MAR1992 

01APR1992 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

01 DECl992 

3OJANl992 

19AUG1992 

O5MAY 1993 

osMAR1992 

12MAR1992 

01APR1992 

04MAY 1992 

13MAY 1992 

16JULl993 

2WAY 1992 

26MAY1992 

01 JUN1992 

06JULl995 

O8JUNl992 

05AUG1993 

QWY 

1994 

15JUN1992 

22JUN1992 

29JUN1992 

06JULl992 

02SEP1993 

13JUL1992 

OUUN1994 

21JUL1992 

27JULl992 

O3AUG1992 

I OAUG1992 

050CT1993 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

< 

< 

< 

< 

< 

< 

< 

< 

< 

c 

c 

< 

< 

< 

UJ 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

Q 

< 

< 

< 

< N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ug1L 

uglL 

uglL 

uglL 

uglL 

mglL 

mglL 

mg1L 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mg1L 

SU 

su 

su 

su 

SU 

SU 

su 

SU 

su 

SU 

su 

su 

SU 

SU 

su 

SU 

su 

SU 

su 

SU 

su 

SU 

mglL 

Page 27 of 176




SO296 1548-92 17AUG1992 WS 7.00E+00 N su 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

WAG 7, SWU 8, C746K-2 

1,l-Dchloroethane 



1 .l -Dchloroethane 




1 .I-Dichbroethane 





1 ,l -Dichloroethene 









Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

SO296 

SO296 

so296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

so296 

SO296 

SO296 

SO296 

so296 

so296 

SO296 

SO296 

SO296 

so296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

so296 

SO296 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-354 

75-35-4 

75-35-4 

75-35-4 

75-354 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

1596-92 

1612-94 

1621 -92 

1659-92 

1681-92 

17-94 

1793-92 

18-95 

1836-93 

1918-94 

1964-92 

2098-92 

2121-94 

2134-92 

2152-93 

218-95 

2411-94 

2689-94 

2859-94 

286-94 

393-92 

435-95 

505-94 

609-92 

619-93 

628-92 

631-95 

634-93 

653-92 

697-92 

709-92 

785-95 

800-93 

824-92 

852-92 

886-92 

899-94 

919-92 

954-95 

973-92 

991-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099 - 92 

629-92 

69892 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

193592 

2099-92 

24AUG1992 

01 JUL1994 

31 AUG1992 

OlSEPl992 

14SEP1992 

05JAN1994 

070CT1992 

OSJAN1995 

04NOV1993 

05AUG1994 

09NOV1992 

01DEC1992 

02SEP1994 

07DEC1992 

lODEC1993 

03FEBl995 

070CT1994 

04NOV1994 

O2DECl994 

04FEB1994 

3OJAN1992 

03MAR1995 

03MAR1994 

02MAR1992 

OSMAY 1993 

05MAR1992 

OJAPR 1995 

OSMAY 1993 

OW1992 

12MAR1992 

16MAR1992 

03MAY 19% 

02JUN1993 

23MAR1992 

01 APRl992 

06APR1992 

08APR1994 

13APR1992 

01JUN1995 

22APR1992 

27APRl992 

01JUNl992 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

OJNOV1992 

01 DECl992 

05MAR 1992 

12MAR1992 

01 APR 1992 

04MAY1992 

01JUN1992 

06JULl992 

O3AUG 1992 

31AUG1992 

070CT1992 

03NOV1992 

01 DECl992 

WAR1992 

12MAR1992 

01 APRl992 

04MAY 1992 

01 JUN1992 

06JUL1992 

03AUG1992 

3lAUGl992 

070CTl992 

03NOV1992 

01 DECl992 


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ws 

ws 

ws 

ws 

ws 

ws 

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ws 

ws 

ws 

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< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

c 

< 

c 

< 

< 

< 

c 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

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su 

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su 

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su 

su 

su 

su 

su 

uglL 

uglL 

uglL 

uglL 

ugfl 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ugk 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ugk 

uglL 

ug/L 

mg/L 

mglL 

mgk 

mglL 

WlL 

mglL 

mgfl 

mglL




Aluminum 7429-90-5 620-93 05MAY1993 WS 1.00E+00 N mglL 

Aluminum 

Aluminum 

Aluminum 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

7429-90-5 

7429-90-5 

7429-90-5 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

71-43-2 

71-43-2 

71-43-2 

71-43-2 

7143-2 

71-43-2 

71-43-2 

71-43-2 

71-43-2 

71-43-2 

71-43-2 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41 -7 

7440-41 -7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

629-92 

698-92 

853-92 

1021 -92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021 -92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021 -92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

05MAR1992 

12MAR1992 

01APRl992 

04MAY 1992 

OlJUN1992 

06JUL1992 

O3AUG 1992 

31AUG1992 

070CT1992 

03NOV1992 

01DEC1992 

O5MAY 1993 

05MAR1992 

12MAR1992 

01APR1992 

04MAY 1 992 

01JUN1992 

O6JUL1 992 

03AUG1992 

3lAUG1992 

070CT1992 

03NOV1992 

01DEC1992 

05MAY 1993 

05MARl992 

12MAR1992 

01 APRI 992 

04MAY 1992 

01 JUNl992 

06JUL1992 

03AUG1992 

3lAUG 1992 

070CT1992 

03NOV1992 

01 DECl992 

05MAY1993 

05MARl992 

1 2MARl 992 

01 APRl992 

04MAY 1992 

01 JUN1992 

06JUL1992 

03AUG1992 

31 AUG 1992 

070CT1992 

03NOV1992 

01 DEC1992 

MAR1992 

12MARl992 

01 APR1992 

04MAY 1992 

OlJUNl992 

06JULl992 

03AUGl992 

3lAUGl992 

070CT1992 

03NOV1992 

OlDEC1992 

MAY1993 

05MAR1 992 

12MAR1992 

01APR1992 

04MAYI992 

01JUNl992 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

01 DECl992 

05MAY 1993 


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ws 

ws 

ws 

ws 

ws 

ws 

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ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

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ws 

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ws 

ws 

ws 

ws 

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ws 

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ws 

ws 

ws 

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ws 

ws 

ws 

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ws 

ws 

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C 

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< 

C 

C 

C 

C 

C 

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< 

c 

c 

C 

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C 

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c 

c 

c 

< 

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c 

c 

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< 

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< 

c 

c 

< 

< 

c 

c 

c 

< 

c 

< 

< 

c 

< 

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N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mgfl 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

mglL 

mgfl 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mgfl 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

wfl 

mgfl 

mgfl 

wlL 

mglL 

mglL 

wfl 

wfl




Bismuth 7440-69-9 629-92 05MAR1992 WS O.OOE+OO C N 

Bismuth 

Bismuth 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Coban 

Coban 

Coban 

Coban 

Cobalt 

Coban 

Cobalt 

Coban 

Coban 

Cobalt 

Coban 

Cobalt 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

copper 

Copper 

Copper 

Copper 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

7440-69-9 

7440-69-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-439 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-484 

7440-484 

7440-48-4 

7440-484 

7440-48-4 

7440-48-4 

7440-48-4 

7440-50-8 

7440-70-2 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-0 

7440-50-0 

7440-50-8 

7440-50-8 

100-414 

100-41-4 

100-41-4 

100-41-4 

100-41-4 

100-41-4 

100-41-4 

100-41-4 

100-41-4 

7440-50-8 

7440-50-8 

7440-50-8 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1794-92 

1622-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021 -92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021 

-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

69892 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1794-92 

1935-92 

2099-92 

629-92 

1622-92 

12MAR1992 

01APR1992 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUG1992 

31 AUGl992 

070CT1992 

03NOV1992 

01 DEC1992 

O5MAY 1993 

05MAR1992 

12MAR1992 

01 APRl992 

04MAY 1992 

OlJUN1992 

06JULI 992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

01DEC1992 

05MAY 1993 

05MAR1992 

12MAR1992 

01 APR1992 

04MAY1992 

01JUN1992 

06JULl992 

03AUG1992 

31 AUGl992 

070CT1992 

03NOVl992 

OlDEC1992 

05MAY1993 

05MAR1992 

12MAR1992 

01 APR 1992 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUG1992 

3lAUGl992 

070CT1992 

03NOV1992 

01DEC1992 

(HMAY 1993 

osMAR1992 

1 ZMARI 992 

01 APRI 992 

04MAY 1992 

01JUN1992 

06JULl992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

OlDECl992 

05MAY1993 

%MAR1992 

12MARl992 

01APR1992 

04MAY 1992 

0 1 JUN 1992 

06JUL1992 

03AUG1992 

31 AUG1992 

070CTl992 

03NOV1992 

01DEC1992 

05MAR1992 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

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ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

O.OOE+OO 

O.oOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

0.00E+00 

0.00E+00 

1.90€+01 

1.90E+01 

2.00E+Ol 

1.70€+01 

1.80€+01 

1.50E+01 

1.70€+01 

1.50€+01 

1.20E+01 

1.40E+01 

l.lOE+Ol 

O.OOE+W 

O.OOE+W 

O.OOE+W 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+W 

O.OOE+W 

O.OOE+OO 

O.OOE+W 

O.OOE+OO 

O.OOE+W 

O.OOE+OO 

O.WE+W 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

0.00E+00 

0.00E+00 

O.OOE+OO 

0.00E+00 

O.WE+OO 

O.OOE+OO 

0.00E+00 

O.WE+OO 

O.WE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+M) 

O.WE+OO 

O.OOE+W 

O.OOE+OO 

5.00E+W 

5.WE+00 

1.60E+01 

5.00E+W 

5.00E+00 

5.00E+W 

5.00E+W 

5.00E+W 

5.WE+00 

5.00E+00 

C 

< 

C 

C 

C 

C 

C 

C 

< 

C 

C 

C 

C 

C 

C 

c 

C 

C 

C 

C 

C 

C 

C 

C 

C 

C 

< 

c 

C 

< 

C 

< 

C 

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< 

< 

C 

c 

c 

C 

< 

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c 

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C 

C 

N 

C 

N 

< NT 

C 

N 

C 

N 

C 

N 

C 

N 

C 

N 

c 

N 

< N 

N 

c 

N 

C 

N 

C 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

Page 30 of 176



ANALYTE CAS NUMBER SAMPLE ID DATE MPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Ethylbenzene 100-41-4 698-92 12MAR1992 WS 5.00E+00 c N ug1L 

Ethylbenzene 

Iron 

Iron 

Iron 

Iron 

Iron 

iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lilhium 

Lithium 

Lithium 

Lithium 

Lithium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

100-41 -4 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439 - 89 - 6 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-95-4 

7439-95-4 

7439 - 95 -4 

7439-95-4 

7439-954 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-954 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

853-92 

1021 -92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021 -92 

1141-92 

1330-92 

1475-92 

1622-92 

179492 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021 -92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

179492 

1935-92 

2099-92 

620-93 

629-92 

01APRl992 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

01 DECl992 

O5MAY 1993 

05MAR1992 

12MAR1992 

OIAPRI 992 

04MAY1992 

OlJUN1992 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

01DEC1992 

05MAY 1993 

05MAR1992 

12MARl992 

01 APR1992 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUG1992 

3lAUGl992 

070CT1992 

03NOV1992 

OlDEC1992 

05MAY 1993 

05MAR1992 

12MAR1992 

01 APRI 992 

04MAYl992 

01 JUNl992 

06JULl992 

03AUGl992 

31AUG1992 

070CT1992 

03NOV1992 

OlDECl992 

05MAYl993 

(HMAR 1992 

12MARl992 

01 APRI 992 

MMAY 1992 

01JUN1992 

06JUL1992 

O3AUG1992 

31 AUGl992 

070CT1992 

03NOVl 992 

01 DECl992 

OSMAY 1993 

05MARI 992 

12MARl992 

01 APR1992 

04MAY 1992 

01JUN1992 

06JULl992 

03AUG1992 

31 AUGI 992 

070CT1992 

03NOV1992 

01 DECl992 

05MAY 1993 

05MAR1992 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

c 

c 

c 

c 

c 

c 

c 

c 

c 

< 

c 

c 

< 

c 

< 

< 

c 

c 

c 

< 

c 

c 

c 

c 

c 

< 

< 

c 

< 

c 

< 

< 

c 

c 

4 

< 

< 

< 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

ug1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

mglL 

m!35 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

WlL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

Wfl 

mglL 

mgfl 

mglL 

mglL 

WR 

mglL



Mercury 7439-97-6 698-92 12MARl992 WS O.OOE+OO c N mglL 

Mercury 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

PCB 

PCB 













Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

7439-97-6 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98.7 

7439-98-7 

7439-98-7 

7439-98-7 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

1336-36-3 

1336-36-3 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-18-8 

7440-188 

7440-18-8 

7440-188 

7440-18-8 

7440-18-8 

7440-188 

7440-188 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1861-92 

1935-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021 -92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

01APR1992 

04MAY 1992 

01JUN1992 

06JULl992 

03AUG1992 

31 AUGl992 

070CT1992 

03NOV1992 

01DEC1992 

05MAY 1993 

05MAR1992 

12MAR1992 

01APR1992 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUGl992 

31AUG1992 

070CT1992 

03NOV1992 

01 DEC1992 

OMAY 1993 

05MAR1992 

12MAR1992 

01APRl992 

04MAY1992 

01JUN1992 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

01DEC1992 

WAY1993 

WAR1992 

12MAR1992 

01 APRl992 

190CT1992 

03NOV1992 

WAY 1992 

01 JUN1992 

06JUL1992 

03AUGl992 

31AUG1992 

070CT1992 

03NOV1992 

OlDECl992 

WAY1993 

WAR1992 

12MARl992 

OlAPR1992 

MAY1992 

01 JUN1992 

06JUL1992 

03AUG1992 

3IAUG1992 

070CT1992 

03NOV1992 

01 DECl992 

OSMAY 1993 

05MAR1992 

12MARI 992 

01 APRl992 

04MAYl992 

OlJUN1992 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

01 DEC1992 

< 

c 

c 

c 

c 

c 

c 

c 

c 

< 

c 

< 

< 

< 

c 

c 

< 

C 

< 

UJ 

c 

c 

c 

c 

c 

c 

c 

< 

< 

c 

< 

c 

< 

c 

c 

c 

c 

c 

c 

c 

c 

c 

c 

c 

c 

c 

c 

c 

c 

J 

< 

c 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

vvs 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws




Ruthenium 7440-18-8 620-93 05MAY1993 WS O.OOE+OO < N mg1L 

Ruthenium 

Ruthenium 

Ruthenium 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Sulfate 

Sulfate 

Sulfate 

Sulfate 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

7440-18-8 

7440-18-8 

7440-18-8 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

12 143-45-2 

12 143-45-2 

12 143-45-2 

12143-45-2 

7440-25-7 

7440-25-7 

7440-25-7 

1440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-28-0 

1440-28-0 

7440-28-0 

1440-28-0 

7440-28-0 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021 -92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1141-92 

1330-92 

1475-92 

1622-92 

1021 -92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

05MAR1992 

12MAR1992 

01 APRl992 

04MAY1992 

01JUN1992 

06JUL1992 

O3AUG 1992 

31AUG1992 

070CT1992 

03NOV1992 

01DEC1992 

O5MAY 1993 

05MAR1992 

1 2MARl 992 

01 APRl992 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUG1992 

3lAUG 1992 

070CT1992 

03NOV1992 

01DEC1992 

OCMAYI 993 

O5MARl 992 

12MAR1992 

01 APRl992 

04MAY 1992 

01 JUN1992 

06JUL1992 

03AUGl992 

3lAUGl992 

070CT1992 

03NOV1992 

01DEC1992 

OSMAY 1993 

05MAR1992 

12MARl992 

01 APRl992 

04MAY 1992 

01 JUN1992 

06JUL1992 

03AUG1992 

3lAUGl992 

070CT1992 

03NOV1992 

01DEC1992 

05MAY 1993 

05MAR1992 

12MARl992 

01 APRl992 

01JUN1992 

06JULl992 

03AUG1992 

31AUG1992 

04MAY 1992 

01JUNl992 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

OMAY 1993 

05MARl992 

12MAR1992 

01 APRI 992 

04MAY 1992 

OlJUN1992 

06JUL1992 

03AUG1992 

31AUG1992 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

< N 

< N 

< N 

NT 

N 

N 

N 

< 

J 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

c 

J 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgk 

mglL 

mglL 

mglL 

mglL 

mglL 

WlL 

mglL 

WlL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgk 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mg/L 

mglL 

mg/L 

mglL 

mgfl 

mglL 

mglL 

WlL 

mg/L 

mgfl 

Wk 

mglL 

WlL 

Wk 

WlL 

mglL 

Wfl 

mglL




Thallium 7440-28-0 1794-92 070CT1992 WS O.OOE+OO < N mglL 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Tin 

Tin 

Tin 

Tin 

Tin 

Tin 

Tin 

Tin 

Tin 

Tin 

Tin 

Tin 

Titanium 

Titanium 

Titanium 

Titanium 

Titanium 

Titanium 

Titanium 

Titanium 

Titanium 

Titanium 

Titanium 

Titanium 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 







Trans-I .'L-Dichloroethene 






Trihloroethene 






7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-31-5 

7440-31 -5 

7440-31-5 

7440-31-5 

7440-31-5 

7440-31 -5 

7440-31-5 

7440-31-5 

7440-31 -5 

7440-31-5 

7440-31-5 

7440-31 -5 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

108-88-3 

108-88-3 

I 08-88-3 

108-88-3 

108-88-3 

108-88-3 

108-88-3 

108-88-3 

108-88-3 

108-88-3 

108-88-3 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021 -92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141 -92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

03NOV1992 

01 DEC1992 

O5MAY 1993 

05MAR1992 

12MAR1992 

01 APR1992 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

01DEC1992 

05MAY1993 

O5MARl 992 

12MAR1992 

01 APRl992 

04MAY 1992 

01JUN1992 

06JULl992 

03AUG1992 

3lAUGl992 

070CT1992 

03NOV1992 

OlDEC1992 

(HMAY 1993 

OSMAR1992 

12MAR1992 

01 APRl992 

04MAY1992 

01 JUN1992 

06JULl992 

03AUGl992 

3lAUGl992 

070CT1992 

03NOV1992 

01DEC1992 

05MAY1993 

05MAR1992 

12MAR1992 

OlAPR1992 

04MAY 1992 

01 JUN1992 

06JUL1992 

03AUG1992 

31 AUG 1992 

070CT1992 

03NOVl992 

01DECl992 

05MAR1992 

12MAR1992 

OIAPRI 992 

04MAY1992 

01JUN1992 

06JUL1992 

03AUG1992 

31 AUG 1992 

07OCT1992 

03NOV1992 

OlDEC1992 

05MAR 1992 

12MAR1992 

OlAPR1992 

04MAY1992 

OlJUN1992 

06JULl992 

03AUGl992 

31 AUG 1992 

070CT1992 

03NOV1992 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mgll 

mglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

WlL 

mglL 

mglL 

mglL 

mglL 

mglL 

wfl 

mglL 

mgfl 

uglL 

uglL 

uglL 

ug1L 

ugfl 

ugfl 

ug1L 

wfl 

uglL 

ugfl 

uglL 

uglL 

uglL 

ugk 

uglL 

uglL 

uglL 

uglL 

ugfl 

uglL 

ugk 

ugfl 

ugfl 

ugfl 

uglL 

wfl 

ugfl 

ugfl 

ugfl




Trichloroethene 79-01-6 2099-92 OlDEC1992 WS 1.00E+00 




Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

79-01-6 

79-01-6 

79-01-6 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-61-1 

7440-61 

-1 

7440-61 -1 

7440-61 -1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-666 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-67-7 

7440-67-7 

7440-67-7 

7440-66-6 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

629-92 

698-92 

853-92 

1021-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1935-92 

2099-92 

620-93 

698-92 

853-92 

1141-92 

1475-92 

1622-92 

1794-92 

2099-92 

629-92 

698-92 

853-92 

1021 

-92 

11 41 -92 

1330-92 

1475-92 

1141-92 

629-92 

1021-92 

1330-92 

1935-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

698-92 

853-92 

1021-92 

1141-92 

1330-92 

1475-92 

1622-92 

1794-92 

1935-92 

2099-92 

620-93 

629-92 

05MAR1992 

12MAR1992 

01APR1992 

MMAYl992 

01JUN1992 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

01 DEC1992 

05MAY 1993 

OSMARl992 

12MAR1992 

01 APRl992 

04MAY 1992 

01 JUN1992 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

01 DEC1992 

05MAY 1993 

05MAR1992 

12MAR1992 

01 APRl992 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUGl992 

31 AUGl992 

03NOV1992 

01DEC1992 

OSMAY 1993 

05MAR1992 

12MAR1992 

01 APRl992 

04MAY 1992 

OlJUN1992 

06JUL1992 

03AUGl992 

31AUG1992 

070CT1992 

03NOV1992 

01DEC1992 

05MAR1992 

12MARl992 

01 APRl992 

04MAY 1992 

01 JUN1992 

06JUL1992 

O3AUG 1992 

31 ALJG1992 

070CT1992 

03NOV1992 

01DEC1992 

05MAY 1993 

05MAR1992 

12MAR1992 

0 1 APR 1 992 

04MAY 1992 

01JUN1992 

06JULl992 

03AUG1992 

3lAUGl992 

070CT1992 

03NOV1992 

01DEC1992 

(HMAY 1 993 

05MAR1992 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

0.00E+00 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+W 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

l.OOE+Ol 

l.OOE+Ol 

l.OOE+Ol 

l.OOE+Ol 

l.OOE+Ol 

1.00E+01 

l.OOE+Ol 

l.OOE+Ol 

l.OOE+Ol 

l.OOE+Ol 

l.OOE+Ol 

0.00E+00 

0.00E+00 

O.WE+OO 

O.OOE+W 

O.OOE+OO 

0.00E+00 

0.00E+00 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+W 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

0.00E+00 

0.00E+00 

0 .OOE+ 00 

O.OOE+W 

O.OOE+OO 

0.00E+00 

0.00E+00 

0.00E+00 

c 

c 

c 

< 

< 

< 

< 

< 

Q 

c 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

ug1L 

uglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mg1L 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mgfl 

mgk 

mgfl 

mgk 

mglL 

mgfl 

mglL 

mglL 

mgfl 

uglL 

uglL 

uglL 

uglL 

ug1L 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

mglL 

mglL 

mgfl 

mglL 

mgfl 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mgk 

mglL 

mglL 

mglL 

m9fl 

mglL 

mglL 

mglL 

Page 35 of 176




Zirconium 7440-67-7 698-92 12MAR1992 WS O.OOE+OO < N mglL 

Zirconium 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

WAG 7. smu a. ~ 7 4 6 ~ 











Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Barium 

Barium 

Barium 

Barium 

Barium 

Benzene 

Benzene 

Benzene 

7440-67-7 

SO296 

SO296 

SO296 

so296 

SO296 

so296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

so296 

SO296 

SO296 

so296 

so296 

so296 

so296 

so296 

SO296 

so296 

SO296 

SO296 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

71-43-2 

71-43-2 

71-43-2 

853-92 

1021-92 

1065-92 

1094-92 

1109-92 

1141-92 

1193-92 

1220-92 

1265-92 

1307-92 

1330-92 

1367-92 

1416-92 

1442-92 

1475-92 

1501-92 

1549-92 

1597-92 

1622-92 

1660-92 

1682-92 

1794-92 

1965-92 

2099-92 

2135-92 

610-92 

620-93 

629-92 

654-92 

698-92 

710-92 

825-92 

853-92 

887-92 

920-92 

974-92 

992-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

01 APRl992 

04MAY 1992 

13MAY 1992 

20MAYl992 

26MAY 1992 

01JUN1992 

08JUN1992 

15JUNl992 

22JUN1992 

29JUN1992 

06JUL1992 

13JUL1992 

21 JUL1992 

27JUL1992 

03AUG1992 

10AUG1992 

17AUG1992 

24AUG1992 

31AUG1992 

08SEPl992 

14SEP1992 

070CT1992 

09NOV1992 

01DEC1992 

07DEC1992 

02MAR1992 

OWY 1993 

05MAR1992 

OM1992 

12MAR 1992 

16MAR1992 

23MAR1992 

01APR1992 

06APR1992 

13APR1992 

2ZAPR1992 

27APR1992 

04MAY 1992 

01JUNl992 

05MAR1992 

12MAR1992 

01APR1992 

04MAY1992 

01 JUN1992 

-1992 

12MAR1992 

OlAPR1992 

MY1992 

01 JUN1992 

05MAR1992 

12MAR1992 

01APR1992 

04MAY1992 

01 JUN1992 

05MAR1992 

12MAR1992 

01 APR1992 

04MAY1992 

01 JUN1992 

osMAR1992 

12MAR1992 

01 APR 1992 

MY1992 

01 JUN1992 

05MAR1992 

12MAR1992 

OlAPR1992 

my1992 

OlJUNl992 

osMAR1992 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

< N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

< 

< 

< 

< 

c 

c 

< 

< 

< 

< 

c 

< 

< 

< 

< 

< 

c 

c 

c 

c 

< 

c 

c 

c 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

mg/L 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

uglL 

wfl 

ugfl 

uglL 

uglL 

uglL 

ugfl 

uglL 

ug1L 

uglL 

ma/L 

mg1L 

mglL 

WlL 

mgk 

mglL 

WlL 

mglL 

mglL 

mglL 

mgfl 

mgfl 

mglL 

WIL 

mgk 

mgk 

Wfl 

mglL 

mgfl 

mgnuglL 

ugk 

UdL




Benzene 71-43-2 699-92 12MAR1992 WS 5.00E+00 c N UglL 

Benzene 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Coban 

Cobalt 

Cobalt 

Cobalt 

Coban 

Copper 

Copper 

Copper 

Copper 

Copper 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Gross Alpha 

Gross Beta 

Iron 

Iron 

Iron 

Iron 

Iron 

Lead 

Lead 

Lead 

Lead 

Lead 

Lithium 

Lithium 

Lithiurn 

Lithium 

Lithium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Mercury 

Mercury 

Mercury 

71-43-2 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

100-41-4 

100-41-4 

100-41-4 

100-41-4 

100-414 

12587-46-1 

12587-47-2 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7439-97-6 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

4952-92 

4952-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

01 APRl992 

04MAY 1992 

01JUN1992 

05MAR1992 

12MAR 1992 

01APR1992 

04MAY1992 

01JUN1992 

05MAR1992 

12MAR1992 

01 APRl992 

04MAY 1992 

01JUNl992 

05MAR1992 

12MAR1992 

01 APR 1992 

04MAY 1992 

01JUN1992 

05MAR1992 

12MAR1992 

01 APR1992 

04MAY 1 992 

01 JUN1992 

05MARl992 

12MAR1992 

01 APR 1992 

04MAY1992 

01 JUN1992 

05MAR1992 

12MAR1992 

01 APRl992 

04MAY 1992 

01JUN1992 

05MAR1992 

12MARl992 

01 APR 1992 

04MAY1992 

01JUN1992 

05MAR1992 

12MAR1992 

01 APRl992 

12MAY 1992 

1 2MAY 1992 

04MAY1992 

01 JUNl992 

MAR1992 

12MAR1992 

01 APRl992 

04MAY 1992 

01JUN1992 

05MAR1992 

12MAR1992 

OlAPR1992 

04MAY 1992 

01JUN1992 

(HMAR1992 

12MAR1992 

OlAPR1992 

04MAY 1992 

01JUN1992 

05MAR1992 

12MAR1992 

01 APRl992 

04MAY 1992 

01 JUN1992 

05MAR1992 

12MAR1992 

OlAPR1992 

04MAY 1992 

01JUNl992 

05MAR1992 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

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C 

C 

C 

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N 

N 

N 

N 

NT 

N 

N 

N 

N 

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N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

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N 

N 

ug1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mgfl 

mglL 

mg1L 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

mg1L 

ug/L 

uglL 

ug1L 

ug1L 

ugfl 

pciR 

pCiL 

mglL 

mglL 

mglL 

mg/L 

mglL 

mglL 

mgfl 

mglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

mglL 

mgn 

mglL 

mglL 

mglL 

mglL 

mg/L 

mglL 

mgfl 

mglL




Mercury 7439-97-6 699-92 12MAR1992 WS O.OOE+OO < N mglL 

Mercury 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 






Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silver 

Silver 

Silver 

Silver 

Silver 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Sulfate 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Technetium99 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Tin 

Tin 

Tm 

7439-97-6 

7439-98-7 

7439-98-7 

7439 - 9 a - 7 

7439-98-7 

7439-98-7 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-18-8 

7440-18-8 

7440-18-8 

7440-18-8 

7440-18-8 

7440-21-3 

7440-21 -3 

1440-21 -3 

7440-21 -3 

7440-21-3 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

12143-45-2 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

14133-76-7 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-2&0 

7440-29-1 

7440-29- I 

7440-29-1 

7440-29-1 

7440-29-1 

7440-31-5 

7440-31-5 

7440-31-5 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1142-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

4952-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

I 142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

01 APRl992 

MMAY1992 

01JUN1992 

05MAR1992 

12MAR1992 

01 APR 1992 

04MAY 1992 

01 JUN1992 

05MAR1992 

12MAR1992 

01APR1992 

04MAY 1992 

01JUN1992 

05MAR1992 

12MARl992 

01 APRI 992 

04MAY1992 

01 JUN1992 

05MARl992 

12MAR 1992 

01 APRI 992 

04MAY 1992 

01JUN1992 

05MAR1992 

12MARl992 

01APR1992 

04MAY 1992 

01JUN1992 

05MAR1992 

12MARl992 

OlAPRl992 

04MAY1992 

01JUNl992 

oEiMARl992 

12MAR1992 

01 APRl992 

04MAY1992 

01JUN1992 

05MAR1992 

12MARl992 

01 APRl992 

04MAY 1992 

01 JUN1992 

05MAR1992 

12MAR1992 

01 APRl992 

04MAY1992 

01JUNl992 

05MAR1992 

12MAR1992 

01APR1992 

01JUN1992 

04MAY 1992 

01JUN1992 

05MAR1992 

12MAR1992 

01 APRl992 

12MAY 1992 

04MAY 1 992 

OIJUN1992 

05MAR1992 

12MAR1992 

01 APRI 992 

04MAY 1992 

01 JUNI 992 

05MAR1992 

12MAR1992 

01 APRI 992 

MMAY 1992 

01JUN1992 

oEiMAR1992 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

N 

< NT 

< N 

< N 

< N 

< N 

< NT 

< N 

C 

N 

C 

N 

< N 

c 

NT 

C 

N 

< N 

< N 

< N 

NT 

< N 

< N 

< N 

c 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N




Tin 7440-31-5 699-92 12MAR1992 WS O.OOE+OO < N mg1L 

Tin 

Tikanium 

Titanium 

Tiianium 

Titanium 

Titanium 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 



Trans- 1,2-Dichloroeihene 


Trans-l,2-Dichloroeihene 






Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

WAG 7. S MU 8. C746K-3A 

7440-31-5 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

108-88-3 

108-88-3 

108-88-3 

108-88-3 

108-88-3 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-61-1 

7440-61-1 

7440-61 -1 

7440-61-1 

7440-61 - 1 

7440-61 -1 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

SO296 

SO296 

SO296 

SO296 

SO296 

so296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

so296 

so296 

SO296 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

4952-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1142-92 

630-92 

699-92 

854-92 

1022-92 

1066-92 

1095-92 

1110-92 

1142-92 

1194-92 

1221-92 

611-92 

630-92 

655-92 

699-92 

711-92 

826-92 

854-92 

886-92 

921-92 

975-92 

993-92 

01 APRl992 

04MAY 1992 

01JUN1992 

05MARl992 

12MAR1992 

01 APRl992 

04MAY 1992 

01JUN1992 

05MAR1992 

12MAR1992 

01 APRl992 

04MAY 1992 

01JUN1992 

O5MAR1992 

12MAR1992 

01 APRl992 

04MAY 1992 

01JUN1992 

05MAR1992 

12MAR 1992 

01 APRI 992 

O4MAY 1992 

01JUN1992 

05MAR1992 

1 2MARl 992 

01 APRl992 

04MAYI 992 

01 JUN1992 

12MAY1992 

05MAR1992 

12MAR1992 

OlAPR1992 

04MAY 1992 

01JUN1992 

OSMAR1992 

12MARl992 

01APR1992 

04MAY 1992 

01 JUNl992 

05MAR1992 

12MARl992 

01 APRI 992 

04MAY1992 

01 JUNl992 

05MAR1992 

12hMRI 992 

01 APRl992 

04MAY1992 

01 JUN1992 

05MAR1992 

12MAR1992 

01 APR1992 

04MAY 1992 

13MAY 1992 

2WAY 1992 

26MAY 1992 

01 JUN1992 

08JUN1992 

15JUN1992 

02MAR1992 

OSMAR1992 

09MAR1992 

12MAR1992 

16MAR1992 

23MAR1992 

OlAPR1992 

06APR1992 

13APRl992 

22APR1992 

27APR1992 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

< 

c 

< 

c 

c 

c 

< 

< 

c 

c 

< 

c 

< 

< 

c 

c 

c 

c 

< 

< 

c 

< 

c 

c 

c 

< 

c 

< 

< 

c 

< 

c 

c 

c 

c 

c 

c 

c 

c 

c 

c 

< 

< 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

rnglL 

rnglL 

mgfl 

mglL 

mglL 

mglL 

ug1L 

ug1L 

ug1L 

uglL 

UglL 

uglL 

uglL 

ug1L 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

mglL 

mgfl 

mglL 

WlL 

mgk 

mglL 

mglL 

mglL 

Wfl 

mglL 

mglL 

WlL 

mgfl 

mglL 

mglL 

mg/L 

uglL 

uglL 

ugk 

uglL 

uglL 

mg/L 

mglL 

mglL 

mglL 

mgk 

mglL 

mglL 

mglL 

mglL 

mglL 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

Page 39 of 176




1 ,l-Dichloroethane 75-34-3 1331-92 06JUL1992 ws 5.00E+00 < N uglL 












Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-354 

75-35-4 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

1476-92 

1623-92 

1795-92 

1936-92 

2100-92 

1331-92 

1476-92 

1623-92 

1795-92 

1936-92 

2100-92 

1073-93 

1203-93 

1203-94 

1331-92 

1347-93 

1377-94 

1476-92 

1547-93 

1613-94 

1623-92 

1795-92 

18-94 

1837-93 

03AUGl992 

31AUG1992 

070CT1992 

03NOV1992 

01 DEC1992 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

01 DEC1992 

16JULl993 

O5AUGl993 

05MAY1994 

06JULl992 

02SEPl993 

03JUN1994 

03AUGl992 

050CT1993 

01 JULl994 

31 AUG 1992 

070CT1992 

O5JAN1994 

04NOV1993 

5.00€+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00€+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

O.OOE+OO 

1.00E+00 

O.OOE+OO 

O.OOE+OO 

1.00E+00 

O.OOE+OO 

O.OOE+OO 

0.00€+00 

i.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

0.00€+00 

< 

< 

< 

< 

< 

c 

c 

c 

C 

< 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Aluminum 

7429-90-5 

19-95 05JAN1995 

O.OOE+OO 

N 

Aluminum ' 7429-90-5 

1919-94 05AUG1994 

0.00E+00 

N 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminurn 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-360 

7440-36-0 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

1936-92 

2100-92 

2122-94 

2153-93 

219-95 

2412-94 

2690-94 

2860-94 

207-94 

436-95 

506-94 

5510-92 

621-93 

632-95 

635-93 

786-95 

801 -93 

900-94 

1331 -92 

1476-92 

1623-92 

1795-92 

1833-93 

193692 

2100-92 

333-95 

5510-92 

621-93 

1073-93 

1203-93 

1203-94 

1331 -92 

1347-93 

1377-94 

1476-92 

1547-93 

1613-94 

1623-92 

1795-92 

18-94 

1833-93 

1837-93 

19-95 

1919-94 

1936-92 

03NOV1992 

01DEC1992 

02SEPl994 

1 ODEC1993 

03FEB1995 

070CT1994 

04NOV1994 

02DEC1994 

04FEB1994 

O3MAR1995 

03MAR1994 

19AUG 1992 

OSMAY 1993 

05APRl995 

05MAY 1993 

03MAYl995 

02JUN1993 

O8APR1994 

06JUL1992 

03AUGl992 

31AUG1992 

070CT1992 

1 ONOV1993 

03NOV1992 

OlDECl992 

22FEB1995 

19AUG1992 

OSMAY 1993 

16JULl993 

05AUG1993 

05MAYl994 

06JUL1992 

02SEPl993 

03JUN1994 

03AUG1992 

050CT1993 

01 JULl994 

31AUG1992 

070CT1992 

05JAN1994 

10NOV1993 

04NOV1993 

WAN1995 

05AUG1994 

03NOV1992 

0.00E+00 

O.OOE+W 

1.00E+00 

l.WE+OO 

1.00E+00 

O.OOE+W 

l.OOE+OO 

0.00E+W 

1.00E+00 

l.OOE+OO 

1.00E+00 

0.00E+00 

1.00E+00 

0.00E+00 

1 .OOE+OO 

1.00E+00 

0.00E+W 

1.00E+00 

O.WE+W 

O.WE+W 

O.OOE+OO 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.OOE+OO 

0.00E+00 

O.M)E+M) 

O.WE+OO 

O.WE+W 

O.OOE+OO 

0.00E+00 

O.WE+W 

O.WE+OO 

O.WE+OO 

O.OOE+W 

0.00E+W 

O.WE+OO 

O.WE+OO 

O.WE+OO 

0.00E+W 

0.00E+00 

0.00E+00 

O.WE+W 

O.WE+W 

N 

< 

c 

X 

c 

< 

c 

c 

c 

c 

c 

c 

< 

c 

c 

c 

< 

c 

< 

c 

c 

< 

< 

c 

c 

c 

c 

< 

< 

c 

< 

c 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws



ANALYTE CAS NUMBER SAMPLE ID DATE WPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Arsenic 7440-30-2 2100-92 01DEC1992 WS O.OOE+OO < N mglL 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Bismuth 

Bismuth 

Bismuth 

7440-30-2 

7440-382 

7440-30-2 

7440-30-2 

7440-30-2 

7440-30-2 

7440-30-2 

7440 - 30 - 2 

7440-30-2 

7440-38-2 

7440-38-2 

7440-30-2 

7440-30-2 

7440-30-2 

7440-30-2 

7440-30-2 

7440-30-2 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7 44 0 - 3 9 - 3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

71-43-2 

71-43-2 

7 1 -43-2 

7 1-43-2 

71-43-2 

7 1 -43-2 

7440-41-7 

7440-41 -7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41 -7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-69-9 

7440-69-9 

7440-69-9 

2122-94 

2153-93 

219-95 

2412-94 

2690-94 

2860-94 

207-94 

333-95 

436-95 

506-94 

5510-92 

621-93 

632-95 

635-93 

786-95 

801-93 

900-94 

1073-93 

1203-93 

1203-94 

1331-92 

1347-93 

1377-94 

1476-92 

1547-93 

1613-94 

1623-92 

1795-92 

10-94 

1033-93 

1037-93 

19-95 

1919-94 

1936-92 

2100-92 

2122-94 

2153-93 

219-95 

2412-94 

2690-94 

2860-94 

207-94 

333-95 

436-95 

506-94 

5510-92 

621-93 

632-95 

635-93 

786-95 

801-93 

900-94 

1331-92 

1476-92 

1623-92 

1795-92 

1936-92 

2100-92 

1331-92 

1476-92 

1623-92 

1795-92 

1833-93 

1936-92 

2100-92 

333-95 

5510-92 

621-93 

1331-92 

1476-92 

1623-92 

02SEP1994 

10DEC1993 

03FEB1995 

070CT1994 

04NOV1994 

02DEC1994 

04FEB1994 

22FEB1995 

O3MAR1995 

03MARl994 

19AUG1992 

05MAY 1993 

05APR1995 

O5MAY 1993 

O3MAY 1995 

02JUN1993 

OBAPRl994 

16JUL1993 

05AUGl993 

O5MAY 1994 

06JUL1992 

02SEP1993 

03JUN1994 

03AUG1992 

050CT1993 

01 JULl994 

3lAUG1992 

070CT1992 

05JAN1994 

lONOV1993 

04NOVl993 

05JAN1995 

05AUG1994 

03NOV1992 

01 DEC1992 

02SEPl994 

lODECl993 

03FEB1995 

070CT1994 

04NOV1994 

02DEC1994 

04FEB1994 

22FEB1995 

03MAR1995 

03MAR1994 

19AUG1992 

WAY 1993 

05APR1995 

05MAY 1993 

OJMAY 1995 

02JUN1993 

00APR1994 

06JULl992 

03AUG1992 

31 AUG 1992 

070CT1992 

03NOV1992 

01 DECl992 

06JULl992 

03AUG1992 

3lAUG1992 

070CT1992 

10NOV1993 

03NOV1992 

01 DECl992 

22FEB1995 

19AUGl992 

WAY 1993 

06JUL1992 

03AUGl992 

3lAUGl992 


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ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

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ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

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N 

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N 

cs 

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Bismuth 7440-69-9 1795-92 070CT1992 WS O.OOE+OO 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

744047-3 

7440-43-9 

7440-43-9 

7440-70-2 

1936-92 

2100-92 

5510-92 

621-93 

1073-93 

1203-93 

1203-94 

1331-92 

1347-93 

1377-94 

1476-92 

1547-93 

1613-94 

1623-92 

1795-92 

18-94 

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833-93 

1837-93 

19-95 

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1936-92 

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2122-94 

2153-93 

219-95 

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333-95 

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632-95 

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1331-92 

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1613-94 

1623-92 

1795-92 

1833-93 

1837-93 

19-95 

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1936-92 

2100-92 

2122-94 

2153-93 

2412-94 

la94 

03NOV1992 

01 DEC1992 

19AUG1992 

05MAY1993 

16JULl993 

05AUG1993 

O5MAY 1994 

06JUL1992 

02SEPl993 

03JUN1994 

03AUGl992 

050CT1993 

OlJUL1994 

31 AUG 1992 

070CT1992 

05JAN1994 

1 ONOVl993 

04NOV1993 

05JAN1995 

05AUG1994 

03NOV1992 

01DECl992 

OZSEPI 994 

10DEC1993 

03FEBl995 

070CT1994 

WNOV1994 

02DECl994 

04FEB1994 

22FEB1995 

03MAR1995 

03MAR1994 

19AUG 1992 

05MAY1993 

05APR1995 

05MAY 1993 

O3MAY 1995 

02JUN1993 

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01 JUN1995 

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31AUG1992 

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03NOV1992 

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05MAY1993 

16JUL1993 

05AUG1993 

05MAY1994 

06JUL1992 

02SEP1993 

03JUN1994 

03AUG1992 

050CT1993 

01 JULl994 

3lAUGl992 

07OCT1992 

05JAN1994 

lONOVl993 

WNOVI 993 

05JAN1995 

O5AUG I994 

03NOVI 992 

01 DECl992 

O2SEPl 994 

10DEC1993 

070CT1994 

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Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Cobalt 

Coban 

Coban 

Coban 

Cobalt 

Coban 

Cobalt 

Coban 

Coban 

Coban 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GClMS Scan 

GCMS Scan 

GCMS Scan 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

100-41-4 

100-41-4 

100-41-4 

100-41-4 

100-41-4 

100-41-4 

GClMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GClMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

12587-46-1 

1258746-1 

12587-46-1 

12587-46-1 

12587-46-1 

1258746-1 

12587-46-1 

1258746-1 

12587-46-1 

12581-46-1 

12587-46-1 

12587-46-1 

1258746-1 

12587-46-1 

12587-46-1 

12587-46-1 

2860-94 

287-94 

333-95 

506-94 

5510-92 

621 -93 

635-93 

801-93 

900-94 

1331-92 

1476-92 

1623-92 

1795-92 

1833-93 

1936-92 

2100-92 

333-95 

5510-92 

621-93 

1331-92 

1476-92 

1623-92 

1795-92 

1833-93 

1936-92 

2100-92 

333-95 

5510-92 

621-93 

1331-92 

1476-92 

1623-92 

1795-92 

1936-92 

2100-92 

1073-93 

1146-95 

1203-94 

1377-94 

1547-93 

18-94 

1837-93 

19-95 

2153-93 

219-95 

2412-94 

2690-94 

2860-94 

287-94 

436-95 

506-94 

632-95 

786-95 

900-94 

955-95 

1073-93 

1146-95 

1203-93 

1203-94 

1347-93 

1377-94 

1547-93 

1613-94 

18-94 

1833-93 

1837-93 

19-95 

1919-94 

2122-94 

2153-93 

219-95 

02DECI 994 

04FEB1994 

22FEB1995 

03MAR1994 

19AUG 1992 

O5MAY 1993 

O5MAY 1993 

02JUN1993 

08APR1994 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

1 ONOV1993 

03NOV1992 

01DEC1992 

22FEB1995 

19AUG1992 

OSMAY 1993 

06JUL1992 

O3AUG 1992 

31AUG1992 

070CT1992 

1 ONOVl993 

03NOV1992 

01DEC1992 

22FEBl995 

19AUG1992 

OSMAYl993 

06JUL1992 

03AUGl992 

31 AUG 1992 

070CT1992 

03NOV1992 

01DEC1992 

16JUL1993 

06JUL1995 

05MAY I 994 

03JUN1994 

050CT1993 

05JANl994 

04NOVI 993 

05JANl995 

1 ODECl993 

03FEB1995 

07OCT1994 

04NOV1994 

02DEC1994 

04FEB1994 

03MAR1995 

03MAR1994 

05APR1995 

03MAY 19% 

08APR1994 

01 JUN1995 

16JUL1993 

06JULl995 

OSAUG1993 

05MAY 1994 

02SEP1993 

03JUNl994 

050CTl993 

OlJULl994 

OSJANl994 

10NOV1993 

MNOV1993 

05JAN1995 

05AUG1994 

O2SEPl994 

lODEC1993 

03FEB1995 


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5.00E+W 

5.00E+00 

5.00E+W 

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O.WE+OO 

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O.OOE+W 

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O.OOE+W 

O.OOE+W 

O.OOE+OO 

O.OOE+W 

O.OOE+W 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+W 

l.OOE+W O.OOE+OO 

O.OOE+OO 1.00E-01 

5.WE+00 1.60E+00 

3.OOE+00 1.30E+00 

9.00E+00 2.70E+00 

1.00E+00 6.00E-01 

I.WE+OO 7.WE-01 

l.OOE+OO I .00E+00 

I.OOE+W 5.00E-01 

-3.00E+00 1.90E+00 

O.OOE+OO 1.00E-01 

O.WE+W 7.00E-01 

2.00E+00 2.20E+W 

3.OOE+00 2.40E+00 

2.00E+W 1.00E+00 

I .00E+00 6.00E-01 

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N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Q 

N 

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N 

N 

N 

N 

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Q 

Q 

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N 

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mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mg1L 

mg1L 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

WlL 

mglL 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ug1L 

uglL 

ug1L 

uglL 

ug1L 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ug/L 

uglL 

pCilL 

pCilL 

pCiL 

pCiL 

pCiL 

pCiL 

pCiL 

pCiL 

pciR 

pCiL 

pciR 

pCiL 

pciR 

pciR 

pCiL 

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Gross Alpha 12587-46-1 2412-94 070CT1994 WS 2.00E+00 l.OOE+OO PCVL 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Bela 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 































12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

1258747-2 

12587-47-2 

1258747-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

CAC03HARDNES 

CAC03HARDNES 

CACOJHARDNES 

CACO3HARDNES 

CAC03HARDNES 

CACOJHARDNES 

CACO3HARDNES 

CACOJHARDNES 

CACOJHARDNES 

CACO3HARDNES 

CACOJHARDNES 

CACOJHARDNES 

CACO3HARDNES 

CAC03HARDNES 

CACOIHARDNES 

CACO3HARDNES 

CACOJHARDNES 

CAC03HARDNES 

CACOJHARDNES 

CAC03HARDNES 

CAC03HARDNES 

CACO3HARDNES 

CACO3HARDNES 

CACO3HARDNES 

CACOJHARDNES 

18540-29-9 

18540-29-9 

18540-29-9 

18540-29-9 

18540-29-9 

2690-94 

2860-94 

287-94 

333-95 

436-95 

506-94 

6164-92 

632-95 

786-95 

801-93 

900-94 

955-95 

1073-93 

1146-95 

1203-93 

1203-94 

1347-93 

1377-94 

1547-93 

1613-94 

18-94 

1833-93 

1837-93 

19-95 

1919-94 

2122-94 

2153-93 

219-95 

2412-94 

2690-94 

2860-94 

287-94 

333-95 

436-95 

506-94 

6 164-92 

632-95 

786-95 

801 -93 

900-94 

955-95 

1073-93 

1203-93 

1203-94 

1347-93 

1377-94 

1547-93 

1613-94 

18-94 

1837-93 

19-95 

1919-94 

2122-94 

2153-93 

2 19-95 

2412-94 

2690-94 

2860-94 

287-94 

436-95 

506-94 

632-95 

786-95 

801-93 

900-94 

955-95 

19-95 

2 19-95 

436-95 

632-95 

786-95 

04NOV1994 

02DECl994 

04FEB1994 

22FEB1995 

03MAR1995 

03MAR1994 

llNOV1992 

(HAPR 1995 

03MAY 1995 

02JUN1993 

08APRl994 

01JUN1995 

16JULl993 

06JULl995 

OSAUG1993 

05MAY1994 

02SEP1993 

03JUN1994 

050CT1993 

OlJUL1994 

05JAN1994 

10NOV1993 

04NOV1993 

OSJAN1995 

OSAUG1994 

OZSEP1994 

10DEC1993 

03FEB1995 

070CT1994 

04NOV1994 

02DECl994 

04FEB1994 

22FEB1995 

03MARl995 

03MARl994 

1 1 NOVl992 

05APR1995 

03MAY1995 

02JUN1993 

08APR1994 

OlJUN1995 

16JUL1993 

05AUG 1993 

OSMAY 1994 

02SEP1993 

03JUN1994 

050CT1993 

OlJULl994 

WAN1994 

04NOV1993 

WAN1995 

OSAUGl994 

02SEPl994 

lODEC1993 

03FEBl995 

070CT1994 

04NOVl994 

02DECl994 

04FEB1994 

03MAR1995 

03MAR1994 

OSAPR1995 

03MAYl995 

02JUN1993 

08APR1994 

01JUNl995 

05JAN1995 

03FEB1995 

03MAR1995 

OSAPRl995 

OWY 1995 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

3.00E+00 1.70E+00 

l.OOE+OO 6.00E-01 

O.OOE+OO 4.00E-01 

1.00E+00 6.00E-01 

l.OOE+OO 6.00E-01 

O.OOE+OO 6.00E-01 


1.00E+00 8.00E-01 

l.OOE+OO 9.00E-01 

-1.00E+00 O.OOE+OO 

1.00€+00 6.00E-01 

l.OOE+OO 8.00E-01 

6,00E+00 l.OOE+OO 

7.00E+00 1.00E+00 

1.20E+01 2.00€+00 

7.00E+00 3.00E+00 

2.70€+01 3.00E+00 

7.00E+00 2.00E+00 

3.00€+00 l.OOE+OO 

2.OOE+Ol 6.00E+00 


4.00E+00 1.00€+00 

7.00E+00 l.OOE+W 

l.OOE+Ol 2.00E+00 

1.22E+02 5.80E+01 

1.70E+01 7.00E+00 

3.00E+00 l.OOE+OO 


l.lOE+Ol 3.00E+00 

8.00E+00 3.00E+00 


3.OOE+00 2.00E+00 

2.0OE+00 l.OOE+OO 

3.OOE+00 2.00E+00 


9.00E+00 

4.00E+00 1 .OCE+00 

3.00E+00 1.00E+00 

6.00E+00 l.OOE+OO 

4.00€+00 2.00E+00 

2.00E+00 0.00€+00 

1.44E+02 

2.62€+02 

7.20E+01 

3.68E+02 

1.36E+02 

9.70E+01 

1.98E+02 

7.40E+01 

7.20E+01 

9.40E+01 

5.62€+02 

1.09E+O3 

6.20E+01 

5.60E+01 

1.64E+02 

8.00E+01 

7.60E+01 

7.00E+01 

6.00€+01 

6.40E+01 

6.40€+01 


9.20€+01 

5.40€+01 

5.80E+01 

0.00€+00 

0.00E+00 

0.00E+00 

0.00E+00 

0.00€+00 

N 

N 

X 

N 

N 

N 

N 

N 

X 

N 

pCilL 

pCVL 

pciR 

pCVL 

pCilL 

pCVL 

pCVL 

pCVL 

pciR 

pCVL 

pCVL 

pCVL 

pCVL 

pCUL 

pCVL 

pCVL 

pCVL 

pCVL 

pCiL 

pCi 

pciR 

pCiL 

pCilL 

pCVL 

pCiL 

pCilL 

pCVL 

pcin 

pCiL 

pCilL 

pCilL 

pcin 

pcin 

pciR 

pCiL 

pCiL 

pCiL 

pciR 

pciR 

pCi 

pCiL 

mgR CaCO3 

mgR CaC03 

mglL CaC03 

mglL CaC03 

mglL CaCO3 

mgR CaC03 

mgfl CaC03 

mgR CaC03 

mg/L CaC03 

mglL CaC03 

mgR CaCO3 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mg/L CaCO3 

mglL CaCO3 

mglL CaC03 

mglL CaC03 

mglL CaCO3 

mg/L CaC03 

mglL CaC03 

mglL CaC03 

mgfl 

mgk 

mglL 

mgfl




Hexavalent Chromium 18540-29-9 955-95 01JUN1995 WS O.OOE+OO < N mglL 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439 - 89 - 6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439 - 89 - 6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

1073-93 

1203-93 

1203-94 

1331-92 

1347-93 

1377-94 

1476-92 

1547-93 

1613-94 

1623-92 

1795-92 

18-94 

1833-93 

1837-93 

19-95 

1919-94 

1936-92 

2100-92 

2122-94 

2153-93 

219-95 

2412-94 

2690-94 

2860-94 

287-94 

333-95 

436-95 

506-94 

5510-92 

621-93 

632-95 

635-93 

786-95 

801 -93 

900-94 

1073-93 

1203-93 

1203-94 

1331-92 

1347-93 

1377-94 

1476-92 

1547-93 

1613-94 

1623-92 

1795-92 

18-94 

1833-93 

1837-93 

19-95 

I91 9-94 

1936-92 

2100-92 

2122-94 

2153-93 

219-95 

2412-94 

2690-94 

2860-94 

287-94 

333-95 

43695 

506-94 

5510-92 

621-93 

632-95 

635-93 

786-95 

801 -93 

900-94 

955-95 

16JUL1993 

05AUG1993 

OBMAY1994 

06JULl 992 

02SEP1993 

03JUN1994 

03AUG1992 

050CT1993 

OlJUL1994 

31AUG1992 

070CT1992 

05JAN1994 

10NOV1993 

04NOV1993 

O5JANl995 

O5AUG 1994 

03NOV1992 

01 DEC1992 

02SEP1994 

10DECl993 

03FEBl995 

070CT1994 

04NOVl994 

02DECl994 

04FEBl994 

22FEBl995 

03MAR1995 

03MAR1994 

19AUG1992 

05MAY 1993 

05APR1995 

05MAY1993 

03MAYl995 

02JUNl993 

08APR1994 

16JUL1993 

05AUG1993 

(HMAY 1994 

06JUL1992 

02SEPl993 

03JUN1994 

03AUG1992 

050CT1993 

OlJULl994 

31 AUGl992 

070CT1992 

05JAN1994 

10NOV1993 

04NOVl993 

05JAN1995 

05AUGl994 

03NOV1992 

01 DEC1992 

02SEP1994 

10DEC1993 

03FEB1995 

070CT1994 

04NOVl994 

02DECl994 

04FEB1994 

22FEB1995 

03MAR1995 

03MARl994 

19AUG1992 

(HMAY 1993 

05APRl995 

05MAYI993 

03MAY 1995 

02JUN1993 

08APR1994 

01JUN1995 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

N 

N 

< 

< 

< 

< 

c 

< 

< 

c 

< 

< 

< 

< 

< 

< 

U 

< 

< 

< 

< 

< 

c 

c 

< 

U 

< 

U 

U 

< 

< 

< 

U 

< 

U 

< 

< 

U 

N 

N 

N 

N 

X 

N 

N 

X 

N 

N 

X 

N 

N 

X 

X 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

m& 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mg/L 

mgfl 

mglL 

mglL 

mgfl 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mg1L 

mglL 

mg/L 

mglL 

mglL 

mg5 

mglL 

mglL 

mglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

w/L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL



ANALYTE CAS NUMBER SAMPLE ID DATE TfPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Lithium 7439-93-2 1331 -92 06JUL1992 WS O.OOE+OO < N 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

743946-5 

1476-92 

1623-92 

1795-92 

1936-92 

2100-92 

5510-92 

621-93 

1073-93 

1203-93 

1203-94 

1331-92 

1347-93 

1377-94 

1476-92 

1547-93 

161 3-94 

1623-92 

1795-92 

18-94 

1833-93 

1837-93 

19-95 

191 9-94 

1936-92 

21 00-92 

2122-94 

21 53-93 

219-95 

2412-94 

2690-94 

2860-94 

287-94 

333-95 

436-95 

506-94 

5510-92 

62 1-93 

632-95 

635-93 

786-95 

801-93 

900-94 

1073-93 

1203-93 

1203-94 

1331 -92 

1347-93 

1377-94 

1476-92 

1547-93 

1613-94 

1623-92 

1795-92 

18-94 

1833-93 

1837-93 

19-95 

191 9-94 

1936-92 

21 00-92 

2122-94 

2153-93 

219-95 

2412-94 

2690-94 

2860-94 

287-94 

333-95 

436-95 

506-94 

5510-92 

O3AUGl 992 

3lAUGl992 

070CT1992 

03NOV1992 

01DEC1992 

19AUGl992 

05MAY 1993 

16JUL1993 

05AUG1993 

O5MAY 1994 

06JUL1992 

02SEP1993 

03JUNl994 

03AUGl992 

050CT1993 

01 JULl994 

31AUG1992 

070CT1992 

05JAN1994 

I ONOVl993 

04NOV1993 

05JAN1995 

05AUGl994 

03NOV1992 

01 DECI 992 

02SEP1994 

1 ODECI993 

O3FEB1995 

070CT1994 

04NOV1994 

02DEC1994 

04FEB1994 

22FEBl995 

03MAR1995 

03MAR1994 

19AUG1992 

(HMAY 1993 

05APRI995 

05MAY 1993 

03MAY1995 

02JUNI 993 

08APR1994 

16JUL1993 

OSAUG 1993 

05MAY 1 994 

06JULl992 

O2SEPl993 

03JUN1994 

03AUGl992 

050CT1993 

OIJUL1994 

31AUG1992 

070CT1992 

WAN1994 

1 ONOV1993 

04NOV1993 

05JAN 1995 

05AUG1994 

03NOV1992 

OlDEC1992 

O2SEPl994 

10DEC1993 

03FEB1995 

07OCT1994 

04NOVI994 

02DECl994 

04FEB1994 

22-81995 

03MAR1995 

03MAR1994 

19AUG1992 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

8.00E+00 

1.40E+01 


6.00E+00 

2.00E+01 

l.OOE+OI 

8.00E+00 


1.10E+01 

6.00E+00 



4.WE+W 

5.00E+W 

7.WE+W 

2.80E+01 



5.WE+01 

3.00E+00 


9.00E+00 

5.00E+00 

5.00E+W 





2.20E+01 

3.00E+W 


3.OOE+W 

3.WE+W 

5.WE+W 

3.WE+00 

I.WE+W 

8.WE+00 

O.WE+W 

1 .WE+00 

9.00E+00 

2.WE+W 

2.WE+00 

1 .OOE+W 

3.WE+W 

2.WE+W 

l.WE+W 

O.WE+W 

O.WE+OO 

O.WE+W 

l.WE+W 

1.40E+OI 

O.WE+W 

O.WE+W 

2.90E+01 

O.WE+OO 

O.WE+W 

3.WE+W 

I.WE+W 

O.WE+OO 

O.WE+W 

O.WE+W 

O.WE+W 

O.WE+W 

6.WE+00 

< N 

< N 

< N 

c 

N 

< N 

< N 

< N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N




Manganese 

7439-96-5 621-93 05MAY1993 WS O.OOE+OO N mg1L 

Manganese 

7439-96-5 

632-95 05APR1995 ws 

N 

Manganese 

7439-96-5 

635-93 O5MAY 1993 ws 

N 

Manganese 

7439-96-5 

786-95 O3MAY 1995 ws 

N 

Manganese 

7439-96-5 

801-93 02JUNl993 ws 

N 

Manganese 

7439 - 96 - 5 

900-94 OBAPR1994 ws 

N 

Mercury 

7439-97-6 

1331-92 06JUL1992 ws 

c 

N 

Mercury 

7439-97-6 

1476-92 O3AUG 1992 ws 

< 

N 

Mercury 

7439-97-6 

1547-93 050CT1993 ws 

< 

N 

Mercury 

7439-97-6 

1623-92 31 AUG 1992 ws 

< 

N 

Mercury 

7439-97-6 

1795-92 070CT1992 ws 

< 

N 

Mercury 

7439-97-6 

1833-93 10NOV1993 ws 

< 

N 

Mercury 

7439-97-6 

1936-92 03NOV1992 ws 

< 

N 

Mercury 

7439-97-6 

2100-92 01 DEC1992 ws 

< 

N 

Mercury 

7439-97-6 

333-95 22FEB1995 ws 

< 

N 

Mercury 

7439-97-6 

5510-92 19AUG 1992 ws 

UJ 

N 

Mercury 

7439-97-6 

621-93 O5MAY 1993 ws 

c 

NT 


75-09-2 

1347-93 02SEP1993 ws 

J 

N 

Molybdenum 

7439-98-7 

1331-92 06JUL1992 ws 

< 

N 

Molybdenum 

7439-98-7 

1476-92 03AUG1992 ws 

< 

N 

Molybdenum 

7439-98-7 

1623-92 31AUG1992 ws 

c 

N 

Molybdenum 

7439-98-7 

1795-92 070CT1992 ws 

c 

N 

Molybdenum 

7439-98-7 

1936-92 03NOV1992 ws 

< 

N 

Molybdenum 

7439-98-7 

2100-92 01DECl992 ws 

< 

N 

Molybdenum 

7439-98-7 

5510-92 19AUG 1992 ws 

< 

N 

Molybdenum 

7439-98-7 

621-93 05MAY 1993 ws 

< 

N 

Nickel 

7440-02-0 

1073-93 16JUL1993 ws 

< 

N 

Nickel 

7440-02-0 

1203-93 OSAUGl993 ws 

< 

N 

Nickel 

7440-02-0 

1203-94 05MAY 1994 ws 

< 

N 

Nickel 

7440-02-0 

1331-92 06JUL1992 ws 

< 

N 

Nickel 

7440-02-0 

1347-93 02SEP1993 ws 

< 

N 

Nickel 

7440-02-0 

1377-94 OjJUNl994 ws 

< 

N 

Nickel 

7440-02-0 

1476-92 03AUGl992 ws 

< 

N 

Nickel 

7440-02-0 

1547-93 050CTl993 ws 

< 

N 

Nickel 

7440-02-0 

1613-94 OlJUL1994 ws 

< 

N 

Nickel 

7440-02-0 

1623-92 3lAUGl992 ws 

< 

N 

Nickel 

7440-02-0 

1795-92 070CT1992 ws 

c 

N 

Nickel 

7440-02-0 i 8-94 OSJAN1994 ws 

< 

N 

Nickel 

7440-02-0 

1833-93 1 ONOV1993 ws 

c 

N 

Nickel 

7440-02-0 

1837-93 04NOV1993 ws 

< 

N 

Nickel 

7440-02-0 

19-95 05JAN1995 ws 

< 

N 

Nickel 

7440-02-0 

1919-94 05AUG1994 ws 

< 

N 

Nickel 

7440-02-0 

1936-92 03NOV1992 ws 

< 

N 

Nickel 

7440-02-0 

2100-92 01DEC1992 ws 

UJ 

N 

Nickel 

7440-02-0 

2122-94 02SEP1994 ws 

Nickel 

7440-02-0 

2153-93 1 ODEC1993 ws 



ANAL- CAS NUMBER SAMPLE ID DATE TYPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Phosphorus (P) 7723-14-0 1331 -92 06JUL1992 WS O.OOE+OO C 

N 

mglL 


7723-14-0 

1476-92 03AUGl992 ws O.OOE+OO 

c 

N 

mglL 


7723-14-0 

1623-92 3lAUGl992 ws O.OOE+OO 

N 

mglL 


7723-14-0 

1795-92 070CT1992 ws O.OOE+OO 

< N 

mglL 


7723-14-0 

1936-92 03NOV1992 ws O.OOE+OO 

< N 

mglL 


7723-14-0 

2100-92 

01 DEC1992 ws O.OOE+OO 

C 

N 

mglL 


7723-14-0 

5510-92 

19AUG 1992 ws O.OOE+OO 

< N 

mglL 


7723-14-0 

621-93 05MAY 1993 ws O.OOE+OO 

< N 

mglL 

Potassium 

7440-09-7 

1073-93 16JUL1993 ws 6.00E+00 

N 

mglL 

Potassium 

7440-09-7 

1203-93 05AUG1993 ws 7.00€+00 

N 

mglL 

Potassium 

7440-09-7 

1203-94 O5MAY 1994 ws 2.00E+00 

C 

N 

mglL 

Potassium 

7440-09-7 

1331-92 06JUL1992 ws 3.00E+00 

N 

mglL 

Potassium 

7440-09-7 

1347-93 02SEP1993 ws 8.00E+00 

N 

mglL 

Potassium 

7440-09-7 

1377-94 03JUN1994 ws 3.00E+00 

N 

mglL 

Potassium 

7440-09-7 

1476-92 03AUGl992 ws 4.00E+00 

N 

mglL 

Potassium 

7440-09-7 

1547-93 050CTl993 ws 4.00E+00 

N 

mg1L 

Potassium 

7440-09-7 

1613-94 01 JULl994 ws 6.00E+00 

N 

mglL 

Potassium 

7440-09-7 

1623-92 31AUG1992 ws 5.00E+00 

N 

mglL 

Potassium 

7440-09-7 

1795-92 070CT1992 ws 4.00E+W 

N 

mglL 

Potassium 

7440-09-7 

18-94 OSJANl994 ws 2.00E+00 

N 

mglL 

Potassium 

7440-09-7 

i 833-93 10NOV1993 ws 2.00€+00 

N 

mglL 

Potassium 

7440-09-7 

1837-93 04NOV1993 ws 4.00E+00 

N 

mglL 

Potassium 

7440-09-7 

19-95 OUANl995 ws 3.OOE+00 

N 

mglL 

Potassium 

7440-09-7 

1919-94 

OSAUG1994 ws l.OOE+Ol 

N 

mg1L 

Potassium 

7440-09-7 

1936-92 03NOV1992 ws 4.00E+00 

N 

mglL 

Potassium 

7440-09-7 

2100-92 OlDEC1992 ws 2.00E+00 

J 

N 

mglL 

Potassium 

7440-09-7 

2122-94 02SEPl994 ws 1.30E+01 

N mgk 

Potassium 

7440-09-7 

2153-93 lODECl993 ws 2.00E+00 

N 

mglL 

Potassium 

7440-09-7 

219-95 03FEBl995 ws 2.00E+00 

N 

mglL 

Potassium 

7440-09-7 

2412-94 070CT1994 ws 5.00E+00 

N 

mgfl 

Potassium 

7440-09-7 

2690-94 MNOV1994 ws 3.00E+W 

N mgk 

Potassium 

7440-09-7 

2a60-94 02DECl994 ws 4.WE+W 

N 

mglL 

Potassium 

7440-09-7 

287-94 MFEB1994 ws 2.00E+00 

N 

mglL 

Potassium 

7440-09-7 

333-95 22FEB1995 ws 2.00E+00 

N 

mglL 

Potassium 

7440-09-7 

436-95 OWR1995 ws 2.00E+00 

N 

mglL 

Potassium 

7440-09-7 

506-94 03MAR1994 ws 2.00E+00 

< 

N 

mglL 

Potassium 

7440-09-7 

5510-92 19AUG1992 ws 6.00E+W 

N 

mglL 

Potassium 

7440-09-7 

621-93 OWY 1993 ws 2.WE+00 

C 

N 

mglL 

Potassium 

7440-09-7 

632-95 OSAPR1995 ws 5.00E+00 

< 

N 

mglL 

Potassium 

7440-09-7 

635-93 05MAY1993 ws 2.00E+00 

< 

N 

mg/L 

Potassium 

7440-09-7 

786-95 03MAY 1995 ws l.OOE+OO 

N 

mglL 

Potassium 

7440-09-7 

801 -93 02JUNl993 ws 3.00E+00 

N mgk 

Potassium 

7440-09-7 

900-94 08APR1994 ws 2.00E+00 

< 

N 

mglL 

Rad Alpha 

12587-46-1 

1146-95 

WUL1995 ws l.OOE+OO 

< 

N pCiml 

Rad Alpha 

12587-46-1 

219-95 03FEB1995 ws 1 .00E+00 

c 

N pCiml 

Rad Alpha 

12587-46-4 

333-95 22FEB1995 ws l.OOE+W 

C 

N pCiml 

Rad Alpha 

12587-46-1 

436-95 03hMR1995 ws l.OOE+OO 

C 

N pCiml 

Rad Alpha 

ixa7-46-1 

632-95 OSAPRl995 ws l.OOE+W 

C 

N pCilml 

Rad Alpha i 2587-46-1 

7a6-95 03MAY 1995 ws 1 .WE+OO 

< 

N pCiml 

Rad Alpha 

i2sa7-46-i 

801-93 02JUN1993 ws l.WE+W 

< 

N pCimL 

Rad Alpha 

12587-46-1 

869-95 24MAY1995 ws 1 .00E+00 

c 

N pCiml 

Rad Alpha 

12587-46-1 

955-95 01 JUN1995 ws 1.00E+W 

C 

N pCilml 

Rad Beta 

12587-47-2 

1146-95 06JULl995 ws 1.00E+W 

C 

N pCilml 

Rad Beta 

12587-47-2 

219-95 03FEBl995 ws l.OOE+W 

< 

N pCilml 

Rad Beta 

12587-47-2 

333-95 22FEB1995 ws 1.00E+00 

< 

N pCiml 

Rad Beta 

12587-47-2 

436-95 OMARl995 ws l.WE+W 

< 

N pCiml 

Rad Beta 

12587-47-2 

632-95 OSAPR1995 ws 1 .00E+00 

C 

N pCilml 

Rad Beta 

12587-47-2 

786-95 03MAY 1995 

ws l.OOE+W 

C 

N pCilml 

Rad Beta 

~2587-47-2 

801-93 02JUNl993 ws 1.00E+00 

< 

N pCimL 

Rad Beta 

12587-47-2 

869-95 24MAY 1995 ws 1 .00E+00 

< 

N pCilml 

Rad Beta 

12587-47-2 

955-95 OlJUN1995 ws 1 .00E+00 

< 

N pCilml 

Ruthenium 

7440-188 

1331 -92 06JUL1992 ws 0.00E+00 

< 

N 

mgfl 

Ruthenium 

7440-188 

1476-92 03AUG1992 ws 0.00E+00 

< 

N mgk 

Ruthenium 

7440-10-0 

1623-92 3lAUGl992 ws 0.00E+00 

< 

N mgk 

Ruthenium 

7440-188 

1795-92 070CT1992 ws 0.00E+W 

< 

N Wfl 

Ruthenium 

7440-188 

193692 03NOV1992 ws 0.00E+00 

C 

N mgk 

Ruthenium 

7440-10-0 

2100-92 01 DEC1992 ws 0.00E+00 

< 

N mgk 

Ruthenium 

7440-ia-a 

5510-92 19AUG1992 ws O.WE+OO 

C 

N mgk 

Ruthenium 

7440-188 

621-93 OSMAY 1993 

ws 0.00E+00 

< 

N 

mglL 

Selenium 

7782-49-2 

1833-93 10NOV1993 ws 0.00E+00 

C 

N 

mglL 

Selenium 

7782-49-2 

333-95 22FEB1995 ws 0.00E+00 

CSX 

N mgfl 

Silicon 

7440-21-3 

1073-93 16JUL1993 ws 5.00E+W 

N mgk 

Page 48 of 176



DATE TYPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

ANALYTE CAS NUMBER SAMPLE ID 

Silicon 7440-2 1-3 1203-93 05AUG1993 WS 9.00E+00 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

7440-2 1-3 

7440-21-3 

7440-2 1-3 

7440-21-3 

7440-2 1 -3 

7440-21-3 

7440-21 -3 

7440-21 

-3 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-21-3 

7440-2 1-3 

7440-21-3 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-22-4 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

1203-94 

1331 -92 

1347-93 

1377-94 

1476-92 

1547-93 

1613-94 

1623-92 

1795-92 

18-94 

1837-93 

19-95 

191 9-94 

1936-92 

2100-92 

2153-93 

219-95 

2412-94 

2690-94 

2860-94 

287-94 

436-95 

506-94 

551 0-92 

62 1 -93 

632-95 

635-93 

786-95 

801 -93 

900-94 

1331-92 

1476-92 

1623-92 

1795-92 

1833-93 

1936-92 

21 00-92 

333-95 

5510-92 

621-93 

1203-93 

1203-94 

1331-92 

1347-93 

1377-94 

1476-92 

1547-93 

1623-92 

2122-94 

1073-93 

1613-94 

1795-92 

1837-93 

19-95 

191 9-94 

1936-92 

21 00-92 

18-94 

2122-94 

2153-93 

219-95 

2412-94 

2690-94 

2860-94 

287-94 

436-95 

506-94 

5510-92 

621-93 

635-93 

632-95 

05MAY1994 

06JULl992 

02SEP1993 

03JUNl994 

03AUGl992 

050CT1993 

OlJUL1994 

31AUG1992 

070CT1992 

05JAN1994 

04NOV1993 

05JAN1995 

OSAUG1994 

03NOV1992 

01 DECl992 

02SEP1994 

lODEC1993 

03FEB1995 

070CT1994 

04NOV1994 

02DECl994 

04FEB1994 

03MARl995 

03MAR1994 

19AUG1992 

05MAY1993 

05APR1995 

05MAY1993 

03MAY1995 

02JUN1993 

08APRl994 

06JUL1992 

03AUG1992 

3lAUGl992 

070CT1992 

1 ONOVl993 

03NOV1992 

01DEC1992 

22FEBl995 

19AUG 1992 

05MAYl993 

16JULl993 

OSAUG1993 

OSMAY 1994 

06JULl992 

02SEP1993 

03JUN1994 

03AUG1992 

050CT1993 

01 JULl994 

3lAUGl992 

070CT1992 

05JAN1994 

04NOV1993 

05JANl995 

OSAUG1994 

03NOV1992 

OlDEC1992 

02SEP1994 

lODEC1993 

O3FEBl995 

07OCT1994 

04NOV1994 

02DECl994 

04FEB1994 

03MAR1995 

OWR1994 

19AUG1992 

05MAY 1993 

OSAPR1995 

MAY 

1993 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

< 

X 

J 

B 

J 

< 

< 

< 

< 

< 

< 

< 




Sodium 

7440-23-5 786-95 O3MAY1995 WS 7.00E+00 J N 

mglL 

Sodium 

7440-23-5 

801-93 02JUNl993 ws 1.70E+01 

N 

mglL 

Sodium 

7440-23-5 

900-94 08APRl994 ws 8.00E+00 

N 

mglL 


1073-93 16JULl993 ws 3.82E+02 

N umhoslcm 


1146-95 

06JUL1995 ws 1.40E+02 

N umhodcm 


1203-93 05AUG1993 ws 6.06E+02 

N umhoslcm 


1203-94 05MAY 1994 

ws 2.11E+02 

N umhoslcm 


1347-93 02SEP1993 ws 7.05E+02 

N umhoslcm 


1377-94 03JUN1994 ws 4.00E+02 

N umhoslcm 


1547-93 050CT1993 ws 2.22E+02 

N urnhoslcm 


1613-94 OlJUL1994 ws 5.56E+02 

N umhoslcm 


18-94 05JAN1994 ws 2.25E+02 

N umhoslcm 


1837-93 04NOV1993 ws 2.54E+02 

N umhoslcm 


19-95 05JAN1995 ws 3.33E+02 

N umhoslcm 


1919-94 05AUG1994 ws 1.22E+03 

N 

urn hoslcm 


2122-94 O2SEPl994 ws 2.04E+03 

N umhoslcm 


2153-93 lODEC1993 ws 1.71 E+02 

N umhodcm 


219-95 03FEBl995 ws 1.96E+02 

N umhoslcm 


2412-94 070CTl994 ws 5.16E+02 

N umhoslcm 


2690-94 04NOV1994 ws 2.95E+02 

N umhoslcm 


SO145 

2860-94 02DEC1994 ws 2.46E+02 

N umhoslcm 


287-94 04FEB1994 ws 1.98E+02 

N umhoslcm 


SO145 

436-95 03MAR1995 ws 2.08€+02 

N umhoslcm 


SO145 

506-94 03MAR1994 ws 1.90E+02 

N umhoslcm 


SO145 

632-95 05APRl995 ws 2.49€+02 

N umhoslcm 


SO145 

78695 03MAY 1995 ws 1.38E+02 

N umhoslcm 


801-93 02JUN1993 ws 2.81E+02 

N umhodcm 


SO145 

900-94 08APRl994 ws 1.42E+02 

N umhoslcm 


SO145 

955-95 OlJUNl995 ws 1.94E+02 

N umhodcm 

Strontium 

7440-24-6 

1073-93 16JULl993 ws O.OOE+OO 

N 

mglL 

Strontium 

7440-24-6 

1203-93 05AUG1993 ws O.OOE+OO 

N 

mg1L 

Strontium 

7440-24-6 

1203-94 05MAY 1994 ws O.OOE+OO 

N 

mg/L 

Strontium 

7440-24-6 

1331 -92 06JUL1992 ws O.WE+W 

N 

mg/L 

Strontium 

7440-24-6 

1347-93 02SEPl993 ws O.OOE+OO 

N 

mg5 

Strontium 

7440-24-6 

1377-94 O3JUNl994 ws O.WE+W 

N 

mgfl 

Strontium 

7440-24-6 

147692 03AUG1992 ws O.OOE+W 

N 

mglL 

Strontium 

7440-24-6 

1547-93 050CTl993 ws O.WE+OO 

N 

mglL 

Strontium 

7440-24-6 

1613-94 01 JULl994 ws O.WE+OO 

N 

mglL 

Strontium 

7440-24-6 

1623-92 3lAUGl992 ws O.WE+W 

N 

mglL 

Strontium 

7440-24-6 

1795-92 070CT1992 ws O.WE+W 

N 

mglL 

Strontium 

7440-24-6 

16-94 WAN1994 ws O.WE+OO 

N 

mglL 

Strontium 

7440-24-6 

1837-93 04NOV1993 ws O.WE+OO 

N 

mg/L 

Strontium 

7440-24-6 

19-95 WAN1995 ws I.WE+W 

N 

mglL 

Strontium 

7440-24-6 

1919-94 05AUGl994 ws O.WE+OO 

N 

mglL 

Strontium 

7440-24-6 

193692 03NOV1992 ws O.WE+OO 

N 

mgfl 

Strontium 

7440-24-6 

2100-92 01DECl992 ws O.WE+OO 

N 

mgk 

Strontium 

7440-24-6 

2122-94 02SEPl994 ws 1 .WE+00 

N mgR 

Strontium 

7440-24-6 

2153-93 10DEC1993 ws O.OOE+W 

N 

mg/L 

Strontium 

7440-24-6 

219-95 03FEB1995 ws l.WE+W 

c 

N 

mglL 

Strontium 

7440-24-6 

2412-94 070CT1994 ws O.WE+OO 

N 

mglL 

Strontium 

7440-24-6 

2690-94 MNOV1994 ws O.WE+OO 

N 

mgfl 

Strontium 

7440-24-6 

2860-94 02DECl994 ws 3.WE+W 

< 

N 

mglL 

Strontium 

7440-24-6 

287-94 MFEBl994 ws O.WE+W 

N mgk 

Strontium 

7440-24-6 

43695 03MAR1995 ws l.WE+W 

c 

N 

mgk 

Strontium 

7440-24-6 

506-94 03MARl994 ws O.WE+OO 

N 

mglL 

Strontium 

7440-24-6 

5510-92 19AUG1992 ws O.OOE+W 

N 

mglL 

Strontium 

7440-24-6 

621-93 05MAY 1993 ws O.WE+W 

N 

mgfl 

Strontium 

7440-24-6 

632-95 05APRI995 ws O.WE+W 

N 

mglL 

Strontium 

7440-24-6 

635-93 05MAY1993 ws O.WE+OO 

N 

mglL 

Strontium 

7440-24-6 

78695 03MAY 19% ws O.WE+W 

N 

mglL 

Strontium 

7440-24-6 

801 -93 02JUNl993 ws O.OOE+OO 

N 

mglL 

Strontium 

7440-24-6 

900-94 08APR1994 ws O.WE+OO 

N mgk 

Sulfate 

12143-45-2 

1331-92 06JULl992 ws 5.3OE+01 

N 

mglL 

Sulfate 

12143-45-2 

147692 03AUG 1992 ws 1.24E+02 

N 

mgfl 

Sulfate 

12143-45-2 

1623-92 3lAUGl992 ws 6.80€+01 

N mgn 

Tantalum 

7440-25-7 

1331 -92 06JUL1992 ws O.WE+W 

N 

mgfl 

Tantalum 

7440-25-7 

1476-92 03AUG1992 ws O.WE+OO 

N 

mglL 

Tantalum 

7440-25-7 

1623-92 3lAUG1992 ws O.OOE+OO 

N 

mglL 

Tantalum 

7440-25-7 

1795-92 07OCT1992 ws O.WE+OO 

N 

mgfl 

Tantalum 

7440-25-7 

1936-92 03NOV1992 ws O.WE+W 

N 

mglL 

Tantalum 

7440-25-7 

5510-92 19AUGl992 ws O.WE+W 

N 

mgfl 

Tantalum 

7440-25-7 

621-93 OSMAY 1993 ws O.WE+W 

< 

N 

mglL 

Page 50 of 176




Technetium-99 14133-76-7 1833-93 10NOV1993 WS 3.00E+01 2.20E+01 N DCVL 

Technetium-99 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Tin 

Tin 

Tin 

Tin 

Tin 

Tin 

Tin 

Tin 

Ttanium 

Ttanium 

Titanium 

Ttanium 

Ttanium 

Titanium 

Titanium 

Titanium 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 










Trichbroethene 



Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

14133-76-7 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-31 -5 

7440-31-5 

7440-31-5 

7440-31 -5 

7440-31-5 

7440-31-5 

7440-31-5 

7440-31-5 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

108-88-3 

ioa-a8-3 

I 08-88-3 

108-88-3 

108-88-3 

108-88-3 

156-60-5 

156-60-5 

156-60-5 

15660-5 

156-60-5 

156-60-5 

79-01 -6 

79-01-6 

79-01-6 

79-01 -6 

79-01-6 

79-01-6 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-61-1 

7440-61-1 

7440-61 -1 

744061-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

744061-1 

6164-92 

1331-92 

1476-92 

1623-92 

1795-92 

1936-92 

2100-92 

5510-92 

621-93 

1331-92 

1476-92 

162392 

1795-92 

1936-92 

2100-92 

5510-92 

621-93 

1331-92 

1476-92 

1623-92 

1795-92 

1936-92 

2100-92 

5510-92 

621-93 

1331-92 

1476-92 

1623-92 

1795-92 

193692 

2100-92 

5510-92 

621-93 

1331 -92 

1476-92 

1623-92 

1795-92 

1936-92 

2100-92 

1331-92 

1476-92 

1623-92 

1795-92 

1936-92 

2100-92 

1331-92 

147692 

1623-92 

1795-92 

1936-92 

2100-92 

1331-92 

1476-92 

1623-92 

1795-92 

193692 

2100-92 

5510-92 

621-93 

1073-93 

1203-93 

1203-94 

1331-92 

1347-93 

1377-94 

1476-92 

1-7-93 

1613-94 

1623-92 

1795-92 

i a94 

llNOV1992 

O6JUL1 992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

01 DEC1992 

19AUG1992 

05MAY 1993 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

01 DEC1992 

19AUG1992 

O5MAY 1993 

06JUL1992 

03AUG1992 

3lAUGl992 

070CT1992 

03NOV1992 

01 DECl992 

19AUG 1992 

WAY1993 

06JUL1992 

03AUGl992 

31AUG1992 

O7OCTI 992 

03NOV1992 

OlDECl992 

19AUGl992 

OWAY 1993 

OGJULI 992 

O3AUGl 992 

31AUG1992 

070CT1992 

03NOV1992 

OlDECl992 

06JUL1992 

03AUG1992 

31 AUG 1992 

070CT1992 

03NOV1992 

01 DECl992 

06JUL1992 

03AUG1992 

3lAUGl992 

070CTI 992 

OJNOVl992 

01DEC1992 

06JUL1992 

03AUG1992 

31AUGl992 

070CT1992 

03NOV1992 

OlDEC1992 

19AUG1992 

WAY 1993 

16JUL1993 

05AUG1993 

(HMAY 1994 

06JUL1992 

02SEP1993 

03JUNl994 

03AUG1992 

050CT1993 

OlJULl994 

3lAUG 1992 

070CT1992 

05JANI 994 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

pC$L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

mg1L 

mgR 

mg1L 

mgfl 

mg/L 

mglL 

mgfl 

mgnmglL 

mg/L 

mgfl 

mglL 

uglL 

uglL 

ugR 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ugR 

uglL 

uglL 

uglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mgR 

mglL 

mglL 

m9fl 

mgR 

mglL 

mglL 

mgk 

mglL 

mglL 

mgn-




Uranium 7440-61-1 1833-93 10NOV1993 WS 0.00€+00 

c 

N 

mglL 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

7440-61-1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61-1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61-1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61-1 

7440-61 -1 

7440-61-1 

7440-61-1 

7440-61 -1 

7440-61 -1 

7440-61-1 

7440-61-1 

7440-61 -I 

7440-61-1 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

1837-93 

19-95 

1919-94 

1936-92 

2100-92 

2122-94 

2153-93 

219-95 

2412-94 

2690-94 

2860-94 

287-94 

333-95 

436-95 

506-94 

5510-92 

6164-92 

621-93 

632-95 

786-95 

801-93 

900-94 

955-95 

1331-92 

1476-92 

1623-92 

1936-92 

2100-92 

5510-92 

621-93 

1331-92 

1476-92 

1623-92 

1795-92 

1936-92 

2100-92 

1331-92 

1476-92 

1623-92 

1795-92 

1833-93 

1936-92 

2100-92 

333-95 

5510-92 

621-93 

1331 -92 

1476-92 

1623-92 

1795-92 

1936-92 

04NOV1993 

OSJANI 995 

05AUGl994 

03NOV1992 

01 DEC1992 

02SEP1994 

1 ODECl993 

03FEB1995 

070CT1994 

04NOV1994 

02DEC1994 

04FEBl994 

22FEB1995 

03MARl995 

03MAR 1994 

19AUGl992 

llNOV1992 

05MAY1993 

05APR1995 

03MAY 1995 

02 JUN 1993 

OBAPR1994 

01JUNl995 

06JUL1992 

03AUG1992 

3lAUG1992 

03NOV1992 

01 DEC1992 

19AUG1992 

WAY1993 

06JUL1992 

03AUG1992 

31 AUG 1992 

07OCT1992 

03NOV1992 

01 DECI 992 

06JUL1992 

03AUGl992 

3lAUGl992 

070CTI 992 

lONOV1993 

03NOV1992 

01DECl992 

22FEB1995 

19AUGI 992 

OSMAY 1993 

06JUL1992 

03AUG1992 

3IAUG1992 

070CT1992 

03NOV1992 

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O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

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O.OOE+OO 

O.OOE+OO 

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O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+W 

O.OOE+OO 

O.OOE+OO 

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O.OOE+W 

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O.OOE+OO 

O.WE+W 

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0.00E+W 

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I.WE+Ol 

1 .OOE+OI 

1 .WE+Ol 

l.WE+Ol 

I .WE+OI 

O.OOE+OO 

O.WE+W 

O.WE+W 

O.OOE+W 

O.WE+OO 

O.WE+W 

O.WE+W 

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N 

N 

N 

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N 

N 

N 

N 

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N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

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N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

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Zirconium 

Zirconium 

Zirconium 



cis-I .2dichloroethene 

cis-I ,2dichloroethene 


PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

7440-67-7 

7440-67-7 

7440-67-7 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

SO296 

SO296 

SO296 

SO296 

so296 

so296 

so296 

SO296 

so296 

so296 

so296 

so296 

2100-92 

5510-92 

621-93 

1203-93 

1347-93 

1613-94 

I91 9-94 

2122-94 

1073-93 

1146-95 

1203-93 

1203-94 

1266-92 

1308-92 

1331-92 

1347-93 

1368-92 

1377-94 

1417-92 

1443-92 

01DECl992 

19AUG1992 

OSMAY1993 

05AUGl993 

02SEPl993 

01 JULl994 

05AUGl994 

O2SEP1994 

16JUL1993 

06JUL1995 

05AUG1993 

05MAYl994 

22JUN1992 

29JUN1992 

06JUL1992 

02SEPl993 

13JUL1992 

OUUN1994 

21JULl992 

27JULl992 

0.00€+00 

O.WE+W 

O.WE+W 

3.WE+00 

3.WE+W 

3.00E+W 

9.WE+W 

7.WE+W 

7.00E+W 

7.00E+W 

7.00E+00 

7.WE+W 

7.WE+W 

7.WE+W 

7.WE+W 

7.WE+W 

7.WE+00 

7.WE+00 

7.WE+W 

7.00E+W 

e 

e 

Q 

J 

J 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

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ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

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ws 

ws 

ws 

ws 

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ws 

ws 

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ws 

ws 

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PH SO296 1476-92 03AUG1992 WS 7.00E+00 N su 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

WAG 7, SWU 8, C746K-4 
















1 .I-Dichloroelhene 





Acetone 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

67-64-1 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

1502-92 

1547-93 

1550-92 

1598-92 

1613-94 

1623-92 

1661 -92 

1683-92 

1795-92 

18-94 

1837-93 

19-95 

1919-94 

1966-92 

2100-92 

2122-94 

2136-92 

2153-93 

219-95 

2412-94 

2690-94 

2860-94 

287-94 

436-95 

506-94 

621 -93 

632-95 

635-93 

786-95 

801 -93 

900-94 

955-95 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

631-92 

700-92 

855-92 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

631 -92 

700-92 

855-92 

1839-93 

1023-92 

1074-93 

1143-92 

1204-93 

1204-94 

1332-92 

1348-93 

1378-94 

1477-92 

1548-93 

1614-94 

1624-92 

1796-92 

1839-93 

1840-93 

19-94 

1920-94 

10AUG1992 

050CT1993 

17AUG1992 

24AUG1992 

01 JULl994 

31AUG1992 

08SEPl992 

14SEP1992 

070CT1992 

05JAN1994 

04NOV1993 

OSJAN 1 995 

05AUG1994 

O9NOVI 992 

01 DECl992 

02SEPl994 

07DEC1992 

10DEC1993 

03FEB1995 

070CTI 994 

04NOV1994 

02DEC1994 

04FEB1994 

03MAR1995 

03MAR1994 

O5MAY 1993 

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05MAY1993 

03MAY 1995 

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OlJUN1995 

04MAY 1992 

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06JUL1992 

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31 AUG 1992 

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12MAR1992 

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01JUN1992 

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31AUG1992 

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01APR1992 

04NOV1993 

04MAY 1992 

16JULl993 

01JUN1992 

05AUG1993 

WAY1994 

06JUL1992 

02SEP1993 

03JUN1994 

03AUG1992 

050CT1993 

OlJULl994 

31 AUGI 992 

070CT1992 

04NOV1993 

04NOV1993 

05JAN1994 

05AUG1994 


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ws 

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NT 

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N 

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N 

N 

N 

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N 

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mglL 

mglL 

mglL 

mglL 

mglL 

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Aluminum 7429-90-5 1937-92 03NOV1992 WS l.OOE+OO N 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminurn 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminurn 

Aluminurn 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Barium 

Barium 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

1440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-30-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-30-2 

7440-38-2 

7440-39-3 

7440-39-3 

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2 154-93 

220-95 

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2691-94 

2692-94 

2861-94 

288-94 

437-95 

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622-93 

631-92 

633-95 

636-93 

700-92 

787-95 

802-93 

855-92 

901-94 

1023-92 

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1624-92 

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2861-94 

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05JAN1995 

O2SEPl 994 

10DEC1993 

03FEB1995 

070CT1994 

04NOV1994 

04NOV1994 

02DECl994 

04FEBI 994 

03MAR1995 

03MAR1994 

OSMAY 1993 

05MAR1992 

O5APR 1995 

05MAY 1 993 

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03MAY 1995 

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04MAY 1992 

01 JUN1992 

06JUL1992 

03AUG1992 

31 AUG 1992 

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WAR1992 

12MAR1992 

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04MAY 1992 

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06JUL1992 

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03JUNI994 

03AUG1992 

050CT1993 

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3lAUG1992 

070CT1992 

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04NOV1993 

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03NOVl992 

05JAN1995 

02SEP1994 

IODECI993 

03FEB1995 

070CT1994 

MNOV1994 

MNOV1994 

02DEC1994 

MFEBl994 

03MAR1995 

OW1994 

05MAY1993 

MMAR1992 

OSAPRI995 

05MAY1993 

12MAR1992 

03MAY1995 

02JUN1993 

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08APR1994 

04MAY 1 992 

16JUL1993 

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< 

< 

c 

< 

c 

c 

c 

< 

< 

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< 

< 

c 

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< 

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< 

< 

< 

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CS 

c 

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Barium 7440-39-3 1143-92 01JUN1992 WS O.OOE+OO N mglL 

Barium 

7440-39-3 

1204-93 05AUGl993 ws 

N 

mglL 

Barium 

7440-39-3 

1204-94 O5MAY 1994 ws 

N 

mglL 

Barium 

7440-39-3 

1332-92 06JUL1992 ws 

N 

mglL 

Barium 

7440-39-3 

1348-93 02SEP1993 ws 

N. mglL 

Barium 

7440-39-3 

1378-94 03JUN1994 ws 

N 

mglL 

Barium 

7440-39-3 

1477-92 03AUG1992 ws 

N 

mglL 

Barium 

7440-39-3 

1548-93 050CT1993 ws 

N 

mglL 

Barium 

7440-39-3 

1614-94 

01 JUL1994 ws 

N 

mglL 

Barium 

7440-39-3 

1624-92 31AUG1992 ws 

N 

mglL 

Barium 

7440-39-3 

1796-92 070CT1992 ws 

N 

mg1L 

Barium 

7440-39-3 

1839-93 MNOV1993 ws 

N 

mglL 

Barium 

7440-39-3 

1840-93 04NOV1993 ws 

N 

mglL 

Barium 

7440-39-3 

19-94 05JANl994 ws 

N 

mglL 

Barium 

7440-39-3 

1920-94 05AUG1994 ws 

N 

mglL 

Barium 

7440-39-3 

1937-92 03NOV1992 ws 

N 

mglL 

Barium 

7440-39-3 

20-95 05JAN1995 ws 

< 

N 

mglL 

Barium 

7440-39-3 

2123-94 02SEP1994 ws 

N 

mglL 

Barium 

7440 - 39 - 3 

2154-93 1 ODECl993 ws 

N 

mglL 

Barium 

7440-39-3 

220-95 03FEB1995 ws 

N 

mglL 

Barium 

7440-39-3 

2413-94 070CT1994 ws 

N 

mglL 

Barium 

7440-39-3 

2691-94 04NOV1994 ws 

N 

mglL 

Barium 

7440-39-3 

2692-94 04NOV1994 ws 

N 

mglL 

Barium 

7440-39-3 

2861-94 02DECl994 ws 

N 

mglL 

Barium 

7440-39-3 

268-94 MFEB1994 ws 

N 

mglL 

Barium 

7440-39-3 

437-95 03MARl995 ws 

N 

mglL 

Barium 

7440 - 39 - 3 

507-94 03MARl994 ws 

N 

mg1L 

Barium 

7440-39-3 

622-93 05MAYl993 ws 

N 

mglL 

Barium 

7440-39-3 

631-92 OSMAR1992 ws 

N 

mglL 

Barium 

7440-39-3 

633-95 05APR1995 ws 

c 

N 

mglL 

Barium 

7440-39-3 

636-93 05MAYl993 ws 

N 

mglL 

Barium 

7440-39-3 

700-92 12MAR1992 ws 

N 

mglL 

Barium 

7440-39-3 

787-95 03MAY 1995 ws 

< 

N 

mglL 

Barium 

7440-39-3 

802-93 02JUNl993 ws 

N 

WlL 

Barium 

7440-39-3 

855-92 01APRl992 ws 

N 

mglL 

Barium 

7440-39-3 

901-94 08APR1994 ws 

N 

mg1L 

Benzene 

71-43-2 

1023-92 MMAY 1992 ws 

< 

NT 

ug1L 

Benzene 

71-43-2 

1143-92 

01 JUN1992 ws 

< 

N 

uglL 

Benzene 

71 -43-2 

1332-92 oGJUL1992 ws 

< 

N 

uglL 

Benzene 

71-43-2 

1477-92 03AUG1992 ws 

< 

N 

uglL 

Benzene 

71-43-2 

1624-92 31AUG1992 ws 

< 

N 

uglL 

Benzene 

71 -43-2 

1796-92 070CT1992 ws 

< 

N 

uglL 

Benzene 

71 -43-2 

1937-92 03NOVl992 ws 

< 

N 

uglL 

Benzene 

71-43-2 

631-92 05MAR1992 ws 

c 

N 

uglL 

Benzene 

71-43-2 

700-92 12MARl992 ws 

< 

N 

uglL 

Benzene 

71-43-2 

855-92 01 APR1992 ws 

< 

N 

uglL 

Beryllium 

7440-41-7 

1023-92 WAY1992 ws 

< 

NT mg1L 

Beryllium 

7440-41-7 

1143-92 

01 JUNl992 ws 

< 

N 

mglL 

Beryllium 

7440-41-7 

1332-92 oGJUL1992 ws 

< 

N 

mglL 

Beryllium 

7440-41 -7 

1477-92 03AUGl992 ws 

< 

N 

mglL 

Beryllium 

7440-41 -7 

1624-92 31AUGl992 ws 

< 

N 

mglL 

Beryllium 

7440-41-7 

1796-92 070CT1992 ws 

c 

N 

WlL 

Beryllium 

7440-41-7 

1937-92 03NOV1992 ws 

< 

N 

WlL 

Beryllium 

7440-41-7 

622-93 OCMAY 1993 ws 

< 

N 

WlL 

Beryllium 

7440-41-7 

631-92 05MAR1992 ws 

< 

N 

mglL 

Beryllium 

7440-41-7 

700-92 1 ZMAR 1992 ws 

< 

N 

WlL 

Beryllium 

7440-41 -7 

855-92 01 APR1992 ws 

< 

N 

mglL 

Bismuth 

7440-69-9 

1023-92 WAY 1992 ws 

< 

NT WlL 

Bismuth 

7440-69-9 

1143-92 01 JUN1992 ws 

c 

N WlL 

Bismuth 

7440-69-9 

1332-92 oGJUL1992 ws 

< 

N 

mglL 

Bismuth 

7440-69-9 

1477-92 OJAUGl992 ws 

< 

N 

mglL 

Bismuth 

7440-69-9 

1624-92 31 AUG 1992 ws 

< 

N 

W/L 

Bismuth 

7440-69-9 

1796-92 070CT1992 ws 

< 

N 

mglL 

Bismuth 

7440-69-9 

1937-92 03NOV1992 ws 

< 

N 

mglL 

Bismuth 

7440-69-9 

622-93 05MAY1993 ws 

< 

N 

mglL 

Bismuth 

7440-69-9 

631-92 [HMAR 1992 

ws 

c 

N 

mglL 

Bismuth 

7440-69-9 

700-92 12MAR1992 ws 

< 

N 

mgR 

Bismuth 

7440-69-9 

855-92 OlAPRl992 ws 

c 

N 

mglL 

Cadmium 

7440-43-9 

1023-92 MMAY 1992 ws 

< 

NT mglL 

Cadmium 

7440-43-9 

1074-93 16JUL1993 ws 

c 

N 

mglL 

Cadmium 

7440-43-9 

1143-92 

01JUN1992 ws 

< 

N mgk 

Cadmium 

7440-43-9 

1204-93 [HAUG 1993 ws 

< 

N 

mg/L 

Page 55 of 176



Cadmium 7440-43-9 1204-94 OSMAYl994 WS O.OOE+OO C N mglL 

Cadmium 

7440-43-9 

1332-92 06JULl992 ws 

C 

N 

mg1L 

Cadmium 

7440-43-9 

1348-93 02SEP1993 ws 

c 

N 

mglL 

Cadmium 

7440-43-9 

1378-94 03JUN1994 ws 

< N 

mglL 

Cadmium 

7440-43-9 

1477-92 O3AUG 1992 ws 

C 

N 

mglL 

Cadmium 

7440-43-9 

1548-93 050CT1993 ws 

< N 

mglL 

Cadmium 

7440-43-9 

1614-94 01 JUL1994 ws 

C 

N 

mglL 

Cadmium 

7440-43-9 

1624-92 31 AUGl992 ws 

< N 

mglL 

Cadmium 

7440-43-9 

1796-92 070CT1992 ws 

< N 

mglL 

Cadmium 

7440-43-9 

1839-93 04NOV1993 ws 

< N 

mglL 

Cadmium 

7440-43-9 

1840-93 04NOV1993 ws 

< N 

mglL 

Cadmium 

7440-43-9 

19-94 05JAN1994 ws 

c 

N 

mglL 

Cadmium 

7440-43-9 

1920-94 05AUG1994 ws 

< N 

mglL 

Cadmium 

7440-43-9 

1937-92 03NOV1992 ws 

< N 

mglL 

Cadmium 

7440-43-9 

20-95 O5JANl 995 ws 

U 

N 

mglL 

Cadmium 

7440-43-9 

2123-94 02SEP1994 ws 

< N 

mglL 

Cadmium 

7440-43-9 

2154-93 10DEC1993 ws 

C 

N 

mgfl 

Cadmium 

7440-43-9 

220-95 O3FEBl 995 ws 

C 

N 

mglL 

Cadmium 

7440-43-9 

2413-94 070CT1994 ws 

< N 

mglL 

Cadmium 

7440-43-9 

2691-94 04NOV1994 ws 

C 

N 

WlL 

Cadmium 

7440-43-9 

2692-94 04NOV1994 ws 

C 

N 

mglL 

Cadmium 

7440-43-9 

2861 -94 02DEC1994 ws 

U 

N 

mg/L 

Cadmium 

7440-43-9 

288-94 04FEB1994 ws 

C 

N 

mg1L 

Cadmium 

7440-43-9 

437-95 03MAR1995 ws 

U 

N 

mglL 

Cadmium 

7440-43-9 

507-94 03MAR1994 ws 

< N 

mglL 

Cadmium 

7440-43-9 

622-93 05MAY 1993 ws 

N 

mglL 

Cadmium 

7440-43-9 

631-92 OSMARI 992 ws 

C 

N 

mg5 

Cadmium 

7440-43-9 

633-95 OSAPR1995 ws 

U 

N 

wlL 

Cadmium 

7440-43-9 

636-93 05MAY1993 ws 

< N 

mg/L 

Cadmium 

7440-43-9 

700-92 12MARl992 ws 

C 

N 

wlL 

Cadmium 

7440-43-9 

787-95 03MAY 1995 ws 

C 

N 

mglL 

Cadmium 

7440-43-9 

802-93 O2JUNl 993 ws 

< N 

mglL 

Cadmium 

7440-43-9 

855-92 01 APRl992 ws 

C 

N 

mglL 

Cadmium 

744043-9 

901 -94 08APRl994 ws 

c 

N 

mglL 

Cadmium 

7440-43-9 

956-95 01 JUN1995 ws 

C 

N 

mg/L 

Calcium 

7440-70-2 

1023-92 04MAY 1992 ws 

NT mglL 

Calcium 

7440-70-2 

1143-92 01JUNl992 ws 

N 

mglL 

Calcium 

7440-70-2 

1332-92 06JUL1992 ws 

N 

mglL 

Calcium 

7440-70-2 

1477-92 03AUGl992 ws 

N 

mglL 

Calcium 

7440-70-2 

1624-92 31 AUG1992 ws 

N 

mglL 

Calcium 

7440-70-2 

1796-92 070CT1992 ws 

N 

mglL 

Calcium 

7440-70-2 

1937-92 03NOV1992 ws 

N 

mglL 

Calcium 

7440-70-2 

622-93 05MAY 1993 ws 

N w5 

Calcium 

7440-70-2 

631-92 05MAR1992 ws 

N 

mglL 

Calcium 

7440-70-2 

700-92 12MAR1992 ws 

N 

mglL 

Calcium 

7440-70-2 

855-92 01 APRl992 ws 

N 

wlL 

Chromium 

7440-47-3 

1023-92 04MAY 1992 ws 

C 

NT mg1L 

Chromium 

7440-47-3 

1074-93 16JUL1993 ws 

C 

N 

mg5 

Chromium 

7440-47-3 

1143-92 01 JUN1992 ws 

C 

N 

WlL 

Chromium 

7440-47-3 

1204-93 OSAUG 1993 ws 

< 

N 

wlL 

Chromium 

7440-47-3 

1204-94 MAY 1994 ws 

< 

N 

wlL 

Chromium 

7440-47-3 

1332-92 06JUL1992 ws 

< 

N 

mglL 

Chromium 

7440-47-3 

1348-93 02SEP1993 ws 

C 

N 

mglL 

Chromium 

7440-47-3 

1378-94 OUUN1994 ws 

C 

N 

mglL 

Chromium 

7440-47-3 

1477-92 03AUG1992 ws 

N 

WlL 

Chromium 

7440-47-3 

1548-93 050CT1993 ws 

N 

mglL 

Chromium 

7440-47-3 

1614-94 OlJUL1994 ws 

N 

mglL 

Chromium 

7440-47-3 

1624-92 31AUGI 992 ws 

N 

mg5 

Chromium 

7440-47-3 

1796-92 070CT1992 ws 

N 

mglL 

Chromium 

7440-47-3 

1839-93 04NOVI993 ws 

< 

N 

mgfL 

Chromium 

7440-47-3 

1840-93 04NOVI993 ws 

N 

mg5 

Chromium 

7440-47-3 

19-94 WAN 1994 

ws 

N 

mg5 

Chromium 

7440-47-3 

1920-94 (HAUGI994 ws 

N 

mglL 

Chromium 

7440-47-3 

1937-92 03NOVl 992 ws 

N 

mglL 

Chromium 

7440-47-3 

20-95 (HJ AN 1995 ws 

N 

mg5 

Chromium 

7440-47-3 

2123-94 02SEP1994 ws 

N 

w/L 

Chromium 

7440-47-3 

2154-93 lODEC1993 ws 

< 

N 

mg5 

Chromium 

7440-47-3 

2413-94 070CT1994 ws 

< 

N 

mglL 

Chromium 

7440-47-3 

2691-94 04NOV1994 ws 

C 

N 

mglL 

Chromium 

744047-3 

2692-94 04NOV1994 ws 

C 

N 

mg1L 

Chromium 

7440-47-3 

2861-94 02DEC1994 ws 

U 

N 

mg5 

Chromium 

7440-47-3 

288-94 04FEB1994 ws 

< 

N mgR 

Page 56 of 176




Chromium 7440-47-3 507-94 03MAR1994 WS O.OOE+OO 

C 

N 

mglL 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Cobalt 

Cobalt 

Coban 

Cobalt 

Cobalt 

Cobalt 

Cobalt 

Cobalt 

Cobalt 

Coban 

Cobalt 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

GCNS Scan 

GCNS Scan 

GCMS Scan 

GCMS Scan 

GCNS Scan 

GCMS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

100-41-4 

10041-4 

100-41-4 

100-41-4 

100-41-4 

100-41-4 

100-41-4 

100-41-4 

10041-4 

100-41-4 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCMS SCAN 

GCMS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCMS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

12587-46-1 

12587-46-1 

I 2587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

622-93 

631 -92 

636-93 

700-92 

802-93 

855-92 

901-94 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

622-93 

631-92 

700-92 

855-92 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

622-93 

631 -92 

700-92 

855-92 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

631-92 

700-92 

855-92 

1074-93 

1147-95 

1204-93 

1204-94 

1378-94 

1548-93 

1614-94 

1840-93 

19-94 

1920-94 

20-95 

2123-94 

2154-93 

220-95 

2413-94 

2691-94 

2692-94 

2861-94 

288-94 

437-95 

507-94 

633-95 

787-95 

901-94 

956-95 

1074-93 

1147-95 

1204-93 

1204-94 

138-93 

1378-94 

1548-93 

O5MAY 1993 

O5MARl 992 

05MAY1993 

12MAR1992 

02JUN1993 

01 APRl992 

08APR1994 

04MAYl992 

01 JUN1992 

06JULl 992 

O3AUG 1992 

3lAUGl992 

070CT1992 

03NOV1992 

O5MAY1 993 

05MAR1992 

12MARl992 

01 APRl992 

WMAY 1992 

01JUN1992 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

05MAY1993 

O5MARl992 

12MAR1992 

01 APRI 992 

04MAY 1992 

01 JUN1992 

06JUL1992 

03AUG1992 

3IAUG 1992 

070CT1992 

03NOV1992 

05MAR1992 

12MAR1992 

01 APRI 992 

16JUL1993 

06JUL1995 

05AUG1993 

05MAY 1994 

03JUN1994 

050CT1993 

OlJUL1994 

04NOVI993 

OSJAN 1994 

05AUG1994 

05JAN1995 

02SEP1994 

10DEC1993 

O3FEB1995 

070CT1994 

04NOV1994 

04NOV1994 

02DEC1994 

04FEB1994 

03MAR1995 

03MAR1994 

05APR1995 

03MAY 1995 

08APR1994 

01JUN1995 

16JULl993 

06JUL1995 

05AUGI 993 

05MAY 1994 

02SEP1993 

03JUN1994 

050CT1993 

c 

c 

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c 

c 

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< 

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c 

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c 

c 

c 

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c 

C 

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C 

c 

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V 

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N 

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N 

N 

N 

N 

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N 

N 

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N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

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N 

N 

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N 

N 

N 

N 

N 

N 

N 

N 

N 

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Q 

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N 

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mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

rnglL 

rnglL 

mg1L 

mglL 

rnglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

rnglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

rnglL 

mg1L 

mglL 

mglL 

mgk 

mglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

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uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

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uglL 

uglL 

uglL 

uglL 

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ws 

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ws 

ws 

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ws 

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ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws




Gross Alpha I 2587-46-1 1614-94 OlJUL1994 WS -I.OOE+OO 6.00E-01 pCYL 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 
























i 2587-46-1 

12507-46-1 

12587-46-1 

12507-46-1 

12507-46-1 

12507-46-1 

12587-46-1 

12507-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12507-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12507-46-1 

12507-46-1 

12587-46-1 

12507-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12587-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12587-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12587-47-2 

12587-47-2 

CACOJHARDNES 

CACOBHARDNES 

CACOJHARDNES 

CAC03HARDNES 

CACOBHARDNES 

CAC03HARDNES 

CAC03HARDNES 

CACOJHARDNES 

CACOJHARDNES 

CAC03HARDNES 

CACOJHARDNES 

CAC03HARDNES 

CACOJHARDNES 

CACOJHARDNES 

CACOJHARDNES 

CACOJHARDNES 

CACOJHARDNES 

CACOJHARDNES 

CACOJHARDNES 

CACOJHARDNES 

CAC03HARDNES 

CACOJHARDNES 

CACOJHARDNES 

1839-93 

1040-93 

19-94 

1920-94 

20-95 

2123-94 

2154-93 

220-95 

2413-94 

2691-94 

2692-94 

2061-94 

288-94 

437-95 

507-94 

633-95 

707-95 

002-93 

901-94 

956-95 

1074-93 

1147-95 

1204-93 

1204-94 

I 348-93 

1378-94 

1548-93 

1614-94 

1839-93 

1840-93 

19-94 

1920-94 

20-95 

2123-94 

2154-93 

220-95 

2413-94 

2691-94 

2692-94 

2061-94 

288-94 

437-95 

507-94 

633-95 

787-95 

802-93 

901-94 

956-95 

1074-93 

1204-93 

1204-94 

1348-93 

1378-94 

1548-93 

1614-94 

1039-93 

1840-93 

19-94 

1920-94 

20-95 

2123-94 

2154-93 

220-95 

2413-94 

2691-94 

2692-94 

2061-94 

280-94 

437-95 

507-94 

633-95 

04NOV1993 

04NOV1993 

05JAN1994 

O5AUGl 994 

O5JANl 995 

02SEP1994 

10DEC1993 

03FEB1995 

070CT1994 

04NOV1994 

04NOV1994 

02DECl994 

04FEB1994 

O3MAR 1995 

03MAR1994 

05APRl995 

O3MAY 1995 

02JUNl993 

08APRl994 

OlJUN1995 

16JUL1993 

06JULl995 

05AUGl993 

05MAY1994 

02SEPl993 

03JUNl994 

05OCTI 993 

01 JUL1994 

04NOV1993 

04NOV1993 

05JAN1994 

05AUG1994 

WAN1995 

02SEP1994 

10DEC1993 

03FEB1995 

070CT1994 

04NOVl994 

04NOV1994 

02DECl994 

04FEB1994 

03MAR1995 

03MAR1994 

05APR1995 

03MAY 1995 

02JUNl993 

08APRl994 

01JUNl995 

I6JUL1993 

05AUGl993 

OSMAY 1994 

02SEP1993 

OUUNI 994 

05OCTl993 

01 JUL1994 

04NOV1993 

04NOV1993 

05JAN1994 

05AUGl994 

WAN1995 

02SEPl994 

I ODEC 1993 

03FEB1995 

070CT1994 

04NOVl994 

04NOV1994 

OZDECl994 

MFEBl994 

03MARI 995 

03MARl994 

05APRl995 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

-1.00E+00 7.00E-01 


-l.OOE+OO 5.00E-01 

1.00E+00 7.00E-01 

O.OOE+OO 7.00E-01 

1.00E+00 7.00E-01 

2.00E+00 9.00E-01 

2.00E+00 1.40E+00 

l.OOE+OO 6.00E-01 

1.00E+00 7.00E-01 

1.00E+00 7.00E-01 

1.00E+00 7.00E-01 

O.OOE+OO 5.00E-01 

1.00E+00 6.00E-01 

1.00E+00 7.00E-01 

2.00E+00 1.20E+00 

1.00E+00 6.00E-01 

-l.OOE+OO O.OOE+OO 

1.00€+00 7.00E-01 

-2.00E+00 -1.90E+00 

4.00€+00 l.OOE+OO 

7.00E+00 l.OOE+OO 


1.00E+01 3.00E+00 


7.00E+00 2.00E+00 

3,OOE+00 1 .OOE+OO 

1.00E+01 3.OOE+00 

1.20E+01 2.00E+00 

7.00E+00 l.OOE+OO 

7.00E+00 l.OOE+OO 

1.20E+01 3.00E+00 


6.00E+00 2.00E+00 

5.00E+00 l.OOE+OO 

6.00E+00 2.00E+00 

6.00E+00 2.00E+00 

0.00E+00 3.00E+00 

6.00E+00 2.00E+00 

6.00E+00 3.00E+00 

9.00E+00 2.00E+00 


5.00E+00 2.00E+00 


5.00E+00 1.00E+00 

5.00E+00 1.00E+00 

9.00E+00 2.00E+00 

7.00E+00 1.00E+00 

6.00E+OI 

7.20E+01 

6.00E+01 

5.60E+01 

6.20E+01 

7.40E+01 

5.60E+01 

6.70E+01 

6.70E+01 

7.00E+01 


6.00E+01 

7.00E+01 

5.00E+01 

6.20E+OI 

7.30E+OI 

6.00E+01 

7.20E+01 

6.00E+Ol 

7.00E+Ol 

6.00E+01 

7.80E+01 

6.00E+01 

N 

N 

N 

N 

N 

X 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCVL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCilL 

pciR 

pCYL 

pciR 

pCYL 

pCiL 

pCiL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCYL 

pCiR 

pCYL 

pCi 

pcin 

pCi 

pcin 

pCi 

pCi 

mglL CaC03 

mglL CaCO3 

mgR CaC03 

mgR CaC03 

mglL CaC03 

mglL CaC03 

mgR CaCO3 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mgR CaCO3 

mglL CaCO3 

mgR CaCO3 

mgR CaCO3 

mgR CaC03 

mgR CaCO3 

mgR CaC03 

mglL CaCO3 

mgR CaCO3 

mgR CaC03 

mglL CaCO3 

mgR CaC03 

mglL CaC03




Hardness as CaC03 CAC03HARDNES 787-95 03MAY1995 WS 4.60E+01 X mglL CaC03 










Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

CACOJHARDNES 

CACOJHARDNES 

CACOJHARDNES 

18540-29-9 

18540-29-9 

18540-29-9 

18540-29-9 

18540-29-9 

18540-29-9 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7 4 3 9 - 8 9 - 6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

802-93 

901-94 

956-95 

20-95 

220-95 

437-95 

633-95 

787-95 

956-95 

1023-92 

1074-93 

1143-92 

1204-93 

1204-94 

1332-92 

1348-93 

1378-94 

1477-92 

1548-93 

1614-94 

1624-92 

1796-92 

1839-93 

1840-93 

19-94 

1920-94 

1937-92 

20-95 

2123-94 

2154-93 

220-95 

2413-94 

2691-94 

2692-94 

2861-94 

288-94 

437-95 

507-94 

622-93 

631-92 

633-95 

636-93 

700-92 

787-95 

802-93 

855-92 

901-94 

1023-92 

1074-93 

1143-92 

1204-93 

1204-94 

1332-92 

1348-93 

1378-94 

1477-92 

1548-93 

1614-94 

1624-92 

1796-92 

1839-93 

1840-93 

19-94 

1920-94 

1937-92 

20-95 

2123-94 

2154-93 

220-95 

2413-94 

2691-94 

02 JUNl993 

08APR1994 

01JUN1995 

05JAN1995 

03FEB1995 

03MAR1995 

05APR 1995 

03MAY1995 

01 JUN1995 

04MAY 1992 

16JUL1993 

01JUN1992 

OSAUGl993 

05MAY 1994 

O6JUL1 992 

02SEP1993 

03JUN1994 

03AUG 1992 

050CT1993 

01 JUL1994 

3lAUG1992 

070CT1992 

04NOV1993 

04NOV1993 

05JANl994 

05AUG1994 

03NOV1992 

OSJANl995 

02SEP1994 

lODECl993 

03FEB1995 

070CT1994 

04NOV1994 

04NOV1994 

02DECl994 

04FEB1994 

03MAR1995 

O3MARI 994 

05MAY1993 

05MAR1992 

05APR1995 

O5MAY 1993 

12MAR1992 

03MAY1995 

02 JUN1993 

01APR1992 

OBAPRl994 

MMAY 1992 

16JUL1993 

01JUNl992 

05AUGl993 

O5MAY 1994 

06JUL1992 

02SEP1993 

03JUNl994 

03AUGl992 

050CT1993 

01 JULl994 

31 AUGl992 

070CT1992 

04NOV1993 

04NOV1993 

05JAN1 994 

05AUG1994 

03NOV1992 

05JAN1995 

02SEP1994 

lODECl993 

03FEB1995 

07OCT1994 

04NOV1994 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

7.00E+01 

7.40E+01 

6.00E+01 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

l.OOE+OO 

O.OOE+OO 

l.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

l.OOE+OO 

I .00E+00 

l.OOE+OO 

O.OOE+OO 

O.OOE+OO 

l.OOE+OO 

O.OOE+OO 

0.00E+00 

l.OOE+OO 

l.WE+OO 

l.OOE+OO 

O.OOE+OO 

O.WE+OO 

l.OOE+OO 

l.OOE+OO 

1.00E+00 

O.OOE+OO 

1 .OOE+OO 

l.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0,00E+00 

O.OOE+OO 

0.00E+00 

O.WE+W 

O.WE+OO 

O.WE+W 

O.WE+W 

O.WE+OO 

O.OOE+W 

O.M)E+OO 

O.WE+OO 

O.OOE+OO 

O.WE+OO 

0.00E+00 

0.00E+00 

0.00E+00 

O.OOE+OO 

O.OOE+W 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

< 

< 

< 

< 

< 

< 

< 

< 

< 

c 

< 

c 

< 

< 

< 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL CaC03 

mg1L CaC03 

mg1L CaCO3 

mglL 

rnglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mgfl 

mgfl 

mglL 

mglL 

mgfl 

mglL 

wfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mgk 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

m& 

mgfl 

mgfl




7439-92-1 2692-94 04NOV1994 WS O.OOE+OO C N mg1L 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-92-1 

2861-94 

288-94 

437-95 

507-94 

622-93 

631-92 

633-95 

636-93 

700-92 

787-95 

802-93 

855-92 

901-94 

956-95 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

622-93 

631 -92 

700-92 

855-92 

1023-92 

1074-93 

1 143-92 

1204-93 

1204-94 

1332-92 

1348-93 

1378-94 

1548-93 

1614-94 

1624-92 

1839-93 

1840-93 

19-94 

1920-94 

1937-92 

20-95 

2123-94 

2154-93 

220-95 

2413-94 

2691-94 

2692-94 

2861-94 

288-94 

437-95 

507-94 

622-93 

1477-92 

1796-92 

631-92 

633-95 

636-93 

700-92 

787-95 

802-93 

855-92 

901-94 

1023-92 

1074-93 

1143-92 

1204-93 

1204-94 

1332-92 

1348-93 

I 

378-94 

02DEC1994 

04FEB1994 

03MAR1995 

03MAR1994 

05MAYI 993 

OSMAR1992 

OSAPR1995 

OSMAY 1993 

12MAR1992 

OJMAY 1995 

02JUN1993 

01 APRl992 

OBAPR1994 

01JUN1995 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUG1992 

31AUGI 992 

070CT1992 

03NOV1992 

OSMAY 1993 

05MAR1992 

12MAR1992 

01APR1992 

04MAY1992 

16JUL1993 

01 JUN1992 

OSAUG1993 

05MAY I994 

06JULl992 

02SEPl993 

03JUN1994 

03AUG1992 

OSOCTI 993 

01 JUL1994 

3lAUGl992 

070CTI 992 

04NOV1993 

04NOV1993 

05JAN1994 

OSAUG1994 

03NOVl 992 

05JAN1995 

02SEP1994 

10DEC1993 

03FEB1995 

070CT1994 

04NOV1994 

04NOVl994 

02DECl994 

04FEB1994 

om1995 

om1994 

05MAY 1993 

05MARl992 

OSAPR1995 

05MAY 1993 

12MAR1992 

03MAY 1995 

O2JUNl 993 

01 APRI 992 

08APR1994 

04MAY I 

992 

16JUL1993 

01JUN1992 

OSAUGl993 

05MAY1994 

06JUL1992 

02SEPl993 

03JUN1994 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

U 

N 

N 

U 

N 

N 

N 

N 

U 

N 

N 

N 

U 

N 

N 

N 

N 

U 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

C 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

C 

C 

c 

C 

< 

C 

C 

C 

< 

< 

C 

C 

C 

C 

C 

< 

< 

C 

C 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

mgk 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

WlL 

mglL 

WlL 

mglL 

mglL 

mglL 

WlL 

mglL 

mglL 

mg1L 

WlL 

mgk 

mglL 

mglL 

mglL 

mglL 

WlL 

mgk 

mg/L 

WlL 

WlL 

WlL 

Wfl 

mglL 

Page 60 of 176




Manganese 7439-96-5 1477-92 03AUG1992 WS O.OOE+OO N mglL 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 


Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

7439-96-5 

7439 - 96 - 5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439 - 96 - 5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

75-09-2 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440 - 02 - 0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

1548-93 

1614-94 

1624-92 

1796-92 

1839-93 

1840-93 

19-94 

1920-94 

1937-92 

20-95 

2123-94 

2154-93 

220-95 

2413-94 

2691-94 

2692-94 

2861-94 

288-94 

437-95 

507-94 

622-93 

631 -92 

633-95 

636-93 

700-92 

787-95 

802-93 

855-92 

901-94 

1023-92 

114392 

1332-92 

1477-92 

154893 

1624-92 

1796-92 

1937-92 

622-93 

631-92 

700-92 

855-92 

1348-93 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

622-93 

631-92 

700-92 

855-92 

1023-92 

1074-93 

1143-92 

1204-93 

1204-94 

1332-92 

1348-93 

1378-94 

1477-92 

1548-93 

1614-94 

1624-92 

1796-92 

1839-93 

1840-93 

19-94 

1920-94 

1937-92 

050CT1993 

OlJUL1994 

31AUG1992 

070CT1992 

04NOV1993 

04NOV1993 

05JAN1994 

05AUG 1994 

03NOV1992 

05JAN1995 

02SEP1994 

10DEC1993 

03FEB1995 

070CT1994 

04NOV1994 

MNOV1994 

02DEC1994 

04FEB1994 

O3MAR1995 

03MAR1994 

O5MAY 1 993 

05MAR1992 

05APR1995 

O5MAY 1993 

12MAR1992 

03MAY 1995 

02JUNl993 

01 APRl992 

OBAPR1994 

04MAY 1992 

01JUN1992 

06JULl992 

03AUGl992 

050CT1993 

31AUGl992 

070CT1992 

03NOV1992 

O5MAY 1993 

05MAR1992 

12MAR1992 

01 APRl992 

02SEP1993 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUGl992 

3lAUGl992 

070CT1992 

03NOV1992 

05MAY 1993 

05MAR1992 

12MARl992 

01 APRl992 

04MAY 1992 

16JUL1993 

01 JUN 1992 

05AUG1993 

05MAY1994 

06JUL1992 

02SEP1993 

03JUN1994 

03AUG1992 

050CTl993 

01 JULl994 

3lAUG1992 

070CT1992 

04NOV1993 

MNOV1993 

05JAN1994 

05AUGl994 

03NOV1992 


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ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

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c 

c 

< 

c 

c 

c 

< 

c 

< 

< 

< 

< 

< 

c 

c 

c 

c 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

rnglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

rnglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mg1L 

mglL 

WlL 

mglL 

WlL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

WlL 

mglL 

mg1L 

mglL 

mglL 

uglL 

mglL 

mglL 

mglL 

mglL 

mglL 

W/L 

WlL 

mglL 

WlL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

WlL 

mglL 

WlL 

mglL 

mglL 

WlL 

mglL 

mglL 

WlL




Nickel 7440-02-0 20-95 05JAN1995 WS O.OOE+OO < N mglL 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

PCB 

PCB 

Phosphate as P 











Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

1336-36-3 

1336-36-3 

PHOSPHATEASP 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7440-09-7 

7440-09-7 

744049-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7640-09-7 

7440-09-7 

2123-94 

2154-93 

220-95 

2413-94 

2691-94 

2692 - 94 

2861-94 

288-94 

437-95 

507-94 

622-93 

631-92 

633-95 

636-93 

700-92 

787-95 

802-93 

855-92 

901-94 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

622-93 

631-92 

700-92 

855-92 

1863-92 

1937-92 

1796-92 

1023-92 

I 143-92 

1332-92 

1477-92 

1624-92 

1937-92 

622-93 

631 -92 

700-92 

855-92 

1023-92 

1074-93 

1143-92 

1204-93 

1204-94 

1332-92 

1348-93 

1378-94 

1477-92 

1548-93 

1614-94 

1624-92 

1796-92 

1839-93 

1840-93 

19-94 

1920-94 

1937-92 

20-95 

2123-94 

2154-93 

220-95 

2413-94 

2691-94 

2692-94 

2861 -94 

288-94 

437-95 

02SEP1994 

10DEC1993 

03FEB1995 

070CT1994 

04NOV1994 

04NOV1994 

02DEC1994 

04FEB1994 

03MARl995 

03hlAR1994 

05MAY 1993 

(HMAR 1992 

05APR1995 

OSMAY 1993 

12MAR1992 

03MAY 1995 

02JUN1993 

01 APRl992 

O8APR 1 994 

04MAY 1992 

OlJUN1992 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

05MAY1993 

05MAR1992 

12MAR 1992 

01 APRI 992 

190CT1992 

03NOV1992 

O7OCTI 992 

04MAY1992 

01JUNl992 

06JUL1992 

03AUG1992 

31AUG1992 

03NOV1992 

OSMAY1993 

05MAR1992 

12MAR1992 

01 APRl992 

04MAYl992 

16JUL1993 

01 JUNl992 

05AUGl993 

05MAY 1994 

OGJULI 992 

02SEPl993 

O3JUNl994 

03AUG1992 

050CTI 993 

01 JULl994 

3lAUGl992 

070CT1992 

04NOV1993 

04NOVl993 

05JAN1994 

OSAUG1994 

03NOV1992 

OSJAN1995 

02SEP1994 

10DECl993 

03FEB1995 

070CT1994 

04NOV1994 

04NOV1994 

02DECl994 

04FEBl994 

03MARl995 


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ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

c 

N 

< N 

c 

N 

c 

N 

c 

N 

c 

N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

e 

N 

< N 

c 

N 

< N 

< N 

c 

NT 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

c 

N 

< N 

N 

NT 

< N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

uglL 

wfl 

mglL 

mglL 

mgfl 

mgk 

mglL 

mglL 

mg1L 

mglL 

mgL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mgL 

mgL 

mgfl 

mglL 

mg5 

mgfl 

mglL 

mgfl 

mgfl 

mgfl 

mglL 

mgfl 

mglL 

mglL 

mgk 

mgk 

mglL 

mgfl




Potassium 7440-09-7 507-94 03MAR1994 WS 2.00E+00 N 

mglL 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Beta 

Rad Beta 

Rad Beta 

Rad Beta 

Rad Beta 

Rad Beta 

Rad Beta 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

12507-46-1 

12507-46-1 

12507-46-1 

12507-46-1 

12507-46-1 

12507-46-1 

12507-46-1 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

7440-10-0 

7440-10-8 

7440-10-0 

7440-10-0 

7440-10-0 

7440-10-0 

7440-10-0 

7440-10-0 

7440-10-0 

7440-10-0 

7440-10-0 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-21-3 

7440-21 -3 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

1440-21-3 

7440-21 -3 

1440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

622-93 

631-92 

633-95 

636-93 

700-92 

707-95 

002-93 

055-92 

901 -94 

1147-95 

220-95 

437-95 

633-95 

707-95 

002-93 

956-95 

1147-95 

220-95 

437-95 

633-95 

707-95 

002-93 

956-95 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

622-93 

631-92 

700-92 

055-92 

1023-92 

1074-93 

1143-92 

1204-93 

1204-94 

1332-92 

1340-93 

1370-94 

1477-92 

1540-93 

1614-94 

1624-92 

1796-92 

1039-93 

1040-93 

19-94 

1920-94 

1937-92 

20-95 

2123-94 

2154-93 

220-95 

2413-94 

2691-94 

2692-94 

2061-94 

200-94 

437-95 

507-94 

622-93 

631-92 

633-95 

63693 

700-92 

707-95 

802-93 

055-92 

05MAY 1993 

05MAR1992 

05APR1995 

05MAY1993 

12MAR1992 

03MAY 1995 

02 JUNl993 

01 APRl992 

00APR1994 

06JULl995 

O3FEBl 995 

03MAR1995 

05APR 1995 

OJMAY1995 

02JUN1993 

01JUN1995 

06JUL1995 

O3FEB1995 

O3MAR1995 

05APR 1995 

O3MAY 1995 

02JUN1993 

01JUN1995 

04MAY 1992 

01 JUN1992 

06JULl992 

03AUG1992 

31AUGl992 

070CT1992 

03NOV1992 

OSMAY 1993 

05MAR1992 

12MARl992 

01 APRl992 

04MAY 1992 

16JUL1993 

01 JUN1992 

05AUG1993 

05MAYl994 

06JUL1992 

O2SEPl 993 

O3JUNI 994 

03AUG 1992 

050CT1993 

01 JUL1994 

3lAUGl992 

070CT1992 

MNOV1993 

MNOV1993 

05JANl994 

05AUG1994 

03NOV1992 

05JAN1995 

02SEP1994 

10DECl993 

03FEBl995 

070CT1994 

04NOV1994 

MNOV1994 

02DEC1994 

MFEB 1994 

03MAR1995 

03MARl994 

05MAYl993 

OSMAR1992 

05APR1995 

OSMAY 1993 

12MAR 1992 

03MAY 1995 

02JUN1993 

01APR1992 

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C 

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< 

C 

C 

< 

< 

< 

< 

C 

C 

C 

C 

J 

J 

J 

B 

J 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mgtL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

pCilml 

pCUml 

pCUml 

pCilml 

pCilml 

pCVmL 

pCilml 

pCiml 

pCilml 

pCiml 

pCUmi 

pCiml 

pCimL 

pCilml 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mgR 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

mglL 

mg/L 

mglL 

mgfl 

mglL 

mg/L 

mglL 

WlL 

mglL 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws




Silicon 7440-21-3 901 -94 08APR1994 WS 6.00E+00 N mg1L 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 














Specfic conductance 



spec if^ conductance 

Specib conductance 





7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7 44 0 - 2 3- 5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

622-93 

631-92 

700-92 

855-92 

1023-92 

1074-93 

1143-92 

1204-93 

1204-94 

1332-92 

1348-93 

1378-94 

1477-92 

1548-93 

1614-94 

1624-92 

1796-92 

1839-93 

1840-93 

19-94 

1920-94 

1937-92 

20-95 

2123-94 

2154-93 

220-95 

2413-94 

2691-94 

2692-94 

2861-94 

288-94 

437-95 

507-94 

622-93 

631-92 

633-95 

636-93 

700-92 

787-95 

802-93 

855-92 

901-94 

1074-93 

1147-95 

1204-93 

1204-94 

1348-93 

1376-94 

1548-93 

1614-94 

1839-93 

1840-93 

19-94 

1920-94 

20-95 

2123-94 

2154-93 

220-95 

2413-94 

2691-94 

2692-94 

2861-94 

268-94 

437-95 

04MAY 1992 

01 JUN1992 

06JUL1992 

03AUG1992 

31 AUGl992 

070CT1992 

03NOV1992 

05MAY1993 

05MAR1992 

12MAR1992 

OiAPR1992 

04MAY1992 

16JUL1993 

01JUNl992 

05AUGl993 

05MAY1994 

06JUL1992 

02SEP1993 

OUUNl994 

03AUG1992 

050CT1993 

01 JUL1994 

31AUG1992 

070CT1992 

04NOV1993 

04NOV1993 

05JAN1994 

05AUG1994 

03NOV1992 

05JAN1995 

02SEP1994 

10DECl993 

03FEB1995 

070CT1994 

04NOV1994 

04NOV1994 

02DEC1994 

04FEE1994 

03MAR1995 

03MAR1994 

05MAYl993 

05MAR1992 

05APR1995 

osMAY1993 

12MAR1992 

03MAY1995 

02JUNl993 

01APR1992 

08APR1994 

16JUL1993 

06JUL1995 

05AUGl993 

osMAY 1994 

02SEP1993 

03JUN1994 

050CT1993 

01 JUL1994 

MNOV1993 

MNOVl993 

WAN1994 

05AUGl994 

05JANl995 

02SEPl994 

1 ODECi993 

03FEB1995 

070CT1994 

MNOVl994 

MNOVl994 

02DECl994 

MFEB1994 

03MAR1995 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

< NT 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

B 

J 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

m&L 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mgfl 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

wfl 

mgfl 

wfl 

mglL 

mg1L 

mg/L 

mglL 

mgk 

mgfl 

WlL 

mg/L 

wfl 

mglL 

mglL 

mgfl 

mglL 

mgfl 

mglL 

mgfl 

mglL 

WlL 

mg/L 

WlL 

mg/L 

mglL 

wfl 

umhodcm 

umhodcm 

umhoslcm 

umhodcm 

umhos/cm 

urnhodcm 

umhodcm 

umhodcm 

urnhoslcm 

umhodcm 

umhodcm 

urnhoslcm 

umhodcm 

umhodcm 

umhodcm 

umhoslcm 

umhodcm 

umhoslcm 

umhoslcm 

umhodcm 

umhodcm 

umhodcm




Specific conductance SO145 507-94 03MAR1994 WS 2.10E+02 N umhoslcrn 






Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Sulfate 

Sulfate 

Sulfate 

Sulfate 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Tantalum 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thorium 

Thorium 

SO145 

SO145 

SO145 

SO145 

SO145 

7440-24-6 

7440-24-6 

7440-24-6 

7440 - 24 - 6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

I 2143-45-2 

12143-45-2 

12143-45-2 

12143-45-2 

7440-25-7 

1440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-25-7 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-26-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-29-1 

7440-29-1 

633-95 

787-95 

802-93 

901-94 

956-95 

1023-92 

1074-93 

1143-92 

1204-93 

1204-94 

1332-92 

1348-93 

1378-94 

1477-92 

1548-93 

1614-94 

1624-92 

1796-92 

1839-93 

1840-93 

19-94 

1920-94 

1937-92 

20-95 

2123-94 

2154-93 

220-95 

2413-94 

2691-94 

2692-94 

2861-94 

288-94 

437-95 

507-94 

622-93 

631-92 

633-95 

636-93 

700-92 

787-95 

802-93 

855-92 

901-94 

1143-92 

1332-92 

1477-92 

1624-92 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

622-93 

631-92 

700-92 

855-92 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

622-93 

631-92 

700-92 

855-92 

1023-92 

1143-92 

05APR1995 

O3MAY 1995 

02JUN1993 

08APR1994 

01JUNl995 

04MAY 1992 

16JUL1993 

01JUN1992 

OSAUGI 993 

OSMAY 1994 

06JUL1 992 

02SEP1993 

03JUN1994 

O3AUGl 992 

050CT1993 

01JUL1994 

31AUGI 992 

070CT1992 

04NOV1993 

04NOV1993 

05JAN1994 

OSAUG1994 

O3NOVl 992 

05JAN1995 

02SEPl994 

10DECl993 

03FEB1995 

070CT1994 

04NOV1994 

04NOV1994 

02DEC1994 

04FEB1994 

03MAR1995 

03MAR1994 

05MAY 1993 

05MAR1992 

05APR1995 

05MAY 1993 

12MAR1992 

03MAY1995 

O2JUNl 993 

01 APRl992 

08APR1994 

01JUN1992 

06JUL1992 

03AUG1992 

3lAUGl992 

04MAY 1992 

01 JUNl992 

06JULl992 

03AUG1992 

3lAUGl992 

070CT1992 

O3NOVl 992 

05MAY 1993 

osMAR1992 

12MAR1992 

01 APRl992 

04MAYI992 

01JUN1992 

06JUL1992 

03AUG1992 

3lAUGl992 

07OCT1992 

03NOV1992 

OSMAY 1993 

WR1992 

12MAR1992 

01APR1992 

04MAY 1992 

01 JUN1992 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

vvs 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

< 

c 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

umhoslcrn 

umhoslcrn 

umhoslcrn 

umhoslcm 

umhoslcrn 

mglL 

mg/L 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mg/L 

mg/L 

mglL 

mglL 

mglL 

mglL 

mglL 

mgn 

mglL 

mglL 

mg1L 

mglL 

WlL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

WlL 

WlL 

W/L 

mg/L 

mg/L 

WlL 

rnglL 

mgfl 

mglL 

mg1L 

mglL 

WlL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

WlL 

mglL 

WIL 

mglL 

mglL 

mglL 

mglL 

mglL 

WlL 

mglL 

mgiL 

mglL 

mglL 

mglL 

WlL 

mglL 

W/L 

mg/L 

mgn 

mglL




Thorium 7440-29-1 1332-92 06JUL1992 WS O.OOE+OO < mglL 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Thorium 

Tin 

Tin 

Tin 

Tin 

Tin 

Tin 

Tin 

Tin 

Tin 

Tin 

Tin 

Titanium 

Titanium 

Titanium 

Titanium 

Titanium 

Titanium 

Titanium 

Titanium 

Titanium 

Titanium 

Titanium 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 




















Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-31-5 

7440-31 -5 

7440-31-5 

7440-31-5 

7440-31 -5 

7440-31-5 

7440-31 -5 

7440-31 -5 

7440-31 -5 

7440-31 -5 

7440-31 -5 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

108-88-3 

108-88-3 

108-88-3 

108-88-3 

7440-32-6 

7440-32-6 

1 oa-88-3 

108-88-3 

108-88-3 

1 oa-aa-3 

108-88-3 

1 08-aa-3 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

156-60-5 

79-01-6 

7440-33-7 

1477-92 

1624-92 

1796-92 

1937-92 

622-93 

631-92 

700-92 

855-92 

1023-92 

11 43-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

622-93 

631-92 

700-92 

855-92 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

622-93 

631-92 

855-92 

1023-92 

1143-92 

1332-92 

1477-92 

1796-92 

700-92 

1624-92 

1937-92 

631 -92 

700-92 

855.92 

1023-92 

1143-92 

1477-92 

1624-92 

1796-92 

1937-92 

631-92 

700-92 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

700-92 

855-92 

1023-92 

1143-92 

1332-92 

1624-92 

1796-92 

1937-92 

622-93 

631-92 

700-92 

855-92 

1332-92 

855-92 

631-92 

1477-92 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

OSMAY 1993 

05MAR1992 

12MARl992 

01 APRl992 

04MAY 1992 

01JUN1992 

06JULl992 

03AUG1992 

31 AUGl992 

070CT1992 

03NOV1992 

05MAY 1993 

OSMAR1992 

12MAR1992 

01 APR1992 

04h4AY 1992 

01JUN1992 

06JUL1992 

03AUGl992 

31AUG1992 

070CT1992 

03NOV1992 

05MAY1993 

05MARl992 

12MARl992 

OlAPRl992 

04MAY 1992 

01 JUN1992 

06JUL1992 

03AUGl992 

3lAUGl992 

070CT1992 

03NOV1992 

05MAR1992 

12MAR1992 

OlAPRl992 

04MAY 1992 

01 JUNl992 

06JUL1992 

03AUGI992 

3lAUGl992 

070CT1992 

03NOV1992 

05MAR1992 

12MAR1992 

01APR1992 

04MAY1992 

01 JUN1992 

06JULl992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

05MAR1992 

I 

ZMARI 992 

01 APRI 992 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUG1992 

3lAUGl992 

070CTl992 

03NOV1992 

OSMAY 1 993 

05MAR1992 

12MAR1992 

01 APR1992 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

< 

< 

< 

< 

c 

4 

< 

< 

< 

< 

< 

c 

< 

< 

< 

< 

< 

4 

c 

< 

c 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

c 

c 

< 

< 

< 

c 

< 

< 

< 

< 

< 

< 

< 

< 

< 

c 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

c 

< 

< 

< 

< 

< 

c 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

WlL 

Wfl 

mgfl 

mglL 

mglL 

mg1L 

mglL 

mg1L 

mglL 

mg1L 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

WlL 

mglL 

mgll 

mglL 

mglL 

W/L 

mglL 

mg1L 

WlL 

mglL 

mgfl 

m a 

ug1L 

ugk 

ugk 

ug1L 

ug1L 

uglL 

uglL 

uglL 

uglL 

uglL 

ugfl 

ug1L 

uglL 

uglL 

ugk 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ugfl 

uglL 

uglL 

ug1L 

uglL 

ug/L 

ugfl 

ugfl 

uglL 

Wfl 

Wfl 

mglL 

mgfl 

mgfl 

mgk 

mg/L 

mglL 

mglL 

WlL 

WlL 

mglL 

Page 66 of 176



ANALYE CAS NUMBER SAMPLE ID DATE WPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Uranium 7440-61-1 1023-92 04MAY1992 WS O.OOE+OO NT mglL 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zirconium 

Zirconium 

zirconium 

7440-61 -1 

7440-61 -1 

7440-61-1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61-1 

7440-61 -1 

7440-61 -1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61 -1 

7440-61 -1 

7440-61-1 

7440-61-1 

7440-61 -1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61 -1 

7440-61-1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61 -1 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-67-7 

7440-67-7 

7440-67-7 

1074-93 

1143-92 

1204-93 

1204-94 

1332-92 

1348-93 

1378-94 

1477-92 

1548-93 

1614-94 

1624-92 

1796-92 

1839-93 

1840-93 

19-94 

1920-94 

1937-92 

20-95 

2123-94 

2154-93 

220-95 

2413-94 

2691-94 

2692-94 

2861 -94 

286-94 

437-95 

507-94 

622-93 

631 -92 

633-95 

700-92 

787-95 

802-93 

855-92 

901-94 

956-95 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1937-92 

622-93 

631 -92 

700-92 

855-92 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

631-92 

700-92 

855-92 

1023-92 

1143-92 

1332-92 

1477-92 

1624-92 

1796-92 

1937-92 

622-93 

631-92 

700-92 

855-92 

1023-92 

1143-92 

1332-92 

16JUL1993 

01JUN1992 

05AUG1993 

O5MAY 1994 

06JUL1992 

02SEP1993 

03JUN1994 

03AUG1992 

050CT1993 

OlJUL1994 

31 AUG 1992 

070CT1992 

04NOV1993 

04NOV1993 

OSJANl994 

05AUG1994 

03NOV1992 

OSJANl995 

02SEP1994 

10DEC1993 

03FEB1995 

070CT1994 

04NOV1994 

04NOV1994 

02DECl994 

04FEB1994 

03MAR 1995 

03MARl994 

OSMAY1993 

OSMAR1992 

OSAPR1995 

12MAR1992 

03MAY 1995 

02JUNl993 

01 APRl992 

OBAPRl994 

01 JUNl995 

04MAY 1992 

OlJUN1992 

06JULl992 

03AUG1992 

3lAUGl992 

03NOV1992 

OSMAY 1993 

OSMARl992 

12MAR1992 

OlAPR1992 

04MAY 1992 

01 JUNl992 

06JUL1992 

03AUG1992 

3lAUGl992 

070CT1992 

03NOV1992 

05MAR1992 

12MAR1992 

01 APR1992 

MAY 1992 

01JUN1992 

06JUL 1992 

O3AUG1992 

31AUG1992 

07OCT1992 

03NOV1992 

WAY 1993 

05MAR1992 

12MARl992 

01APR1992 

WMAY 1992 

01 JUN1992 

06JUL1992 


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ws 

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ws 

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N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

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mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

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mglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

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mglL 

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mglL 

mglL 

mglL 

mgk 

mglL 

mglL 

mgfl 

mglL 

mglL 

mgfl 

mglL 

mg/L 

mglL 

WlL 

Wfl 

mglL 

mglL 

mg1L 

WlL 

mglL 

mgfl 

mglL 

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uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

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mg1L 

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mglL 

mglL 

mgfl 

mglL




Zirconium 7440-67-7 1477-92 03AUG1992 WS 0.00E+00 C N mglL 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

zirconium 

Zirconium 

Zirconium 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

so296 

SO296 

SO296 

SO296 

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SO296 

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so296 

SO296 

so296 

SO296 

SO296 

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SO296 

SO296 

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SO296 

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SO296 

SO296 

SO296 

so296 

so296 

SO296 

so296 

so296 

so296 

so296 

SO296 

so296 

so296 

7440-67-7 

1624-92 

1796-92 

1937-92 

622-93 

631-92 

700-92 

855-92 

1023-92 

1067-92 

1074-93 

11 11-92 

1143-92 

11 47-95 

11 95-92 

1204-93 

1222-92 

1309-92 

1332-92 

1348-93 

1369-92 

1378-94 

1444-92 

1477-92 

1503-92 

1551-92 

1599-92 

1614-94 

1624-92 

1684-92 

179692 

1096-92 

1204-94 

1267-92 

1418-92 

i 548-93 

1662-92 

1839-93 

1840-93 

19-94 

1920-94 

1967-92 

20-95 

2123-94 

2137-92 

2154-93 

2413-94 

2691-94 

220-95 

2692-94 

2861-94 

288-94 

437-95 

507-94 

612-92 

622-93 

631-92 

633-95 

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636-93 

700-92 

712-92 

787-95 

802-93 

827-92 

855-92 

88982 

901-94 

922-92 

956-95 

976-92 

994-92 

3lAUGl992 

070CT1992 

03NOV1992 

O5MAY 1993 

OSMARl992 

12MAR1992 

01APR1992 

MMAY 1992 

13MAY 1992 

16JUL1993 

2OMAY 1992 

26MAY1992 

OlJUN1992 

06JUL1995 

08JUN1992 

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21JUL1992 

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1 OAUGl992 

050CTl993 

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07DEC1992 

10DEC1993 

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04NOV1994 

04NOVl994 

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03MAR1995 

03MAR1994 

02MAR1992 

05MAY 1993 

OsMAR1992 

05APR1995 

OSMAY 1993 

09MAR1992 

12MAR1992 

1-1992 

03MAY 1995 

02JUN1993 

23MAR1992 

0 1 APR1992 

06APR1992 

08APR1994 

13APR1992 

01JUN1995 

22APR1992 

27APR1992 

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N 

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N 

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N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

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mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

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Page 68 of 176




WAG 7, SMU 8. C746K-5 









1.1 -Dichloroethane 




1 ,I-Dichloroelhene 












Acetone 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminurn 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminurn 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

67-64-1 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

1024-92 

1144-92 

1333-92 

1478-92 

1625-92 

1797-92 

1938-92 

2102-92 

395-92 

632-92 

701-92 

856-92 

1024-92 

1144-92 

1333-92 

1478-92 

1625-92 

1797-92 

1938-92 

2102-92 

395-92 

632-92 

701-92 

856-92 

1838-93 

1024-92 

1075-93 

1144-92 

1205-93 

1205-94 

1206-93 

1206-94 

1333-92 

1349-93 

1374-93 

1379-94 

1380-94 

147a92 

1549-93 

1550-93 

1615-94 

1616-94 

1625-92 

1797-92 

1838-93 

1921-94 

1922-94 

ma92 

20-94 

21-95 

2102-92 

2124-94 

2125-94 

2155-93 

2161-93 

22-95 

221-95 

222-95 

23-94 

2414-94 

2415-94 

2693-94 

2862-94 

2863-94 

289-94 

290-94 

395-92 

43895 

439-95 

508-94 

623-93 

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01 JUN1992 

06JUL1992 

03AUG1992 

31AUGl992 

070CT1992 

03NOV1992 

01DEC1992 

3OJAN1992 

05MAR1992 

12MARl992 

01 APR1992 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUG1992 

31AUG 1992 

070CT1992 

03NOV1992 

01DEC1992 

3OJANl992 

OSMAR 1992 

12MARl992 

01 APRI 992 

04NOV1993 

04MAY 1992 

16JULl993 

01JUN1992 

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05MAY 1 994 

05AUG1993 

05MAY1994 

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03JUN1994 

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050CTI993 

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05AUGl994 

05AUG1994 

03NOV1992 

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05JAN1995 

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02SEP1994 

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10DEC1993 

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03FEB1995 

%JAN1994 

070CT1994 

070CT1994 

04NOVl994 

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O2DEC1994 

04FEB1994 

04FEB1994 

30JAN1992 

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03MPR1995 

03MAR1994 

OSMAY 1993 


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N 

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uglL 

uglL 

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ug1L 

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uglL 

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Aluminum 7429-90-5 632-92 05MAR1992 WS O.OOE+OO N mglL 

Aluminum 

Aluminurn 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminurn 

Aluminum 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

7429-90-5 

7429-90-5 

7429-90-5 

1429-90-5 

1429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

1440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

1440-38-2 

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7440-38-2 

7440-38-2 

1440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

1440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

1440-38-2 

7440-38-2 

1440-38-2 

7440-38-2 

740-38-2 

7440-38-2 

7440-38-2 

740-38-2 

7440-38-2 

1440-38-2 

1440-38-2 

1440-38-2 

7w-3a-2 

7440-38-2 

7440-38-2 

7440-30-2 

7440-38-2 

7440-30-2 

7440-382 

7440-38-2 

7440-38-2 

634-95 

635-95 

637-93 

701-92 

788-95 

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803-93 

856-92 

902-94 

903-94 

1 144-92 

1333-92 

1024-92 

1478-92 

1625-92 

1797-92 

1938-92 

21 02-92 

395-92 

623-93 

632-92 

856-92 

1024-92 

1075-93 

1144-92 

1205-93 

1205-94 

1206-93 

1206-94 

1333-92 

1349-93 

1374-93 

1379-94 

1380-94 

1478-92 

1549-93 

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1797-92 

1838-93 

1938-92 

1921-94 

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20-94 

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222-95 

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290-94 

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O.WE+W 

O.WE+W 

O.WE+W 

O.WE+W 

O.WE+W 

O.WE+W 

O.WE+W 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+W 

O.OoE+W 

O.OOE+OO 

O.WE+OO 

O.WE+OO 

O.WE+OO 

O.WE+W 

O.WE+W 

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MEDIA RAD RESULT VALlDATlON 


Arsenic 7440-38-2 635-95 05APR1995 WS O.OOE+OO < N mg1L 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

7440-30-2 

7440-30-2 

7440-30-2 

7440-38-2 

7440-30-2 

7440-30-2 

7440-30-2 

7440-30-2 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440 - 39 - 3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

71-43-2 

71-43-2 

7143-2 

7143-2 

7143-2 

7143-2 

637-93 

701-92 

788-95 

789-95 

803-93 

856-92 

902-94 

903-94 

1024-92 

1075-93 

1144-92 

1205-93 

1205-94 

1206-93 

1206-94 

1333-92 

1349-93 

1374-93 

1379-94 

1380-94 

1470-92 

1549-93 

1550-93 

1615-94 

1616-94 

1625-92 

1797-92 

1830-93 

1921 -94 

1922-94 

1930-92 

20-94 

21-95 

2102-92 

2124-94 

2125-94 

2155-93 

2161-93 

22-95 

221-95 

222-95 

23-94 

2414-94 

2415-94 

2693-94 

2862-94 

2863-94 

289-94 

290-94 

395-92 

430-95 

439-95 

50894 

623-93 

632-92 

634-95 

635-95 

637-93 

701-92 

700-95 

789-95 

803-93 

856-92 

902-94 

903-94 

1024-92 

1144-92 

1333-92 

1478-92 

1625-92 

1797-92 

05MAY 1993 

12MAR1992 

03MAY 1995 

03MAY1995 

O2JUNl 993 

01 APRl992 

00APR1994 

O0APR1 994 

04MAY 1992 

16JUL1993 

01JUN1992 

05AUG1993 

05MAY1994 

05AUG1993 

O5MAYl 994 

06JULI 992 

02SEP1993 

02SEP1993 

03JUN1994 

03JUN1994 

03AUG1992 

050CT1993 

05OCTl 993 

OlJULl994 

OlJUL1994 

31AUG 1992 

070CT1992 

04NOV1993 

05AUG1994 

05AUGl994 

03NOV1992 

05JANl994 

WAN1995 

01DECl992 

O2SEPl994 

O2SEPl 994 

10DECl993 

1 ODEC1993 

05JAN1995 

03FEB1995 

03FEB1995 

(HJANI 994 

070CT1994 

070CT1994 

04NOV1994 

02DECl994 

02DEC1994 

04FEB1994 

04FEB1994 

3OJANl992 

03MAR1995 

03MAR1995 

03MAR1994 

05MAY 1993 

05MAR1992 

05APR1995 

05APRl995 

05MAY1993 

12MAR1992 

03MAY 1995 

03MAYl995 

O2JUN1 993 

OIAPRI 992 

08APR1994 

OWR1994 

04MAY 1992 

01 JUN1992 

06JUL1992 

03AUGl992 

31AUG1992 

070CT1992 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

vvs 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

< N 

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71-43-2 1938-92 03NOV1992 WS 5.00E+00 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmiurn 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmum 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

71-43-2 

7 1-43-2 

71-43-2 

71-43-2 

71-43-2 

7440-41 -7 

7440-41-7 

7440-41 -7 

7440-41 -7 

7440-41 -7 

7440-41-7 

7440-41-7 

7440-41 -7 

7440-41 -7 

7440-41 -7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

744043-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

744043-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

2102-92 

395-92 

632-92 

701-92 

856-92 

1024-92 

1144-92 

1333-92 

1478-92 

1625-92 

1797-92 

1938-92 

2102-92 

395-92 

623-93 

632-92 

701-92 

856-92 

1024-92 

1 144-92 

1333-92 

1478-92 

1797-92 

1938-92 

2102-92 

623-93 

1625-92 

395-92 

632-92 

701-92 

856-92 

1024-92 

1075-93 

1144-92 

1205-93 

1205-94 

120693 

1206-94 

1333-92 

1349-93 

1374-93 

1379-94 

1380-94 

1478-92 

1549-93 

1550-93 

1615-94 

1625-92 

1838-93 

161 6-94 

1797-92 

1921-94 

1922-94 

1938-92 

20-94 

21-95 

2102-92 

2124-94 

2125-94 

2155-93 

2161-93 

22-95 

221-95 

222-95 

23-94 

2414-94 

2415-94 

2693-94 

2862-94 

2863-94 

289-94 

01 DECl992 

3OJAN1992 

OSMARI 992 

12MAR1992 

01 APRl992 

O4MAY 1992 

01 JUN1992 

06JULI 992 

03AUG1992 

3lAUGI 992 

O7OCTI 992 

03NOV1992 

01 DECI 992 

30JAN1992 

05MAY1993 

05MAR1992 

12MARl992 

01 APR 1992 

04MAY 1992 

01JUN1992 

06JUL1992 

03AUG1992 

31AUG1992 

070CT1992 

03NOV1992 

01DEC1992 

30JAN1992 

05MAY1993 

05MAR1992 

1 2MARI 992 

01 APRl992 

04MAY1992 

16JUL1993 

01 JUNl992 

05AUG1993 

WAY 

I994 

O5AUG 1993 

(HMAY 1994 

06JUL1992 

02SEP1993 

02SEP1993 

03JUN1994 

03JUNl994 

03AUG1992 

050CT1993 

OSOCTl993 

OlJUL1994 

OlJULl994 

31AUG 1992 

070CT1992 

MNOV1993 

05AUGl994 

05AUG1994 

03NOV1992 

OSJANl994 

05JANl995 

01 DECl992 

OZSEP1994 

02SEP1994 

1 ODECI 993 

lODECI993 

WAN1995 

03FEB1995 

03FEB1995 

05JAN1994 

070CT1994 

070CT1994 

04NOVl994 

02DEC1994 

02DEC1994 

MFEB1994 

ws 

ws 

ws 

ws 

ws 

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Page 72 of 176




Cadmium 7440-43-9 290-94 04FEB1994 WS O.OOE+OO c N mglL 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Chloride 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

16887-00-6 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

395-92 

438-95 

439-95 

508-94 

623-93 

632-92 

634-95 

635-95 

637-93 

701-92 

788-95 

789-95 

803-93 

856-92 

902-94 

903-94 

957-95 

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1478-92 

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632-92 

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1024-92 

1075-93 

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1205-93 

1205-94 

1206-93 

1206-94 

1333-92 

1349-93 

1374-93 

1379-94 

1380-94 

1478-92 

1549-93 

1550-93 

1615-94 

1616-94 

1625-92 

1797-92 

1838-93 

1921-94 

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1938-92 

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2415-94 

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2862-94 

2863-94 

289-94 

290-94 

30JANI 992 

03MAR1995 

03MAR1995 

03MAR1994 

O5MAY 1993 

05MAR1992 

OSAPR1995 

05APR1995 

OSMAYI 993 

12MAR1992 

03MAY 1995 

O3MAY 1995 

02JUN1993 

01 APR 1992 

08APR1994 

08APR1994 

01JUNl995 

01JUN1995 

04MAY 1992 

01JUN1992 

06JULI 992 

03AUG1992 

31 AUGI 992 

070CTl992 

03NOV1992 

01 DEC1992 

30JAN1992 

05MAYl993 

05MAR1992 

12MAR1992 

01APR1992 

3OJAN1992 

04MAY 1992 

16JULl993 

01JUN1992 

05AUG1993 

05MAY 1994 

05AUG1993 

05MAY 1994 

06JUL1992 

02SEPl993 

O2SEPl993 

03JUN1994 

03JUN1994 

03AUGl992 

050CT1993 

050CTI993 

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mglL 

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mglL 

mglL 

mg1L 

mglL 

mglL 

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mglL 

mglL 

mgfl 

mdL 

mglL 

mg1L 

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mglL 

mg/L 

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mglL 

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Page 73 of 176




Chromium 744047-3 395-92 30JAN1992 WS O.OOE+OO < N mglL 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Cobalt 

Cobalt 

Cobalt 

Cobalt 

Cobalt 

Cobalt 

Cobalt 

Coban 

Cobalt 

Coban 

Cobalt 

Cobalt 

Coban 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 


Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Fluoride 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCMS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-0 

7440-50-8 

7440-50-8 

7440-50-8 

OXYGEN DIS 

100414 

10041-4 

100414 

100-41-4 

100-41-4 

100-41-4 

10041-4 

10041-4 

100-41-4 

100-414 

10041-4 

100-41-4 

I 6984-48-8 

GCMS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

508-94 

623-93 

632-92 

637-93 

701-92 

803-93 

as6-92 

902-94 

903-94 

1024-92 

1144-92 

1333-92 

1478-92 

1625-92 

1797-92 

1938-92 

2102-92 

395-92 

623-93 

632-92 

701-92 

856-92 

1024-92 

1144-92 

1333-92 

1478-92 

1625-92 

1797-92 

I 938-92 

2102-92 

395-92 

623-93 

632-92 

701-92 

856-92 

395-92 

102492 

1144-92 

1333-92 

1478-92 

1625-92 

1797-92 

I 93a-92 

2102-92 

395-92 

632-92 

701-92 

856-92 

395-92 

1075-93 

I 148-95 

1149-95 

1205-93 

1205-94 

1206-93 

1206-94 

1349-93 

1379-94 

I 380-94 

1549-93 

1550-93 

1615-94 

1616-94 

1921-94 

1922-94 

20-94 

21-95 

2124-94 

2125-94 

2155-93 

2161 -93 

03MAR1994 

05MAY 1993 

05MAR1992 

OSMAY 1993 

12MAR1992 

02JUNl993 

01 APRl992 

08APRl994 

08APR1994 

04MAY 1992 

OlJUN1992 

06JUL1 992 

03AUG1992 

3lAUGl992 

O7OCTI 992 

03NOV1992 

01 DECl992 

30JANl992 

OSMAY 1993 

05MAR1992 

12MAR1992 

01APR1992 

04MAY 1992 

01 JUNl992 

06JULl992 

03AUG1992 

3lAUG1992 

070CT1992 

03NOV1992 

OlDEC1992 

3WANl992 

05MAY1993 

05MAR1992 

12MAR1992 

01 APR 1992 

30JANl992 

04MAY 1992 

01JUNl992 

06JUL1992 

03AUG1992 

31 AUG 1992 

070CT1992 

03NOV1992 

01DECl992 

3 WAN1 992 

05MAR1992 

12MAR1992 

01 APRl992 

3WANl992 

16JUL1993 

06JUL1995 

06JULl995 

05AUG1993 

(HMAY 1994 

OSAUGl993 

05MAY1994 

02SEP1993 

03JUNI994 

03JUNl994 

050CT1993 

05OCTl993 

01 JULl994 

01 JUL1994 

05AUGl994 

OSAUG1994 

WAN1994 

05JAN1995 

02SEP1994 

02SEPl994 

1 ODEC1993 

10DECl993 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

4 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

c 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

c 

c 

< 

< 

< 

< 

< 

< 

< 

< 

< 

c 

c 

c 

c 

< 

4 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Q 

Q 

N 

N 

N 

N 

N 

FIELD 

FIELD 

0712- 

0712- 

N 

N 

N 

N 

N 

N 

N 

rnglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

rnglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mgfl 

mglL 

mgfl 

mgfl 

mglL 

mgfl 

Wfl 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ug5 

ugfl 

ugk 

uglL 

uglL 

w/L 

uglL 

ugfl 

ugfl 

ug1L 

ugfl 

uglL 

uglL 

uglL 

Wfl 

ugfl 

uglL 

uglL 

uglL 

uglL 

ugR 

ugfl 

uglL 

ugn 

UglL 

uglL 

ugk 

ugfl 

Page 74 of 176



ANALYE CAS NUMBER SAMPLE ID DATE NPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

GCNS Scan GCNS SCAN 22-95 OSJAN1995 WS O.OOE+OO V N uglL 

GCNS Scan 

GCNS Scan 

GClMS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GClMS Scan 

GClMS Scan 

GClMS Scan 

GClMS Scan 

GCNS Scan 

GCNS Scan 

GCMS Scan 

GClMS Scan 

GClMS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 


Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GClMS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCMS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GClMS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GAMMA 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

1258746-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

1258746-1 

12587-46-1 

221-95 

222-95 

23-94 

2414-94 

2415-94 

2693-94 

2862-94 

2863-94 

289-94 

290-94 

438-95 

439-95 

508-94 

509-94 

634-95 

63195 

788-95 

789-95 

902-94 

903-94 

957-95 

958-95 

395-92 

1075-93 

1 i4a-95 

1149-95 

1205-93 

1205-94 

1206-93 

1206-94 

1349-93 

137493 

1379-94 

1380-94 

1549-93 

1550-93 

1615-94 

1616-94 

ima-93 

1921 -94 

1922-94 

20-94 

21-95 

212494 

2125-94 

2155-93 

2161 -93 

22-95 

221-95 

222-95 

23-94 

241494 

2415-94 

2693-94 

2862-94 

2863-94 

289-94 

290-94 

395-92 

438-95 

439-95 

50894 

634-95 

635-95 

788-95 

789-95 

803-93 

902-94 

903-94 

957-95 

95895 

O3FEBl995 

O3FEB1995 

OSJANl994 

070CT1994 

070CT1994 

04NOV1994 

02DEC1994 

02DEC1994 

04FEB1994 

04FEB1994 

03MAR1995 

03MAR1995 

03MAR1994 

03MAR1994 

05APR1995 

05APR1995 

O3MAY 1995 

O3MAYl995 

08APR1994 

08APRl994 

01 JUN1995 

01 JUN1995 

3OJANl992 

16JUL1993 

06JULl995 

06JUL1995 

OSAUGl993 

osMAY1994 

05AUG1993 

M Y 1994 

02SEP1993 

02SEPl993 

03JUN1994 

O3JUN1994 

05OCTl993 

050CT1993 

01 JULl994 

01 JUL1994 

04NOV1993 

05AUG1994 

05AUG1994 

05JAN 1994 

05JAN1995 

OZSEPl994 

02SEPl994 

10DEC1993 

lODEC1993 

05JAN1995 

03FEB1995 

03FEB1995 

05JAN1994 

070CT1994 

070CT1994 

04NOV1994 

OZDEC 1994 

OZDECl994 

04FEB1994 

04FEB1994 

30JAN1992 

03MAR1995 

03MAR1995 

03MAR1994 

05APR 1995 

05APRl995 

03MAY 1995 

03MAY1995 

02JUN1993 

08APR1994 

08APR1994 

01JUN1995 

OlJUNl995 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

l.OOE+OO O.OOE+OO 

l.OOE+OO 4.00E-01 

2.00E+00 6.00E-01 

-2.00E+00 l.lOE+OO 

1.00E+00 9.00E-01 

-l.OOE+OO 3.00E-01 

l.OOE+OO l.OOE+OO 

6.00E+00 3.10E+00 

5.00E+00 2.80E+00 

0.00E+00 6.00E-01 

1.00E+00 7.00E-01 

5.00E+00 2.50E+00 

-3.00E+00 1.40E+00 

1.00E+00 8.00E-01 

l.OOE+OO 8.00E-01 

-2.00E+00 9.00E-01 

l.OOE+OO 7.00E-01 

1.00E+00 7.00E-01 

-2.00E+00 9.00E-01 

O.OOE+OO 8.00E-01 

2.00E+00 9.00E-01 

2.00E+00 9.00E-01 

O.OOE+OO 1.00E-01 

O.OOE+OO 2.00E-01 

2.00E+00 7.00E-01 

l.OOE+OO 5.00E-01 

2.00E+00 l.lOE+OO 

-2.00E+00 8.00E-01 

1.00E+00 8.00E-01 

l.OOE+OO l.OOE+OO 

l.OOE+OO 5.00E-01 

1.00E+00 7.00E-01 

1.00€+00 7.00E-01 

1.00E+00 5.00E-01 


-3.00E+00 

l.OOE+OO 1.40E+00 

l.OOE+OO 8.00E-01 

-l.WE+OO 6.00E-01 

0.00E+00 -2.00E-01 

0.00E+00 -2.00E-01 

O.OOE+OO -1.00E-01 

0.00E+00 2.00E-01 

3.OOE+00 l.OOE+OO 

O.OOE+OO 6.00E-01 

0.00E+00 6.00E-01 

-2.00E+00 -1.70E+00 

5.00E+00 2.00E+00 

V 

X 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

X 

X 

V 

V 

V 

V 

Q 

Q 

Q 

Q 

Q 

Q 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ug1L 

uglL 

uglL 

uglL 

uglL 

ugfl 

uglL 

uglL 

uglL 

uglL 

pCilL 

pCilL 

pcin 

pCiL 

pCiL 

pCiL 

pCilL 

pCilL 

pCilL 

pCi 

pCiL 

pCilL 

pCilL 

pCi 

pCiL 

pciR 

pcin 

pCi 

pCilL 

pCilL 

pCilL 

pCiL 

pCilL 

pCilL 

pCilL 

pCiL 

pCiL 

pCiL 

pCilL 

pCiL 

pCilL 

pCiL 

pCiL 

pCilL 

pCilL 

pci5 

pCi 

pCilL 

pCiL 

pCiL 

pcin 

pCiL 

pCiR 

pCi 

pCi 

pCiL 

pCilL 

pciR 

pCiL




Gross Beta 12587-47-2 1075-93 16JUL1993 WS 6.00E+00 1.00E+00 N pCtL 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

























12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

im7-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

I 2587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

I 2587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

I 2587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

1258747-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

CAC03HARDNES 

CACO3HARDNES 

CACOJHARDNES 

CACOJHARDNES 

CACO3HARDNES 

CACOJHARDNES 

CACOJHARDNES 

CAC03HARDNES 

CAC03HARDNES 

CAC03HARDNES 

CACOJHARDNES 

CACOJHARDNES 

CACOJHARDNES 

CAC03HARDNES 

CACOJHARDNES 

CACOJHARDNES 

CAC03HARDNES 

CACOJHARDNES 

CACO3HARDNES 

CACO3HARDNES 

CACO3HARDNES 

CACO3HARDNES 

CACO3HARDNES 

CAC03HARDNES 

1148-95 

1149-95 

1205-93 

1205-94 

1206-93 

1206-94 

1349-93 

1374-93 

1379-94 

1380-94 

1549-93 

1550-93 

1615-94 

1616-94 

1838-93 

1921-94 

1922-94 

20-94 

21-95 

2124-94 

2125-94 

2155-93 

2161 -93 

22-95 

221-95 

222-95 

23-94 

2414-94 

241594 

2693-94 

2862-94 

2863-94 

289-94 

290-94 

395-92 

43895 

439-95 

508-94 

634-95 

635-95 

788-95 

789-95 

803-93 

902-94 

903-94 

957-95 

95895 

1075-93 

1205-93 

1205-94 

1206-93 

1206-94 

1349-93 

1374-93 

1379-94 

1380-94 

1549-93 

1550-93 

1615-94 

1616-94 

1838-93 

1921-94 

1922-94 

20-94 

21-95 

2124-94 

2125-94 

215593 

2161 -93 

22-95 

221-95 

06JUL1995 

06JUL1995 

OSAUGI 993 

05MAY1994 

05AUGl993 

O5MAY 1994 

O2SEPl 993 

02SEP1993 

03JUN1994 

O3JUNl 994 

050CT1993 

050CT1993 

01 JULl994 

OlJUL1994 

04NOV1993 

05AUG1994 

05AUG1994 

05JAN1994 

05JAN1995 

02SEPl994 

02SEP1994 

10DEC1993 

10DEC1993 

05JANl995 

03FEB1995 

03FEB1995 

WAN1994 

070CT1994 

070CT1994 

MNOVl994 

02DECl994 

02DECl994 

04FEBl994 

04FEBl994 

3OJAN1992 

03MAR1995 

03MARl995 

03MAR1994 

05APRl995 

05APRl995 

OJMAY I 995 

03MAY 1995 

02JUNl993 

08APR1994 

08APR1994 

01JUN1995 

01 JUN1995 

16JUL1993 

05AUGl993 

05MAY1994 

MAUGl993 

05MAY1994 

02SEP1993 

02SEPl993 

03JUN1994 

03JUNl994 

050CT1993 

05OCTl993 

01 JULl994 

OlJULl994 

04NOVI993 

05AUG1994 

MAUGl994 

WAN1 994 

WAN1995 

02SEPl994 

02SEP1994 

lODEC1993 

lODECl993 

WAN1995 

03FEB1995 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

X 

X 

pCiL 

pCiL 

pCiL 

pCVL 

pCVL 

pCVL 

pCilL 

pCilL 

pCiL 

pci5 

pCVL 

pCVL 

pciR 

pciR 

pCtL 

pCiR 

pCilL 

pci5 

pCVL 

pCi 

pCVL 

pCiL 

pCVL 

pCVL 

pci5 

pCiL 

pCiL 

pCiL 

pcin 

pCilL 

pCiL 

pCi 

pCi 

pCiL 

pCiL 

pCVL 

pCVL 

pCiL 

pCi 

pCilL 

pCiL 

pcin 

pCiL 

pCiL 

pci5 

pCiL 

pci5 

mglL CaC03 

mgR CaC03 

mgR CaC03 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mglL CaC03 

mgR CaC03 

mglL CaCO3 

mglL CaC03 

mgR CaC03 

mglL CaCO3 

mglL CaC03 

mgR CaC03 

mglL CaC03 

mgR CaC03 

mgR CaC03 

mglL CaC03 

mgR CaC03 

mgR CaC03 

mglL CaCO3



Hardness as CaCO3 CACOJHARDNES 222-95 03FEB1995 WS 6.40E+01 mglL CaCO3 


CACOJHARDNES 23-94 05JAN1994 ws 8.00E+01 

mi/L C ~ C O ~ 


CAC03HARDNES 2414-94 07OCT1994 ws 7.20E+01 

mglL CaC03 


CACOJHARDNES 2415-94 070CT1994 ws 7.00E+01 

mg/L CaC03 


CACOJHARDNES 2693-94 04NOV1994 ws 7.20E+01 

mglL CaC03 


CACOSHARDNES 2862-94 O2DECl 994 ws 7.20E+01 

mglL CaC03 


CACOJHARDNES 2863-94 02DEC1994 ws 7.40E+01 

mglL CaCO3 


CACOJHARDNES 289-94 04FEB1994 ws 6.60E+01 

mglL CaCO3 


CAC03HARDNES 290-94 04FEBl994 ws 7.40E+01 

mglL CaC03 


CAC03HARDNES 438-95 03MAR1995 ws 6.20E+01 

mg/L CaC03 


CAC03HARDNES 439-95 03MAR1995 ws 6.40E+01 

mg/L CaC03 


CACOJHARDNES 508-94 O3MARl 994 ws 7.00E+01 

mglL CaC03 

Hardness as CaCO3 CACOJHARDNES 509-94 03MARl994 ws 7.00Et01 

mglL CaC03 

Hardness as CaCO3 CACO3HARDNES 634-95 05APRl995 ws 6.40E+01 

mglL CaC03 


CACOJHARDNES 635-95 OMPR 1995 ws 6.40E+01 

mglL CaC03 


CAC03HARDNES 788-95 03MAY1995 ws 4.00E+01 

X mglL CaCO3 

Hardness as CaCO3 CAC03HARDNES 789-95 03MAY 1995 ws 5.20E+01 

mg/L CaC03 


CACOJHARDNES 803-93 O2JUNl 993 ws 8.60E+01 

N mglL CaC03 


CAC03HARDNES 902-94 08APRl994 ws 6.00E+01 

mg1L CaC03 


CACOJHARDNES 903-94 OBAPR1994 ws 6.60E+01 

mglL CaC03 


CACOMARDNES 957-95 01JUN1995 ws 6.00E+01 

mglL CaC03 


CACOJHARDNES 958-95 01JUN1995 ws 6.20E+01 

mglL CaC03 

Hexavalent Chromium 18540-29-9 

21-95 05JAN1995 ws O.OOE+OO 

C 

N 

mglL 


22-95 05JANI 995 ws O.OOE+OO 

< 

N 

mglL 


221-95 03FEB1995 ws O.OOE+OO 

< 

N 

mglL 


222-95 O3FEBl995 ws O.OOE+OO 

< 

N 

mglL 


438-95 OM1995 ws O.OOE+OO 

C 

N mgk 


439-95 03MAR1995 ws O.OOE+OO 

< 

N 

mglL 


634-95 05APR1995 ws O.OOE+OO 

< 

N 

mglL 


635-95 05APRl995 ws O.OOE+OO 

< 

N 

mglL 


788-95 03MAY 1995 ws O.OOE+W 

< 

N 

mglL 


789-95 03MAY1995 ws O.WE+OO 

< 

N 

mglL 


957-95 01 JUN1995 ws O.OOE+OO 

< 

N 

mglL 


958-95 01 JUNI 995 ws O.OOE+OO 

4 

N 

mglL 

Iron 

7439-89-6 

1024-92 WAY1992 ws l.OOE+OO 

NT mglL 

Iron 

7439-89-6 

1075-93 16JULl993 ws l.WE+OO 

N 

mglL 

Iron 

7439-89-6 

1144-92 01JUNl992 ws O.OOE+OO 

N 

mglL 

Iron 

7439-89-6 

1205-93 05AUG1993 ws O.OOE+OO 

N 

mglL 

Iron 

7439-89-6 

1205-94 WAY1994 ws 1.00E+00 

mglL 

Iron 

7439-89-6 

1206-93 05AUGl993 ws 1 .WE+W 

N 

mglL 

Iron 

7439-89-6 

1206-94 05MAY I 994 ws l.OOE+OO 

mglL 

Iron 

7439-89-6 

1333-92 06JULl992 ws I .00E+00 

N 

mglL 

Iron 

7439-89-6 

1349-93 02SEPl993 ws l.OOE+OO 

N 

mgk 

Iron 

7439-89-6 

1374-93 02SEP1993 ws 2.WE+W 

N 

mglL 

Iron 

7439-89-6 

1379-94 03JUN1994 ws O.WE+OO 

mglL 

Iron 

7439-89-6 

1380-94 03JUN1994 ws O.WE+W 

mglL 

Iron 

7439-89-6 

1478-92 03AUGl992 ws l.OOE+OO 

N 

mglL 

Iron 

7439-89-6 

1549-93 050CTI993 ws l.OOE+OO 

N 

mglL 

Iron 

7439-89-6 

1550-93 050CT1993 ws I .00E+W 

N 

mglL 

Iron 

7439-89-6 

1615-94 

OlJUL1994 ws 1.00E+W 

mglL 

Iron 

7439-89-6 

1616-94 01 JUL1994 ws O.OOE+W 

mglL 

Iron 

7439 -89- 6 

1625-92 31 AUG 1992 ws 1 .WE+OO 

N 

mglL 

Iron 

7439-89-6 

1797-92 070CT1992 ws l.OOE+OO 

N 

mgk 

Iron 

7439-89-6 

1838-93 MNOVl993 ws l.WE+OO 

mglL 

Iron 

7439-89-6 

1921-94 05AUGl994 ws l.OOE+OO 

mglL 

Iron 

7439-89-6 

1922-94 05AUG1994 ws 2.00E+W 

mglL 

Iron 

7439-89-6 

1938-92 O3NOVl 992 ws 1 .OOE+W 

N 

mglL 

Iron 

7439-89-6 

20-94 05JAN1994 ws l.OOE+OO 

rnglL 

Iron 

7439-89-6 

21-95 05JAN1995 ws 1.00E+W 

mglL 

Iron 

7439-89-6 

2102-92 01 DECl992 ws 1.00E+00 

N 

mgk 

Iron 

7439-89-6 

2124-94 02SEPl994 ws O.OOE+OO 

mglL 

Iron 

7439-89-6 

2125-94 02SEP1994 ws O.WE+OO 

mglL 

Iron 

7439-89-6 

2155-93 IODEC1993 ws I .WE+00 

mglL 

Iron 

7439-89-6 

2161-93 I ODEC1993 ws I.WE+W 

mglL 

Iron 

7439-89-6 

22-95 05JAN1995 ws I .WE+W 

mgk 

Iron 

7439-89-6 

221-95 03FEB1995 ws 1 .WE+00 

mglL 

Iron 

7439-89-6 

222-95 03FEB1995 ws 1 .WE+00 

rngk 

Iron 

7439-89-6 

23-94 05JAN1994 ws I.WE+W 

mgk 

Iron 

7439-89-6 

2414-94 

070CT1994 ws O.WE+OO 

mgk 

Iron 

7439-89-6 

2415-94 070CT1994 ws O.WE+W 

mglL 

Iron 

7439-89-6 

2693-94 04NOVl994 ws l.WE+W 

mgfl 

Iron 

7439-89-6 

2862-94 02DEC1994 ws I.WE+OO 

mglL 

Page 77 of 176



ANALYTE CAS NUMBER SAMPLE ID DATE NPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Iron 7439-89-6 2863-94 02DEC1994 WS 1.00E+00 mplL 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-89-6 

7 4 3 9 - 8 9 - 6 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

289-94 

290-94 

395-92 

439-95 

508-94 

623-93 

632-92 

634-95 

635-95 

637-93 

701 -92 

788-95 

789-95 

803-93 

856-92 

902-94 

903-94 

1024-92 

1075-93 

1 144-92 

120593 

1205-94 

1206-93 

1333-92 

1374-93 

1379-94 

43895 

1206-94 

1349-93 

1380-94 

1478-92 

1549-93 

1550-93 

1615-94 

1616-94 

1625-92 

1797-92 

1838-93 

1921-94 

1938-92 

20-94 

21-95 

2 102-92 

2124-94 

2155-93 

2161-93 

22-95 

221-95 

222-95 

23-94 

2414-94 

2415-94 

2693-94 

2862-94 

2863-94 

289-94 

290-94 

395.92 

438-95 

439-95 

50894 

623-93 

632-92 

634-95 

635-95 

637-93 

701-92 

1922-94 

2125-94 

78895 

789-95 

04FEB1994 

04FEB1994 

30JANI 992 

O3MAR 1995 

03MAR1995 

03MAR1994 

O5MAY 1993 

05MAR1992 

05APR1995 

05APR1995 

05MAY 1993 

12MARl992 

03MAY 1995 

03MAY1995 

02JUN1993 

01 APRI 992 

08APR1994 

08APR1994 

04MAY 1992 

16JUL1993 

01 JUNl992 

05AUG1993 

OSMAY 1994 

05AUGl993 

05MAYl994 

06JULl992 

O2SEPl 993 

02SEP1993 

03JUN1994 

03JUN 1994 

03AUG1992 

050CT1993 

050CT1993 

OlJUL1994 

OlJULl994 

3lAUGl992 

070CT1992 

04NOV1993 

05AUG1994 

OSAUGl994 

03NOVl992 

WAN1994 

WAN1995 

01 DECl992 

02SEP1994 

O2SEPl 994 

IODECl993 

1 ODECl993 

WAN1995 

03FEBl995 

03FEBl995 

WAN1994 

070CT1994 

070CT1994 

04NOVI994 

02DEC1994 

O2DEC1994 

04FEB1994 

ME81994 

3OJANl992 

ow1995 

ow1995 

03MARl994 

OSMAY I 

993 

05MAR1992 

05APRl995 

05APR1995 

(HMAY 1 993 

12MAR1992 

OWY 

1995 

03MAY 1995 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

4 

< 

< 

< 

< 

< 

< 

< 

e 

< 

U 

< 

< 

< 

< 

c 

U 

< 

< 

< 

< 

< 

c 

U 

U 

c 

< 

< 

U 

U 

< 

< 

< 

U 

U 

< 

< 

U 

U 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mg/L 

mglL 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mgfl 

mglL 

mglL 

mgfl 

mgfl 

mgfl 

mg5 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

mg1L 

mgn 

mglL 

mglL 

mgfl 

mg5 

wn 

w5 

mgfl 

w5 

mgfl 

mgfl 

mgk 

Page 78 of 176




7439-92-1 803-93 02JUN1993 WS O.OOE+OO mglL 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lithium 

Lithiurn 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Lithium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-954 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-954 

7439.954 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-92-1 

856-92 

902-94 

903-94 

957-95 

958-95 

1024-92 

1144-92 

1333-92 

1478-92 

1625-92 

1938-92 

2102-92 

395-92 

623-93 

632-92 

701-92 

856-92 

1797-92 

1024-92 

1075-93 

1144-92 

1205-93 

1205-94 

1206-94 

1333-92 

1349-93 

1374-93 

1379-94 

1380-94 

1549-93 

1550-93 

161 5-94 

1616-94 

1206-93 

1478-92 

1625-92 

1797-92 

1838-93 

1938-92 

1921-94 

1922-94 

20-94 

21-95 

2 102-92 

2124-94 

2125-94 

2155-93 

2161-93 

22-95 

221-95 

222-95 

23-94 

2414-94 

2415-94 

2862-94 

2863-94 

289-94 

290-94 

395-92 

438-95 

439-95 

50894 

623-93 

634-95 

635-95 

637-93 

701-92 

788-95 

789-95 

2693-94 

632-92 

01 APRl992 

08APR1994 

08APR1994 

01JUN1995 

01JUN1995 

04MAYl992 

01 JUN1992 

06JULl992 

03AUGl992 

3lAUGl992 

070CT1992 

03NOV1992 

01DEC1992 

3OJAN1992 

O5MAY 1993 

05MAR1992 

12MAR1992 

01 APRl992 

04MAY 1992 

16JUL1993 

OlJUNl992 

05AUG1993 

05MAY 1994 

05AUG1993 

OSMAYl994 

06JULl992 

02SEP1993 

OZSEPl993 

03JUNl994 

03JUN1994 

03AUGl992 

050CT1993 

050CTl993 

01 JULl994 

OlJUL1994 

3lAUGl992 

070CT1992 

04NOV1993 

05AUG1994 

05AUGl994 

03NOV1992 

05JAN1994 

05JAN1995 

01DECl992 

02SEP1994 

O2SEPl994 

lODECl993 

lODECl993 

05JAN1995 

03FEBl995 

03FEB1995 

05JAN1994 

070CT1994 

070CT1994 

04NOV1994 

02DEC1994 

02DEC1994 

04FEB1994 

04FEBl994 

30JAN1992 

03MARl995 

OW1995 

03MAR1994 

05MAY1993 

05MAR1992 

05APRl995 

05APRl995 

MAY 

1993 

12MARl992 

03MAYl995 

03MAY1995 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

c 

N 

< N 

< N 

< N 

U 

N 

U 

N 

c 

NT 

c 

N 

< N 

c 

N 

c 

N 

< N 

c 

N 

c 

N 

< N 

c 

N 

< N 

< N 

c 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

mglL 

mg1L 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mgfl 

mglL 

mg/L 

mglL 

mgfl 

wfl 

mglL 

mglL 

mglL 

mglL 

mgfl 

mgfl 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mg/L 

mglL 

mglL 

mgfl 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mg5 

mglL 

mgfl 

mglL 

mgfl 

mgfl 

mglL 

mg/L 

mglL 

Page 79 of 176



Magnesium 7439-95-4 803-93 02JUN1993 WS 5.00€+00 N mg1L 

Magnesium 

Magnesium 

Magnesium 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

7439-95-4 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

856-92 

902-94 

903-94 

1024-92 

1075-93 

1144-92 

1205-93 

1205-94 

1206-93 

1206-94 

1333-92 

1349-93 

1374-93 

1379-94 

1380-94 

1478-92 

1549-93 

1550-93 

1615-94 

1616-94 

1797-92 

1838-93 

1922-94 

1938-92 

20-94 

21-95 

2102-92 

2124-94 

2125-94 

2155-93 

21 61 -93 

22-95 

221-95 

222-95 

23-94 

2414-94 

2415-94 

2693-94 

2863-94 

289-94 

290-94 

395-92 

438-95 

439-95 

508-94 

623-93 

632-92 

634-95 

635-95 

637-93 

701-92 

788-95 

789-95 

803-93 

1625-92 

1921 

-94 

2862-94 

856-92 

902-94 

903-94 

1024-92 

1144-92 

1333-92 

1478-92 

1549-93 

1550-93 

1625-92 

1797-92 

1938-92 

395-92 

2102-92 

01 APRI 992 

08APRl994 

08APRl994 

04MAY1992 

16JULl993 

01JUN1992 

OSAUG1993 

OSMAY 1994 

05AUG1993 

05MAY 1994 

06JUL1992 

02SEPI 993 

02SEPl993 

03JUN1994 

O3JUNl 994 

03AUG1992 

050CT1993 

050CT1993 

01 JUL1994 

OlJULl994 

3 1 AUG 1992 

070CT1992 

04NOV1993 

O5AUGl 994 

OSAUG1994 

03NOV1992 

WAN1994 

WAN1995 

01 DECl992 

02SEPl994 

02SEP1994 

1 ODECI 993 

IODECI 993 

WAN1995 

03FEB1995 

03FE61995 

05JAN1994 

070CT1994 

070CT1994 

04NOV1994 

02DEC1994 

02DEC1994 

04FEBI994 

MFEB1994 

30JANl992 

03MAR1995 

03MAR1995 

03MAR1994 

05MAY1993 

05MAR1992 

05APRl995 

05APRI995 

05MAY 1993 

12MAR1992 

03MAY1995 

OMAY 1995 

02JUNl993 

01APRl992 

08APR1994 

08APR1994 

MAY1992 

01JUNl992 

06JUL1992 

03AUG1992 

050CT1993 

OSOCTI 993 

3lAUGl992 

070CT1992 

03NOV1992 

OlDEC1992 

30JAN1992 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

J.OOE+OO 

3.00E+00 

3.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+W 

0.00E+00 

O.OOE+W 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+W 

O.OOE+OO 

O.OOE+W 

O.WE+OO 

O.WE+OO 

O.OOE+OO 

O.WE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.WE+OO 

0.WEtW 

O.WE+W 

O.WE+OO 

O.OOE+OO 

O.WE+OO 

O.OOE+W 

O.WE+W 

0.00E+00 

O.OOE+OO 

O.OOE+W 

0.WEt00 

0.00E+00 

O.OOE+W 

O.WE+W 

O.WE+W 

O.OOE+W 

O.WE+W 

O.WE+W 

O.WE+W 

O.OOE+OO 

O.WE+W 

O.WE+OO 

O.WE+OO 

O.WE+W 

O.WE+W 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Page 80 of 176




Mercury 7439-97-6 623-93 05MAY1993 WS O.OOE+OO 

NT mgIL 

Mercury 

7439-97-6 

632-92 O5MAR1992 ws 

N 

mg1L 

Mercury 

7439-97-6 

701-92 12MAR1992 ws 

N 

mglL 

Mercury 

7439-97-6 

856-92 01 APRl992 ws 

N 

mglL 


75-09-2 

1374-93 02SEP1993 ws 

N 

uglL 

Molybdenum 

7439-90-7 

1024-92 04MAY 1992 ws 

NT mglL 

Molybdenum 

7439-90-7 

1144-92 

01JUN1992 ws 

N 

mglL 

Molybdenum 

7439-90-7 

1333-92 MJULl992 ws 

N 

mg1L 

Molybdenum 

7439-90-7 

1470-92 O3AUGl 992 ws 

N 

mglL 

Molybdenum 

7439-90-7 

1625-92 31AUG1992 ws 

N 

mglL 

Molybdenum 

7439-90-7 

1797-92 070CT1992 ws 

N 

mglL 

Molybdenum 

7439-90-7 

1930-92 03NOV1992 ws 

N 

mg1L 

Molybdenum 

7439-90-7 

2102-92 01DEC1992 ws 

N 

mglL 

Molybdenum 

7439-90-7 

395-92 3OJAN1992 ws 

N 

mglL 

Molybdenum 

7439-90-7 

623-93 OSMAY1993 ws 

N 

mglL 

Molybdenum 

7439-90-7 

632-92 05MAR1992 ws 

N 

mglL 

Molybdenum 

7439-90-7 

701-92 12MAR1992 ws 

N 

mglL 

Molybdenum 

7439-90-7 

856-92 01 APRl992 ws 

N 

mglL 

Nickel 

7440-02-0 

1024-92 04MAY 1992 ws 

NT mglL 

Nickel 

7440-02-0 

1075-93 16JUL1993 ws 

N 

mglL 

Nickel 

7440-02-0 

1144-92 01 JUN 1992 ws 

N mgk 

Nickel 

7440-02-0 

1205-93 05AUG1993 ws 

N 

mgR 

Nickel 

7440-02-0 

1205-94 (HMAY 1994 ws 

N 

mglL 

Nickel 

7440-02-0 

1206-93 OSAUG 1993 ws 

N 

mglL 

Nickel 

7440-02-0 

1206-94 05MAY 1994 ws 

N 

mglL 

Nickel 

7440-02-0 

1333-92 06JUL1992 ws 

N 

mglL 

Nickel 

7440-02-0 

1349-93 O2SEP1 993 ws 

N 

WlL 

Nickel 

7440-02-0 

1374-93 OZSEPI 993 ws 

N 

mglL 

Nickel 

7440-02-0 

1379-94 03JUN 1994 ws 

N 

mglL 

Nickel 

7440-02-0 

1300-94 03JUN1994 ws 

N 

WlL 

Nickel 

7440-02-0 

1470-92 03AUGl992 ws 

N 

mglL 

Nickel 

7440-02-0 

1549-93 050CT1993 ws 

N 

mglL 

Nickel 

7440-02-0 

1550-93 050CT1993 ws 

N 

mglL 

Nickel 

7440-02-0 

1615-94 OlJUL1994 ws 

N 

mglL 

Nickel 

7440-02-0 

1616-94 

01 JULl994 ws 

N 

mglL 

Nickel 

7440-02-0 

1625-92 31 AUGl992 ws 

N 

mg1L 

Nickel 

7440-02-0 

1797-92 070CT1992 ws 

N 

mglL 

Nickel 

7440-02-0 

1830-93 04NOV1993 ws 

N 

mglL 

Nickel 

7440-02-0 

1921-94 05AUGl994 ws 

N 

mglL 

Nickel 

7440-02-0 

1922-94 OSAUG 1994 ws 

N 

mg/L 

Nickel 

7440-02-0 

1938-92 03NOV1992 ws 

N 

mgk 

Nickel 

7440-02-0 

20-94 05JAN1994 ws 

N 

mglL 

Nickel 

7440-02-0 

21-95 OSJAN1995 ws 

N 

mglL 

Nickel 

7440-02-0 

2102-92 01 DECl992 ws 

N 

mglL 

Nickel 

7440-02-0 

2124-94 02SEP1994 ws 

N 

mglL 

Nickel 

7440-02-0 

2125-94 02SEPl994 ws 

N 

mglL 

Nickel 

7440-02-0 

2155-93 10DEC1993 ws 

N 

mglL 

Nickel 

7440-02-0 

2161-93 10DEC1993 ws 

N 

mglL 

Nickel 

7440-02-0 

22-95 05JAN1995 ws 

N 

mglL 

Nickel 

7440-02-0 

221-95 03FEB1995 ws 

N 

mgk 

Nickel 

7440-02-0 

222-95 03FEB1995 ws 

N 

WlL 

Nickel 

7440-02-0 

23-94 05JAN1994 ws 

N 

mglL 

Nickel 

7440-02-0 

2414-94 070CT1994 ws 

N 

mglL 

Nickel 

7440-02-0 

2415-94 070CT1994 ws 

N 

mglL 

Nickel 

7440-02-0 

2693-94 04NOV1994 ws 

N 

mglL 

Nickel 

7440-02-0 

2862-94 02DEC1994 ws 

N 

mglL 

Nickel 

7440-02-0 

2863-94 OZDEC1994 ws 

N 

mglL 

Nickel 

7440-02-0 

209-94 04FEB1994 ws 

N 

mglL 

Nickel 

7440-02-0 

290-94 04FEB1994 ws 

N 

mgk 

Nickel 

7440-02-0 

39592 3OJANl 992 ws 

N 

mglL 

Nickel 

7440-02-0 

438-95 O3MARl995 ws 

N 

WlL 

Nickel 

7440-02-0 

439-95 03MARI 995 ws 

N 

mglL 

Nickel 

7440-02-0 

508-94 03MAR 1994 ws 

N 

mg/L 

Nickel 

7440-02-0 

623-93 (HMAY 1993 ws 

N 

mglL 

Nickel 

7440-02-0 

632-92 OSMARI 992 ws 

N 

mgfl 

Nickel 

7440-02-0 

634-95 OSAPRl995 ws 

N 

mglL 

Nickel 

7440-02-0 

635-95 OSAPR1995 ws 

N 

WlL 

Nickel 

7440-02-0 

637-93 05MAY 1993 ws 

N 

mglL 

Nickel 

7440-02-0 

701-92 1 ZMAR I992 ws 

N 

mglL 

Nickel 

7440-02-0 

788-95 03MAY 1995 ws 

N 

WlL 

Nickel 

7440-02-0 

789-95 03MAY1995 ws 

N 

mg1L 

Nickel 

7440-02-0 

803-93 02JUN1993 ws 

N 

mglL 

Page 81 of 176

~~ 




Nickel 7440-02-0 856-92 01APR1992 WS O.OOE+OO C N mglL 

Nickel 

Nickel 

7440-02-0 

7440-02-0 

902-94 

903-94 

08APR1994 

08APR1994 

C 

C 

N 

N 

Niobium 

7440-03-1 

1024-92 04MAY 1992 

C 

NT 

Niobium 

7440-03-1 

1144-92 

OlJUN1992 

C 

N 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 

Niobium 



7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

NITRATEASNIT 

SO227 

1333-92 

1478-92 

1625-92 

1797-92 

1938-92 

2102-92 

395-92 

623-93 

632-92 

701-92 

856-92 

395-92 

395-92 

06JUL1992 

03AUGl992 

3lAUGl992 

070CT1992 

03NOV1992 

01 DEC1992 

30JAN1992 

%MAY 1993 

O5MAR1992 

12MARl992 

01 APRI 992 

3OJANl992 

30JAN1992 

C 

C 

C 

C 

C 

C 

C 

C 

C 

C 

C 

C 

C 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

pca 

1336-36-3 

1864-92 190CT1992 

C 

N 

pca 

1336-36-3 

1938-92 03NOV1992 

C 

N 

PCB 

1336-36-3 

20-94 05JAN1994 

C 

N 

PCB 

PCB 














Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

1336-36-3 

1336-36-3 

7723-14-0 

7723-14-0 

7723- 14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

23-94 

395-92 

1024-92 

I 144-92 

1333-92 

147892 

1625-92 

1797-92 

1938-92 

2102-92 

395-92 

623-93 

632-92 

701-92 

856-92 

1024-92 

1075-93 

1144-92 

1205-93 

1205-94 

1206-93 

1206-94 

1333-92 

1349-93 

1374-93 

1379-94 

1380-94 

1478-92 

1549-93 

1550-93 

1615-94 

161694 

1625-92 

1797-92 

183893 

1921-94 

1922-94 

193892 

20-94 

21-95 

2102-92 

2124-94 

2125-94 

2155-93 

2161 -93 

22-95 

221-95 

222-95 

23-94 

2414-94 

2415-94 

O5JAN 1994 

30JANl992 

04MAY 1992 

01 JUNl992 

06JULl992 

03AUGl992 

3lAUGI 992 

070CT1992 

03NOV1992 

OlDECl992 

30JANl992 

WY1993 

osMARl992 

12MAR1992 

OlAPR1992 

04MAY1992 

16JUL1993 

01JUN1992 

05AUGl993 

05MAY 1994 

05AUG1993 

05MAY 1994 

06JUL1992 

02SEPl993 

02SEPl993 

03JUNl994 

03JUNl994 

03AUG 1992 

OSET1993 

050CTI993 

01JULl994 

01 JULl994 

31AUGl992 

070CT1992 

04NOV1993 

05AUGl994 

05AUG 1994 

03NOV1992 

05JAN1994 

05JAN1995 

OlDECl992 

02SEP1994 

02SEPl994 

1 ODECl993 

10DECl993 

osJANl995 

03FEB1995 

03FEBl995 

05JAN1994 

070CT1994 

070CT1994 

C 

C 

< 

C 

C 

C 

4 

C 

C 

e 

< 

J 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws




Potassium 7440-09-7 2693-94 04NOV1994 WS 4.00E+00 N 

mglL 

Potassium 

7440-09-7 

2062-94 02DEC1994 ws 4.00E+00 

N 

mglL 

Potassium 

7440-09-7 

2063-94 02DEC1994 ws 4.00E+00 

N 

mglL 

Potassium 

7440-09-7 

209-94 04FEB1994 ws J.OOE+OO 

N 

mglL 

Potassium 

7440-09-7 

290-94 04FEB1994 ws 3.00E+00 

N 

mglL 

Potassium 

7440-09-7 

395-92 30JAN1992 ws 3.00E+00 

N 

mglL 

Potassium 

7440-09-7 

430-95 03MAR1995 ws 2.00E+00 

N 

mglL 

Potassium 

7440-09-7 

439-95 03MAR1995 ws 2.00E+00 

N 

mglL 

Potassium 

7440-09-7 

500-94 O3MARl 994 ws 2.00E+00 

N 

mglL 

Potassium 

7440-09-7 

623-93 05MAY 1993 ws 2.00E+00 

N 

mglL 

Potassium 

7440-09-7 

632-92 O5MAR 1992 ws 3.00E+00 

N 

mglL 

Potassium 

7440-09-7 

634-95 05APR 1995 ws 5.00E+00 

< 

N 

mgfl 

Potassium 

7440-09-7 

635-95 O5APR 1995 ws 5.00E+00 

< 

N 

mglL 

Potassium 

7440-09-7 

637-93 05MAY1993 ws 3.00E+00 

N 

mglL 

Potassium 

7440-09-7 

701-92 12MAR1992 ws 2.00E+00 

N 

mglL 

Potassium 

7440-09-7 

700-95 03MAY 1995 ws 3.00E+00 

N 

mglL 

Potassium 

7440-09-7 

709-95 03MAY 1995 ws 3.00E+00 

N 

mglL 

Potassium 

7440-09-7 

803-93 02 JUNl993 ws 3.00E+00 

N 

mg1L 

Potassium 

7440-09-7 

856-92 01 APRl992 ws 3.00E+00 

N 

mglL 

Potassium 

7440-09-7 

902-94 00APR1994 ws 2.00E+00 

< 

N 

mglL 

Potassium 

7440-09-7 

903-94 OBAPR1994 ws 2.00E+00 

N 

mglL 

Rad Alpha 

12507-46-1 

1140-95 06JUL1995 ws l.OOE+OO 

N pCilml 

Rad Alpha 

12507-46-1 

1149-95 

06JUL1995 ws 1.00E+00 

N pCilml 

Rad Alpha 

12587-46-1 

221-95 

03FEBl995 ws l.OOE+OO 

N pCilml 

Rad Alpha 

12507-46-1 

222-95 O3FEB1 995 ws l.OOE+OO 

N pCi/ml 

Rad Alpha 

12507-46-1 

438-95 03MARl995 ws l.OOE+OO 

N pCilml 

Rad Alpha 

12507-46-1 

439-95 03MAR1995 ws l.OOE+OO 

N pCiml 

Rad Alpha 

12507-46-1 

634-95 05APRl995 ws l.OOE+OO 

N pCilml 

Rad Alpha 

12587-46-1 


N pCilml 

Rad Alpha 

12587-46-1 

700-95 03MAY 1995 ws 1 .OOE+OO 

N pCiml 

Rad Alpha 

12507-46-1 

709-95 O3MAY 1995 ws l.OOE+OO 

N pCilml 

Rad Alpha 

12507-46-1 

003-93 02JUN1993 ws l.OOE+OO 

N pCilmL 

Rad Alpha 

12507-46-1 

957-95 01JUN1995 ws 1.00E+00 

N pCilml 

Rad Alpha 

12507-46-1 

950-95 01JUN1995 ws l.OOE+OO 

N pCilml 

Rad Beta 

12507-47-2 

1148-95 

06JULl995 ws l.OOE+OO 

N pCilml 

Rad Beta 

12507-47-2 

1149-95 06JUL1995 ws l.OOE+OO 

N pCiml 

Rad Beta 

12507-47-2 

221-95 03FEB1995 ws I .00E+00 

N pCVml 

Rad Beta 

12507-47-2 

222-95 03FEB1995 ws l.OOE+W 

N pCilml 

Rad Beta 

12507-47-2 

430-95 03MAR1995 ws l.OOE+OO 

N pCilml 

Rad Beta 

12507-47-2 

439-95 03MAR1995 ws l.OOE+OO 

N pCilml 

Rad Beta 

12507-47-2 


N pCilml 

Rad Beta 

12507-47-2 

635-95 05APR1995 ws l.OOE+OO 

N pCilml 

Rad Beta 

12507-47-2 

700-95 03MAY 1995 ws 1.00E+00 

N pCiml 

Rad Beta 

12507-47-2 

709-95 03MAY1995 ws l.OOE+OO 

N pCilml 

Rad Beta 

12587-47-2 

003-93 02JUN1993 ws l.OOE+OO 

N pCilmL 

Rad Beta 

12507-47-2 

957-95 OlJUNl995 ws l.WE+W 

N pCilml 

Rad Beta 

12507-47-2 

950-95 01JUN1995 ws l.OOE+W 

N pCilml 

Ruthenium 

7440-10-0 

1024-92 WMAY 1992 ws O.OOE+OO 

NT mglL 

Ruthenium 

7440-10-0 

1144-92 

01JUN1992 ws O.OOE+OO 

N 

mglL 

Ruthenium 

7440-10-0 

1333-92 06JUL1992 ws 0.00E+00 

N 

mglL 

Ruthenium 

7440-10-0 

1470-92 03AUG1992 ws O.WE+OO 

N 

mglL 

Ruthenium 

7440-10-0 

1625-92 3lAUG1992 ws O.OOE+OO 

N 

mglL 

Ruthenium 

7440-10-8 

1797-92 070CT1992 ws O.OOE+W 

N 

mglL 

Ruthenium 

7440-10-0 

1938-92 03NOV1992 ws O.OOE+OO 

N 

mglL 

Ruthenium 

7440-10-0 

2102-92 01 DEC1992 ws O.OOE+OO 

N 

mglL 

Ruthenium 

7440-10-0 

395-92 30JAN1992 ws O.OOE+OO 

N 

mglL 

Ruthenium 

7440-10-0 

623-93 05MAY 1993 ws O.OOE+OO 

N 

mglL 

Ruthenium 

7440-10-0 

632-92 05MAR1992 ws O.OOE+OO 

N 

mglL 

Ruthenium 

7440-10-0 

701-92 12MAR1992 ws O.WE+OO 

N 

mglL 

Ruthenium 

7440-10-0 

856-92 01 APRI 992 ws O.WE+OO 

N 

mglL 

Selenium 

7702-49-2 

395-92 30JANl992 ws O.WE+W 

N 

mglL 

Silicon 

7440-21-3 

1024-92 WMAY 1992 ws 2.00E+00 

NT mglL 

Silicon 

7440-21 -3 

1075-93 16JUL1993 ws 3.00E+00 

N 

mglL 

Silicon 

7440-21-3 

1144-92 01 JUN1992 ws l.OOE+OO 

N 

mglL 

Silicon 

7440-21-3 

1205-93 OSAUGl993 ws 2.WE+W 

N 

mglL 

Silicon 

7440-21-3 

1205-94 OSMAY 1994 ws 6.00E+00 

N 

mglL 

Silicon 

7440-21 -3 

1206-93 OBAUGl993 ws 2.00E+00 

N 

mglL 

Silicon 

7440-21-3 

1206-94 (HMAY 1994 ws 5.00E+W 

N 

mglL 

Silicon 

7440-21-3 

1333-92 06JUL1992 ws 2.00E+00 

N 

mglL 

Silicon 

7440-21-3 

1349-93 02SEPl993 ws l.OOE+OO 

N 

mglL 

Silicon 

7440-21-3 

1374-93 O2SEP1 993 ws l.OOE+OO 

N 

mglL 

Silicon 

7440-21-3 

1379-94 03JUNl994 ws 2.WE+00 

N 

mglL 

Page 83 of 176


MEDIA FAD RESULT VALIDATION 


Silicon 7440-21-3 1380-94 03JUN1994 WS l.OOE+OO N mglL 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

1478-92 

1549-93 

1550-93 

1615-94 

1616-94 

1625-92 

1797-92 

1838-93 

1921-94 

1922-94 

1938-92 

20-94 

21-95 

2102-92 

2124-94 

2125-94 

2155-93 

2161-93 

22-95 

221-95 

222-95 

23-94 

2414-94 

2415-94 

2693-94 

2862-94 

2863-94 

289-94 

290-94 

395-92 

438-95 

439-95 

508-94 

623-93 

632-92 

634-95 

635-95 

637-93 

701-92 

788-95 

789-95 

803-93 

856-92 

902-94 

903-94 

1024-92 

1144-92 

1333-92 

1478-92 

1625-92 

1797-92 

1938-92 

2102-92 

395-92 

623-93 

632-92 

701-92 

856-92 

1024-92 

1075-93 

1144-92 

1205-93 

1205-94 

1206-93 

1206-94 

1333-92 

1349-93 

1374-93 

1379-94 

1380-94 

1478-92 

03AUG1992 

050CT1993 

050CT1993 

OlJUL1994 

OlJUL1994 

3lAUGl992 

070CT1992 

04NOV1993 

05AUG1994 

05AUG1994 

03NOV1992 

05JAN1994 

05JAN1995 

01 DEC1992 

02SEP1994 

OZSEPI 994 

10DECl993 

lODECl993 

05JAN1995 

03FEB1995 

03FEB1995 

05JANl994 

070CT1994 

O7OCTI 994 

04NOV1994 

O2DECl 994 

02DEC1994 

04FEB1994 

04FEB1994 

30JANl992 

03MAR1995 

03MAR1995 

03MAR1994 

05MAYl993 

05MAR1992 

05APRl995 

05APR1995 

OSMAY 1993 

12MARI 992 

03MAYl995 

03MAY 1995 

02JUNl993 

OlAPR1992 

08APRl994 

08APRl994 

04MAY 1992 

OlJUNl992 

06JUL1992 

03AUG1992 

31 AUG1992 

070CT1992 

03NOV1992 

01 DECl992 

30JAN1992 

(HMAY 1993 

(HMARl992 

12MARl992 

01 APRl992 

04MAY 1992 

16JUL1993 

01 JUNl992 

MAUGl993 

M Y 1994 

MAUGl993 

05MAY 1994 

06JUL1992 

02SEPl993 

02SEP1993 

O3JUN1994 

OJJlJN1994 

03AUGl992 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

2.00E+00 

3.00E+00 

3.00E+00 

2.00E+00 

2.00E+00 

2.00E+00 

5.00E+00 

2.00E+00 

J.OOE+OO 


3.00E+00 


3.00E+00 

5.00E+00 

2.00E+00 

2.00E+00 

6.00E+00 

5.00E+00 

3.WE+OO 

6.00E+00 

5.00E+00 

4.WE+OO 

2.00E+00 

2.00E+00 

2.00E+00 

3.OOE+00 

3.00E+00 

6.00E+00 

6.00E+00 

2.00E+00 



6.00E+00 

6.00E+00 

2 .OOE+ 00 

2.00E+00 

2 .OOE+OO 

6.00E+00 


7.WE+W 

7.00E+00 

2.00E+W 

5.00E+00 

6.00E+00 

6.WE+00 

O.OOE+OO 

O.WE+OO 

O.OOE+OO 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+W 

O.WE+W 

O.OOE+OO 

O.OOE+OO 

I .80E+01 

2.10E+01 

2.20E+OI 

2.3OE+Ol 

l.WE+OI 

2.30E+01 

l.OOE+OI 

I .80E+01 

2.10E+01 

2.2OE+O1 

2.20E+01 

2.2OE+Ol 

1.70E+01 

C 

J 

J 

J 

B 

B 

J 

J 

< 

C 

< 

< 

c 

< 

C 

< 

c 

c 

c 

< 

c 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

' N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mg1L 

mglL 

mg/L 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg5 

mglL 

mglL 

mglL 

mgfl 

mglL 

mgk 

mg/L 

mglL 

mgfl 

wfl 

mgfl 

wfl 

wfl




Sodium 

7440-23-5 1549-93 050CT1993 WS 1,80E+01 N mglL 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 










Speck conductance 

Specfic conductance 


















7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

SO145 

SO145 

SO1 45 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

1550-93 

1615-94 

1616-94 

1625-92 

1797-92 

1838-93 

I921 -94 

1922-94 

1938-92 

20-94 

21 -95 

2102-92 

2124-94 

2125-94 

2155-93 

2161 -93 

22-95 

221-95 

222-95 

23-94 

2414-94 

2415-94 

2693-94 

2862-94 

2863-94 

289-94 

290-94 

395-92 

438-95 

439-95 

508-94 

623-93 

632-92 

634-95 

635-95 

637-93 

701-92 

78895 

789-95 

803-93 

856-92 

902-94 

903-94 

1075-93 

I 148-95 

1149-95 

1205-93 

1205-94 

1206-93 

1206-94 

1349-93 

1374-93 

1379-94 

1380-94 

1549-93 

1550-93 

1615-94 

1616-94 

1838-93 

1921-94 

1922-94 

20-94 

21-95 

2124-94 

2125-94 

2155-93 

2161 -93 

22-95 

221-95 

222-95 

23-94 

050CT1993 

01 JUL1994 

01 JULl994 

31AUG1992 

070CT1992 

04NOV1993 

05AUG1994 

O5AUGl 994 

03NOV1992 

05JAN1994 

05JAN 1995 

OlDECl992 

02SEP1994 

02SEP1994 

10DECl993 

10DEC1993 

OSJANI 995 

03FEB1995 

03FEBI 995 

05JANl994 

070CT1994 

070CT1994 

04NOV1994 

02DEC1994 

O2DECl 994 

04FEB1994 

04FEB1994 

3OJANl992 

03MARI 995 

03MAR1995 

03MAR1994 

OSMAYI 993 

05MAR1992 

05APRl995 

OBAPRI 995 

WAY1993 

12MARl 992 

03MAY1995 

03MAY 1995 

02JUN1993 

01 APR 1992 

08APR1994 

OBAPRl994 

16JULl993 

06JUL1995 

WUL1995 

05AUG1993 

WAY1994 

OSAUG 1993 

OSMAY 1994 

02SEP1993 

O2SEPl 993 

03JUN1994 

03JUN1994 

OSOCTI 993 

050CT1993 

01 JUL1994 

01 JUL1994 

04NOV1993 

SAUG 1994 

05AUGl994 

OMAN1994 

05JAN1995 

O2SEPl 994 

02SEP1994 

10DEC1993 

10DEC1993 

osJAN1995 

03FEB1995 

03FEB1995 

OMAN1994 

1.70E+01 

1.90E+01 

2.1OE+O1 

1.40E+01 

1.40E+01 

2.10E+01 

9.00E+00 

l.OOE+Ol 

1.70E+01 

3.3OE+01 

2.20€+01 

1.40E+01 

1.90E+01 

1.90E+01 

1 .I OE+01 

l.lOE+Ol 

2.20E+01 

1.30E+01 

1.3OE+OI 

3.30E+01 

2.3OE+01 

2.2OE+Ol 

2.60€+01 

1.50€+01 

1.40E+01 

1.40E+01 

1.40E+01 

I .70E+01 

1.50E+01 

I .50E+01 

1.30E+01 

6.00€+00 

I .50E+OI 

2.20E+01 

2.20E+01 

6.WE+00 

l.lOE+OI 

7.00E+00 

7.00E+00 

O.OOE+OO 

8.00E+00 

9.00E+00 

8.00E+00 

2.79E+02 

1.74E+02 

1.74E+02 

2.76€+02 

2.03E+02 

2.76E+02 

2.03€+02 

2.54E+02 

2.21€+02 

2.82E+02 

2.82E+02 

2.68E+02 

2.68E+02 

2.51€+02 

2.50E+02 

2.78E+02 

1.55E+02 

1.54E+02 

3.39E+02 

2.88€+02 

2.38€+02 

2.38E+02 

1.94E+02 

1.94€+02 

2.89€+02 

2.18€+02 

2.18€+02 

3.39€+02 

J 

B 

B 

J 

J 

c 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

umhoslcm 

umhoslcm 

umhodcm 

umhoslcm 

umhodcm 

umhoslcm 

umhodcm 

umhodcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhodcm 

umhoslcm 

umhoslcm 

umhodcm 

umhoslcm 

umhoslcm 

umhodcm 

umhodcm 

umhoslcm 

umhoslcm 

umhodcm 

umhoslcm 

umhoslcm 

umhodcm 

umhodcm 


ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws




Specific conductance SO145 2414-94 070CT1994 WS 2.82E+02 N umhoslcm 




















Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

S t r o n t i u m 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

2415-94 

2693 - 94 

2862-94 

2863-94 

289-94 

290-94 

438-95 

439-95 

508-94 

509-94 

634-95 

635-95 

788-95 

789-95 

803-93 

902-94 

903-94 

957-95 

958-95 

1024-92 

1075-93 

1144-92 

1205-93 

1205-94 

1206-93 

1206-94 

1333-92 

1349-93 

1374-93 

1379-94 

1380-94 

1478-92 

1549-93 

1550-93 

1615-94 

1616-94 

1625-92 

1797-92 

1838-93 

1921-94 

1922-94 

I 938-92 

20-94 

21-95 

2102-92 

2124-94 

2125-94 

2155-93 

2161 -93 

22-95 

221-95 

222-95 

23-94 

2414-94 

241194 

2693-94 

2862-94 

2863-94 

289-94 

290-94 

395-92 

438-95 

439-95 

508-94 

623-93 

632-92 

634-95 

635-95 

637-93 

701-92 

788-95 

070CT1994 

04NOV1994 

02DEC1994 

O2DECl 994 

04FEB1994 

04FEB1994 

O3MAR1995 

03MARl995 

03MAR1994 

OJMAR1994 

05APR1995 

O5APRl995 

03MAY 1995 

03MAY 1995 

02JUN1993 

O8APRI994 

08APR1994 

01JUN1995 

01JUN1995 

04MAY 1992 

16JUL1993 

01JUN1992 

05AUG1993 

05MAY 1994 

05AUG1993 

05MAY1994 

06JUL1992 

02SEPl993 

02SEP1993 

03JUN1994 

03JUN1994 

03AUG1992 

050CT1993 

050CTl993 

01 JUL1994 

OlJUL1994 

31AUG1992 

070CT1992 

04NOV1993 

05AUG1994 

OSAUGl994 

03NOV1992 

WAN1 994 

WAN1995 

OlDECl992 

02SEP1994 

02SEPl994 

lODECl993 

10DEC1993 

05JAN1995 

03FEB1995 

03FEB1995 

WAN1994 

070CT1994 

07OCT1994 

04NOV1994 

02DEC1994 

02DECl994 

04FEB1994 

04FEB1994 

3OJAN1992 

03MAR1995 

03MAR1995 

03MARl994 

MAY 1993 

05MAR1992 

05APRl995 

05APR1995 

OSMAY 1993 

12MARl992 

03MAY1995 


ws 

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ws 

ws 

ws 

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ws 

ws 

ws 

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ws 

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2.82E+02 

2.92E+02 

2.37E+02 

2.36E+02 

2.22E+02 

2.22E+02 

2.22E+02 

2.22E+02 

2.09E+02 

2.10E+02 

2.63E+02 

2.63E+02 

I .58E+02 

1.57E+02 

2.69E+02 

1.60E+02 

1.60E+02 

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O.WE+OO 

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O.WE+OO 

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1 .WE+00 

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3.WE+W 

3.WE+00 

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< 

< 

< 

< 

< 

< 

< 

4 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N




Strontium 7440-24-6 789-95 03MAY1995 WS O.OOE+OO N 

mg1L 

Strontium 

7440-24-6 

803-93 02JUN1993 ws 

N 

mglL 

Strontium 

7440-24-6 

856-92 01APR1992 ws 

N 

mglL 

Strontium 

7440-24-6 

902-94 08APR1994 ws 

N 

mglL 

Strontium 

7440-24-6 

903-94 08APR1994 ws 

N 

mglL 

Sulfate 

12143-45-2 

1144-92 01JUN1992 ws 

N 

mglL 

Sulfate 

12143-45-2 

1333-92 06JUL1992 ws 

N 

mglL 

Sulfate 

12 143-45-2 

1478-92 03AUG 1992 ws 

N 

mglL 

Sulfate 

12143-45-2 

1625-92 31AUG1992 ws 

N 

mglL 

Sulfate 

12143-45-2 

395-92 3OJAN1992 ws 

N 

mglL 

TOX 

TOX 

395-92 3OJAN1992 ws 

N 

uglL 

Tantalum 

7440-25-7 

1024-92 04MAY1992 ws 

NT mglL 

Tantalum 

7440-25-7 

1144-92 OlJUN1992 ws 

N 

mglL 

Tantalum 

7440-25-7 

1333-92 06JUL1992 ws 

N 

mglL 

Tantalum 

7440-25-7 

1478-92 03AUG1992 ws 

N 

mglL 

Tantalum 

7440-25-7 

1625-92 31AUG1992 ws 

N 

mglL 

Tantalum 

7440-25-7 

1797-92 070CT1992 ws 

N 

mglL 

Tantalum 

7440-25-7 

1938-92 03NOV1992 ws 

N 

mglL 

Tantalum 

7440-25-7 

395-92 3OJANl992 ws 

N 

mglL 

Tantalum 

7440-25-7 

623-93 O5MAY 1993 

ws 

N 

mglL 

Tantalum 

7440-25-7 

632-92 DSMARl992 ws 

N 

mglL 

Tantalum 

7440-25-7 

701-92 12MAR1992 ws 

N 

mglL 

Tantalum 

7440-25-7 

856-92 01APR1992 ws 

N 

mglL 

Technetium-99 

14133-767 

395-92 30JAN 1992 ws 

N 

pCVL 

Thallium 

7440-28-0 

1024-92 04MAY 1992 ws 

C 

NT mg1L 

Thallium 

7440-28-0 

1144-92 01JUNl992 ws 

< 

N 

w/L 

Thallium 

7440-28-0 

1333-92 06JULl992 ws 

< 

N 

mgfl 

Thallium 

7440 - 28 - 0 

1478-92 03AUG1992 ws 

< 

N 

mglL 

Thallium 

7440-28-0 

1625-92 3lAUGl992 ws 

c 

N 

mgk 

Thallium 

7440-28-0 

1797-92 070CT1992 ws 

c 

N 

WlL 

Thallium 

7440-28-0 

1938-92 03NOV1992 ws 

< 

N 

mglL 

Thallium 

7440-28-0 

2102-92 01 DEC1992 ws 

< 

N 

mglL 

Thallium 

7440-28-0 

395-92 3OJAN 1992 ws 

< 

N 

mglL 

Thallium 

7440-28-0 

623-93 OSMAY 1993 ws 

< 

N 

mglL 

Thallium 

7440-28-0 

632-92 05MAR1992 ws 

< 

N 

mgfl 

Thallium 

7440-28-0 

701-92 12MAR1992 ws 

< 

N 

mglL 

Thallium 

7440-28-0 

856-92 01 APR 1992 ws 

< 

N 

mgfl 

Thorium 

7440-29-1 

1024-92 04MAY 1992 ws 

c 

NT mg1L 

Thorium 

7440-29-1 

1144-92 01JUN1992 ws 

< 

N 

mglL 

Thorium 

7440-29-1 

1333-92 06JUL1992 ws 

< 

N 

mglL 

Thorium 

7440-29-1 

1478-92 03AUG1992 ws 

< 

N 

mgfl 

Thorium 

7440-29-1 

1625-92 31AUG1992 ws 

< 

N 

mglL 

Thorium 

7440-29-1 

1797-92 070CT1992 ws 

c 

N 

mglL 

Thorium 

7440-29-1 

1938-92 O3NOVl 992 ws 

< 

N 

mglL 

Thorium 

7440-29-1 

2102-92 01DEC1992 ws 

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mg1L 

Thorium 

7440-29-1 

395-92 3OJANl992 ws 

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N 

mglL 

Thorium 

7440-29-1 

623-93 MAY 1993 ws 

C 

N 

mglL 

Thorium 

7440-29-1 

632-92 05MAR1992 ws 

< 

N 

mglL 

Thorium 

7440-29-1 

701-92 12MAR1992 ws 

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N 

mglL 

Thorium 

7440-29-1 

856-92 01 APRI 992 ws 

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N 

mglL 

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7440-31-5 

1024-92 04MAY 1992 ws 

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NT mglL 

Tin 

7440-31-5 

1144-92 01JUN1992 ws 

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Tin 

7440-31-5 

1333-92 06JUL1992 ws 

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N 

mglL 

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7440-31 -5 

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N 

mglL 

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7440-31 -5 

1625-92 3lAUG 1992 ws 

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N 

mglL 

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7440-31-5 

1797-92 070CT1992 ws 

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mglL 

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7440-31 -5 

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mglL 

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mglL 

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mg1L 

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mglL 

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7440-31-5 

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mglL 

Tiianium 

7440-32-6 

1024-92 04MAY1992 ws 

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7440-32-6 

1144-92 

01 JUN1992 ws 

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N 

mglL 

Tiianium 

7440-32-6 

1333-92 06JUL1992 ws 

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1478-92 O3AUG 1992 ws 

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mgfl 

Titanium 

7440-32-6 

1625-92 31AUG1992 ws 

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mglL 

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mglL 

Tiianium 

7440-32-6 

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N 

mglL 

litanium 

7440-32-6 

2102-92 01 DEC1992 ws 

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mg/L 

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< 

N WlL 

Page 87 of 176




Titanium 7440-32-6 623-93 05MAY1993 WS O.OOE+OO 

c 

N 

Tianium 

Titanium 

Titanium 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 


























Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Tungsten 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

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7440-32-6 

7440-32-6 

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156-60-5 

156-60-5 

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156-60-5 

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Uranium 

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Uranium 

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Uranium 

Uranium 

Uranium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

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Zinc 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61 -1 

7440-61-1 

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Zinc 

Zinc 

Zinc 

Zirconium 

Zirconium 

Zirconium 

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Zirconium 

Zirconium 

Zirconium 

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7440-67-7 

7440-67-7 

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1068-92 

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1600-92 

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1663-92 

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1921-94 

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1685-92 

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O5MAR1992 

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01 JUN1992 

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31AUG1992 

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01DEC1992 

3OJANl992 

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OJMARl992 

12MAR1992 

01APR1992 

04MAY 1992 

13MAY1992 

16JUL1993 

20MAY1992 

26MAY1992 

01JUN1992 

06JUL1995 

08JUN1992 

05AUG1993 

05MAY1994 

OSAUG1993 

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10AUG1992 

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050CT1993 

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Page 90 of 176




SO296 290-94 04FEB1994 WS 7.00€+00 su 

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Lead 

Lithium 

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Mercury 

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Barium 

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Benzene 

Benzene 

Beryllium 

Beryllium 

Beryllium 

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Cadmium 

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Cadmium 

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mgk 

mgk 

mglL 

mglL 

mglL 

uglL 

uglL 

uglL 

pCiL 

pCVL 

mglL 

mglL 

mg1L 

mglL 

mgk 

mglL 

WlL 

mgk 

mgk 

Lithium 

7439-93-2 

2104-92 OlDEC1992 WL 

N 

mglL 

Lilhium 

7439-93-2 

626-93 05MAY I 993 VK 

N 

mgk 

Magnesium 

7439-95-4 

1801-92 070CT1992 VK 

N mgk 

Page 92 of 176




Magnesium 7439-95-4 1939-92 03NOV1992 VK 2.90E+01 N 

mglL 

Magnesium 

7439-95-4 

2104-92 

OlDEC1992 


N 

mglL 

Magnesium 

7439-95-4 

626-93 05MAYl993 

3.00E+00 

N 

mglL 

Manganese 

7439 - 96 - 5 

1801 -92 070CT1992 

O.OOE+OO 

N 

mglL 

Manganese 

7439 96 - 5 

1939-92 03NOV1992 1.60E+01 

N 

mg1L 

Manganese 

7439 - 96 - 5 

2104-92 01DEC1992 O.OOE+OO 

N 

mglL 

Manganese 

Mercury 

Mercury 

Mercury 

Mercury 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Nickel 

Nickel 

Nickel 

Nickel 

Niobium 

Niobium 

Niobium 

Niobium 



PCB 

PCB 

PCB 





Potassium 

7439 - 96 - 5 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 


SO227 

1336-36-3 

1336-36-3 

1336-36-3 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7440-09-7 

626-93 

1801-92 

1939-92 

2104-92 

626-93 

1801-92 

1939-92 

2104-92 

626-93 

1801 -92 

1939-92 

2104-92 

626-93 

1801-92 

1939-92 

2104-92 

626-93 

1939-92 

1939-92 

1868-92 

1939-92 

2104-92 

1801-92 

1939-92 

2104-92 

626-93 

1801-92 

O5MAY 1993 

070CT1992 

03NOV1992 

01DEC1992 

O5MAY 1993 

070CT1992 

03NOV1992 

01DEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

01DEC1992 

O5MAY 1993 

070CT1992 

03NOV1992 

01 DEC1992 

(HMAY 1993 

03NOV1992 

03NOV1992 

190CT1992 

03NOV1992 

01DEC1992 

070CT1992 

03NOV1992 

01DEC1992 

(HMAY 1993 

07OCT1992 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+W 

O.OOE+OO 

O.OOE+OO 

l.OOE+OO 

5.00E+00 

O.OOE+W 

O.OOE+OO 

O.WE+OO 

O.OOE+OO 

2.WE+00 

O.OOE+OO 

O.WE+OO 


< 

< 

c 

C 

< 

< 

C 

C 

< 

< 

UJ 

< 

C 

c 

C 

< 

< 

C 

c 

< 

C 

< 

< 

C 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mgfl 

mglL 

w/L 

mglL 

mg1L 

mg1L 

mglL 

mglL 

uglL 

uglL 

uglL 

mglL 

mglL 

mgfl 

mglL 

mgfl 

Potassium 

7440-09-7 

1939-92 03NOV1992 1 .ZOE+OI 

N 

mgfl 

Potassium 

7440-09-7 

2104-92 01 DECl992 

2.00E+00 

N wfl 

Potassium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Silicon 

Silicon 

Silicon 

Silicon 

Silver 

Silver 

Silver 

Silver 

Sodium 

Sodium 

Sodium 

Sodium 

Strontium 

Strontium 

Strontium 

Strontium 

Sulfate 

TOX 

Tantalum 

Tantalum 

Tantalum 

Technetium-99 

Thallium 

Thallium 

Thallium 

Thallium 

Thorium 

Thorium 

Thorium 

Thorium 

Tin 

Tin 

7440-09-7 

7440-18-8 

7440-18-8 

7440-18-8 

7440-18-8 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

12143-45-2 

TOX 

7440-25-7 

7440-25-7 

7440-25-7 

14133-76-7 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-31-5 

7440-31 -5 

626-93 

i a01 -92 

1939-92 

2104-92 

626-93 

1801 -92 

1939-92 

2104-92 

626-93 

1801-92 

1939-92 

2104-92 

626-93 

1801-92 

1939-92 

2104-92 

626-93 

1801 -92 

1939-92 

2104-92 

62693 

1939-92 

1939-92 

1801-92 

1939-92 

626-93 

1939-92 

1801-92 

1939-92 

2104-92 

626-93 

1801-92 

1939-92 

2104-92 

626-93 

1801-92 

1939-92 

05MAY1993 

070CT1992 

03NOV1992 

01DEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

01DEC1992 

05MAY1993 

070CT1992 

03NOV1992 

01 DEC1992 

(HMAY 1993 

070CT1992 

03NOV1992 

01 DEC1992 

%MAY 1993 

070CT1992 

03NOV1992 

01 DECl992 

05MAY1993 

03NOV1992 

03NOV1992 

070CT1992 

03NOV1992 

05MAY1993 

03NOV1992 

070CT1992 

03NOV1992 

01DEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

01DECl992 

05MAY 1993 

070CT1992 

03NOV1992 

2.00E+00 

O.OOE+W 

O.WE+OO 

O.WE+OO 

0.00E+00 

5.00E+00 

9.00E+00 


6.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+W 

O.OOE+W 

l.lOE+Ol 

1.90E+01 

1.40E+01 

6.00€+00 

O.OOE+OO 

l.OOE+OO 

O.WE+OO 

O.OOE+OO 

5.06E+02 

2.80E+01 

O.OOE+W 

O.WE+W 

O.OOE+OO 

1.30E+01 

O.OOE+OO 

O.OOE+OO 

O.OOE+W 

O.OOE+W 

O.OOE+OO 

O.WE+OO 

O.WE+OO 

O.OOE+OO 

O.WE+OO 

5.00E+00 

J 

J 

< 

C 

C 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N' 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mg1L 

mglL 

wlL 

mgfl 

wlL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

uglL 

mglL 

mgfl 

mgfl 

pCVL 

mg/L 

mglL 

mgfl 

mgfl 

mglL 

mglL 

mglL 

w/L 

msfl 

mg/L 

Page 93 of 176

~~ 

Tin 

Tiianium 

Titanium 

Titanium 

Titanium 

Toluene 

Toluene 

Toluene 








Tungsten 

Tungsten 

Tungsten 

Tungsten 

Uranium 

Uranium 

Uranium 

Uranium 

Vanadium 

Vanadium 

Vanadium 

Xylene 

Xylene 

Xylene 

Zinc 

Zinc 

Zinc 

Zinc 

Zirconium 

Zirconium 

Zirconium 

Zirconium 


PH 

PH 

PH 

PH 

PH 

WAG 7, S\IuIIU 8. C746K-C 













Aluminum 

Aluminum 

Aluminum 

Aluminum 

Antimony 

Antimony 

Antimony 

Antimony 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Barium 

Barium 

Barium 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

7134-3 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

7440-39-3 




Tin 7440-31-5 2104-92 01DEC1992 VK 5.00E+00 c N mglL 

7440-31-5 

626-93 OSMAY1993 5.00E+00 

N 

mglL 

7440-32-6 

1801-92 070CT1992 

O.OOE+OO 

N 

mglL 

7440-32-6 

1939-92 03NOV1992 

O.OOE+OO 

N 

mg1L 

7440-32-6 

2104-92 

01DEC1992 

O.OOE+OO 

N 

mglL 

7440-32-6 

626-93 OBMAY 1993 O.OOE+OO 

N 

mglL 

108-88-3 

1450-92 27JUL1992 5 .OOE +00 

N 

uglL 

108-88-3 

1801-92 070CT1992 

5.00E+00 

N 

uglL 

108-88-3 

2104-92 01 DEC1992 

5.00E+00 

N 

uglL 

7440-44-0 

1939-92 03NOV1992 

5.00E+00 

N 

mglL 

156-60-5 

1450-92 27 JULl992 

5.00E+00 

N 

uglL 

156-60-5 

1801-92 070CT1992 

5.00E+00 

N 

uglL 

156-60-5 

2104-92 

01 DEC1992 

5.00E+00 

N 

uglL 

79-01-6 

1450-92 27JUL1992 

l.OOE+OO 

N 

uglL 

79-01-6 

1801-92 070CT1992 

l.OOE+OO 

N 

uglL 

79-01 -6 

2104-92 01 DEC1992 

l.OOE+OO 

N 

uglL 

7440-33-7 

1801-92 070CT1992 

O.OOE+OO 

N 

mglL 

7440-33-7 

1939-92 03NOV1992 

O.OOE+OO 

N 

mglL 

7440-33-7 

2104-92 01DEC1992 

O.OOE+OO 

N 

mglL 

7440-33-7 

626-93 05MAY 1993 

O.OOE+OO 

N 

mglL 

7440-61-1 

1 aoi -92 070CT1992 

O.OOE+OO 

N 

mglL 

7440-61-1 

1939-92 03NOV1992 

O.OOE+OO 

N 

mglL 

7440-61-1 

2104-92 01DEC1992 

O.OOE+OO 

N 

mglL 

7440-61 -1 

626-93 O5MAY 1993 O.OOE+OO 

N 

mg1L 

7440-62-2 

1939-92 03NOV1992 

O.OOE+OO 

N 

mg1L 

7440-62-2 

2104-92 

01 DECl992 

O.OOE+W 

N 

mgk 

7440-62-2 

626-93 05MAY1993 

O.OOE+W 

N wfl 

1330-20-7 

1450-92 27JULl992 

l.OOE+Ol 

N 

uglL 

1330-20-7 

1801-92 070CT1992 

l.OOE+Ol 

N 

ug5 

1330-20-7 

2104-92 01DEC1992 

l.OOE+Ol 

N 

uglL 

7440-66-6 

1801 -92 070CT1992 O.OOE+OO 

N 

mgfl 

7440-66-6 

1939-92 03NOV1992 O.OOE+OO 

N 

mglL 

7440-66-6 

2104-92 01DECl992 

O.OOE+OO 

N 

wlL 

7440-66-6 

626-93 OSMAYl993 0.00E+W 

N 

mglL 

7440-67-7 

1801 -92 070CT1992 O.OOE+OO 

N 

mglL 

7440-67-7 

1939-92 03NOV1992 O.OOE+OO 

N 

mglL 

744067-7 

2104-92 01 DECl992 

O.OOE+OO 

N 

wlL 

7440-67-7 

626-93 OSMAY1993 O.OOE+OO 

N 

mglL 

156-59-2 

1939-92 03NOV1992 9.00E+W 

N 

ugfl 

SO296 

1801-92 070CT1992 7.00E+W 

N su 

SO296 

1969-92 09NOV1992 6.WE+W 

N su 

so296 

2104-92 01 DECl992 

7.00E+W 

N su 

SO296 

2140-92 07DEC1992 7.00E+W 

N su 

SO296 

626-93 05MAY1993 6.00€+00 

N su 

1298-92 

1449-92 

1802-92 

1940-92 

2105-92 

4928-92 

1298-92 

1449-92 

1802-92 

1940-92 

2105-92 

4928-92 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

26JUN1992 

27JULl992 

070CT1992 

03NOV1992 

01DECl992 

08MAY1992 

26JUN1992 

27JULl992 

070CT1992 

03NOV1992 

OlDEC1992 

08MAYl992 

070CT1992 

03NOV1992 

OlDECl992 

05MAY1993 

070CT1992 

03NOV1992 

01DECl992 

05MAY1993 

070CT1992 

03NOV1992 

01DECl992 

05MAY1993 

070CT1992 

03NOV1992 

01 DECl992 


l.OOE+Ol 

5.00E+00 

5.00E+00 

5.00E+W 

5.00E+00 

9.00E+W 

5.00E+W 

5.00E+00 

5.WE+00 

5.00E+W 

5.00€+00 

9.00E+00 

O.OOE+OO 

6.00E+W 

1 .WE+00 

1 .WE+00 

O.WE+W 

O.WE+OO 

O.WE+OO 

O.OOE+OO 

O.OOE+W 

0.00E+W 

O.M)E+OO 

O.WE+OO 

O.WE+W 

O.WE+W 

O.WE+OO 

< 

< 

< 

< 

J 

c 

c 

< 

< 

< 

< 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

ugfl 

uglL 

ug5 

ugfl 

uglL 

ug5 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

mgk 

wlL 

wR 

mgfl 

mglL 

mglL 

wR 

wlL 

w5 

wfl



ANALYE CAS NUMBER SAMPLE ID DATE lYPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Barium 7440-39-3 627-93 05MAY1993 WL O.OOE+OO 

N 

mglL 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Calcium 

Calcium 

Calcium 

Calcium 

Chromium 

Chromium 

Chromium 

Chromium 

Cobalt 

Cobalt 

Coban 

Cobalt 

Copper 

Copper 

Copper 

71-43-2 

71 -43-2 

71-43-2 

71-43-2 

71-43-2 

7440-41-7 

7440-41 -7 

7440-41-7 

7440-41-7 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

7440-70-2 

1298-92 

1449-92 

1802-92 

1940-92 

2105-92 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

21-92 

< 

c 

< 

< 

< 

< 

c 

c 

< 

< 

c 

c 

< 

< 

c 

< 

c 

CoPPr 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Iron 

Iron 

Iron 

Iron 

Lead 

Lead 

Lead 

Lead 

Lithium 

Lithium 

Lithium 

Lithium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Manganese 

Manganese 

Manganese 

Manganese 

Mercury 

Mercury 

Mercury 

Mercury 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Nickel 

Nickel 

Nickel 

Nickel 

Niobium 

7440-70-2 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-48-4 

7440-48-4 

7440-48-4 

7440-484 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

100-41-4 

100-414 

100-41-4 

100-41-4 

100-41-4 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-03-1 

627-93 

1298-92 

1449-92 

1802-92 

1940-92 

2105-92 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

26JUN1992 

27JUL1992 

070CT1992 

03NOV1992 

OlDEC1992 

070CT1992 

03NOV1992 

01 DEC1992 

O5MAY 1993 

070CT1992 

03NOV1992 

01 DECl992 

O5MAY 1993 

070CT1992 

03NOV1992 

OlDEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

01 DEC1992 

05MAY1993 

070CT1992 

03NOV1992 

01 DECI 992 

OSMAY 1993 

070CT1992 

03NOV1992 

OlDECl992 

05MAY 1993 

070CT1992 

03NOV1992 

01 DEC1992 

O5MAY1993 

26JUN1992 

27JULl992 

070CT1992 

03NOV1992 

01DEC1992 

070CT1992 

03NOV1992 

OlDEC1992 

05MAY1993 

070CT1992 

03NOVl992 

01 DECl992 

OSMAY 1993 

070CT1992 

03NOV1992 

01 DECl992 

05MAY 1993 

070CT1992 

03NOVl992 

01DECl992 

(HMAY 1993 

070CT1992 

03NOV1992 

01 DECI 992 

OSMAY 1993 

070CT1992 

OJNOVI 992 

01DEC1992 

05MAY1993 

070CT1992 

03NOV1992 

01DEC1992 

05MAY1993 

070CT1992 

03NOV1992 

01 DECl992 

WAY 1993 

070CT1992 


WL 

WL 

WL 

WL 

VK 

VK 

WL 

VK 

WL 

WL 

WL 

WL 

VK 

WL 

VK 

WL 

VK 

VK 

WL 

VK 

WL 

VK 

WL 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

WL 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

WL 

VK 

WL 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

5.00E+00 

5.OOE+OO 

5.00E+00 

5.00E+00 

5.WE+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

1.90E+01 

5.30E+01 

9.90E+01 

1.20E+01 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+W 

O.OOE+OO 

O.WE+OO 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+W 

O.WE+W 

5.WE+00 

5.WE+00 

5.00E+00 

5.00E+00 

5.00E+00 



1.34E+02 

I.WE+OO 

O.WE+W 

O.OOE+W 

O.WE+W 

O.WE+OO 

O.WE+W 

O.WE+OO 

O.WE+OO 

O.WE+OO 


1.30E+01 

3.20E+01 

3.WE+W 

I .WE+W 

6.00E+00 

1.50E+01 

O.WE+OO 

O.WE+OO 

O.OOE+OO 

O.WE+W 

O.OOE+OO 

O.WE+OO 

O.WE+W 

O.WE+W 

O.WE+OO 

O.WE+W 

O.WE+W 

O.OOE+W 

O.WE+W 

0.00E+00 

c 

c 

UJ 

c 

c 

< 

< 

< 

c 

< 

c 

UJ 

c 

c 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N




Niobium 

7440-03-1 1940-92 03NOV1992 WL O.OOE+OO c N mglL 

Niobium 

Niobium 

PCB 

PCB 

PCB 




7440-03-1 

7440-03-1 

1336-36-3 

1336-36-3 

1336-36-3 

7723-14-0 

7723-14-0 

7723-14-0 

2105-92 

627-93 

ia69-92 

1940-92 

2105-92 

1802-92 

1940-92 

2105-92 

01DEC1992 

O5MAY 1993 

190CT1992 

03NOV1992 

01 DEC1992 

070CT1992 

03NOV1992 

01DEC1992 

c 

c 

c 

c 

c 

c 

N 

N 

N 

N 

N 

N 

N 

N 


Potassium 

Potassium 

7723-14-0 

7440-09-7 

7440-09-7 

627-93 

1802-92 

1940-92 

05MAY 1993 

070CT1992 

O3NOVl 992 

< N 

N 

N 

Potassium 

7440-09-7 

2105-92 01 DEC1992 

J 

N 

Potassium 

7440-09-7 

627-93 O5MAY 1993 

c 

N 

Ruthenium 

7440-ia-a 

1802-92 070CT1992 

c 

N 

Ruthenium 

7440-18-8 

1940-92 03NOV1992 

c 

N 

Ruthenium 

7440-1 a-a 

2105-92 

01 DEC1992 

c 

N 

Ruthenium 

7440-1 a-a 

627-93 O5MAYl 993 

< 

N 

Silicon 

Silicon 

7440-21-3 

7440-21-3 

1802-92 

1940-92 

070CT1992 

03NOV1992 

< 

N 

N 

Silicon 

Silicon 

Silver 

Silver 

7440-21-3 

7440-21-3 

7440-22-4 

7440-22-4 

2105-92 

627-93 

1802-92 

1940-92 

01 DECI 992 

O5MAY 1993 

070CT1992 

03NOV1992 

J 

c 

c 

N 

N 

N 

N 

Silver 

Silver 

Sodium 

Sodium 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

2105-92 

627-93 

1802-92 

1940-92 

01DEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

< 

< 

N 

N 

N 

N 

Sodium 

Sodium 

Strontium 

Strontium 

Strontium 

Strontium 

Tantalum 

Tantalum 

Tantalum 

Thallium 

Thallium 

Thallium 

Thallium 

Thorium 

Thorium 

Thorium 

Thorium 

Tin 

Tin 

Tin 

Tin 

Titanium 

Titanium 

Tiianium 

Titanium 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 












Tungsten 

Tungsten 

Tungsten 

7440-23-5 

7440-23-5 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-25-7 

7440-25-7 

7440-25-7 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-31 -5 

7440-31 -5 

7440-31-5 

7440-31 -5 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

108-883 

ioa-aa-3 

ioa-aa-3 

108-88-3 

ioa-aa-3 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

7440-33-7 

7440-33-7 

7440-33-7 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1298-92 

1449-92 

1802-92 

1940-92 

2105-92 

1298-92 

1449-92 

1802-92 

1940-92 

2105-92 

1298-92 

1449-92 

1802-92 

1940-92 

2105-92 

4928-92 

1802-92 

1940-92 

2105-92 

01 DECl992 

(HMAY I 993 

070CT1992 

03NOVl992 

01 DECI 992 

05MAY1993 

070CT1992 

03NOV1992 

(HMAY 1993 

070CT1992 

03NOV1992 

01 DECl992 

05MAY 1993 

070CT1992 

03NOV1992 

01DECl992 

(HMAY 1993 

070CT1992 

03NOV1992 

01 DECl992 

WAY 1993 

070CT1992 

03NOVl 992 

01DEC1992 

(HMAY 1993 

26JUN1992 

27JULl992 

070CT1992 

03NOV1992 

OlDECl992 

26JUN1992 

27JULl992 

070CT1992 

03NOV1992 

01DECl992 

26JUN1992 

27JULl992 

070CT1992 

03NOV1992 

01DECl992 

08MAY 1992 

O7OCTI 992 

03NOV1992 

OlDECl992 

J 

< 

c 

< 

c 

< 

< 

< 

c 

< 

< 

< 

c 

< 

c 

< 

< 

c 

c 

< 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Page 96 of 176




Tungsten 7440-33-7 627-93 05MAY1993 WL O.OOE+OO < N mg1L 

Uranium 

Uranium 

Uranium 

Uranium 

Vanadium 

Vanadium 

Vanadium 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Zinc 

Zinc 

Zinc 

Zinc 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

PH 

PH 

PH 

PH 

PH 

WAG 7, SWU 8, C746K-D 





1 .I-Dchloroethene 



I ,l-Dichloroethene 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Antimony 

Antimony 

Antimony 

Antimony 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Barium 

Barium 

Barium 

Barium 

Benzene 

Benzene 

Benzene 

Benzene 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Calcium 

Calcium 

Calcium 

Calcium 

Chromium 

7440-61-1 

7440-61-1 

7440-61 -1 

7440-61-1 

7440-62-2 

7440-62-2 

7440-62-2 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

SO296 

SO296 

SO296 

SO296 

SO296 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

75-354 

75-35-4 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-39-3 

7440- 39 - 3 

7440-39-3 

7440-39-3 

71-43-2 

71-43-2 

71-43-2 

71-43-2 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-47-3 

1802-92 

1940-92 

2105-92 

627-93 

1940-92 

2105-92 

627-93 

1298-92 

1449-92 

1802-92 

1940-92 

2105-92 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1940-92 

2105-92 

627-93 

1802-92 

1970-92 

2105-92 

2141-92 

627-93 

1448-92 

1803-92 

1941 -92 

2106-92 

I 448-92 

1803-92 

1941-92 

2106-92 

1803-92 

1941-92 

2106-92 

628-93 

1803-92 

1941 -92 

2106-92 

628-93 

1803-92 

1941-92 

2106-92 

628-93 

1803-92 

1941 -92 

2106-92 

628-93 

144892 

1803-92 

1941 -92 

2106-92 

1803-92 

1941 -92 

2106-92 

628-93 

1803-92 

1941-92 

2106-92 

628-93 

1803-92 

1941 -92 

2106-92 

628-93 

1803-92 

1941-92 

2106-92 

628-93 

1803-92 

070CT1992 

03NOV1992 

01DEC1992 

O5MAY 1993 

03NOV1992 

01DEC1992 

O5MAYl 993 

26JUN1992 

27JUL1992 

070CT1992 

03NOV1992 

01 DEC1992 

070CT1992 

03NOV1992 

01 DEC1992 

05MAY1993 

070CT1992 

03NOV1992 

01DECl992 

[HMAYI 993 

070CT1992 

O9NOVI 992 

OlDEC1992 

07DECl992 

05MAY1993 

27JUL1992 

070CT1992 

03NOV1992 

OlDEC1992 

27JUL1992 

070CT1992 

03NOV1992 

01DEC1992 

070CT1992 

03NOV1992 

01DECl992 

05MAY 1993 

070CTI 992 

03NOV1992 

01 DEC1992 

05MAY I 993 

070CT1992 

03NOV1992 

01 DECI 992 

05MAY 1993 

070CT1992 

03NOV1992 

01 DEC1992 

05MAY1993 

27JUL1992 

070CT1992 

03NOV1992 

01 DEC1992 

070CT1992 

03NOV1992 

01 DECl992 

05MAY 1993 

070CT1992 

03NOV1992 

01 DEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

OlDECl992 

05MAY 1993 

070CT1992 

03NOV1992 

01 DECI 992 

05MAY 1993 

070CT1992 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

l.OOE+Ol 

l.OOE+Ol 

1.00E+01 

l.OOE+OI 

l.OOE+OI 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

l.OOE+OO 

0.00E+00 

O.OOE+OO 

7.00E+00 

6.00E+00 

7.00E+00 

7.00E+00 

6.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.WE+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.WE+W 

O.WE+W 

O.WE+OO 

1 .WE+00 

I .00E+00 

O.WE+OO 

O.WE+W 

O.WE+OO 

O.WE+OO 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

5.00E+00 

5.00E+00 

5.00E+00 

5.WE+00 

O.WE+OO 

O.WE+W 

O.WE+OO 

O.WE+W 

O.WE+OO 

O.WE+OO 

O.OOE+OO 

O.WE+W 

O.WE+OO 

O.WE+W 

O.OOE+W 

O.OOE+OO 

2.00E+01 

2.60E+01 

I .80E+01 

1.30E+01 

O.WE+OO 

< 

N 

I 

N 

< 

N 

< 

N 

N 

N 

< N 

< 

N 

c 

N 

c 

N 

< 

N 

< 

N 

N 

N 

N 

< 

N 

< 

N 

N 

< 

N 

Q 

N 

N 

N 

N 

N 

N 

< 

c 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

c 

c 

c 

c 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Page 97 of 176

Chromium 

Chromium 

Coban 

Coban 

Coban 

Coban 

Copper 

Copper 

Copper 

Copper 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Iron 

Iron 

Iron 

Iron 

Lead 

Lead 

Lead 

Lead 

Lithium 

Lithium 

Lithium 

Lithium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Manganese 

Manganese 

Manganese 

Manganese 

Mercury 

Mercury 

Mercury 

Mercury 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Nickel 

Nickel 

Nickel 

Nickel 

Niobium 

Niobium 

Niobium 

Niobium 

PCB 

PCB 

PCB 





Potassium 

Potassium 

Potassium 

Potassium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Silicon 

Silicon 

Silicon 

Silicon 

Silver 

Silver 




Chromium 7440-47-3 1941 -92 03NOV1992 WL O.OOE+OO < N mglL 

7440-47-3 

2106-92 

744047-3 

628-93 

7440-484 

1803-92 

7440-48-4 

1941 -92 

744048-4 

7440-48-4 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

100-41 -4 

100-414 

100-41 -4 

100414 

7439 - 89 - 6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-95-4 

7439-954 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

1336-36-3 

1336-36-3 

1336-36-3 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-18-8 

7440-18-8 

7440-18-8 

7440-18-8 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-224 

7440-224 

2106-92 

628-93 

1803-92 

1941-92 

2106-92 

628-93 

1448-92 

1803-92 

1941 -92 

2106-92 

1803-92 

1941-92 

2106-92 

628-93 

1803-92 

1941-92 

2106-92 

628-93 

1803-92 

1941-92 

2106-92 

628-93 

1803-92 

1941-92 

2106-92 

628-93 

1803-92 

1941-92 

2106-92 

628-93 

1803-92 

1941-92 

2106-92 

628-93 

1803-92 

1941 -92 

2106-92 

628-93 

1803-92 

1941-92 

2106-92 

628-93 

1803-92 

1941 -92 

2106-92 

628-93 

1870-92 

1941-92 

2106-92 

1803-92 

1941-92 

2106-92 

628-93 

1803-92 

1941-92 

2106-92 

628-93 

1803-92 

1941-92 

2106-92 

628-93 

1803-92 

1941-92 

2106-92 

628-93 

180192 

1941-92 

01DEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

01DEC1992 

05MAY1993 

070CT1992 

03NOV1992 

01DEC1992 

05MAY 1993 

27JUL1992 

070CT1992 

03NOV1992 

01DECl992 

070CT1992 

03NOV1992 

01DECl992 

osMAY1993 

070CT1992 

03NOV1992 

01DEC1992 

05MAY1993 

070CT1992 

03NOV1992 

OlDECl992 

OSMAYl993 

070CT1992 

03NOV1992 

01DEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

01 DECl992 

WAY1993 

070CT1992 

03NOV1992 

OlDECl992 

05MAY 1993 

070CT1992 

03NOV1992 

OlDECl992 

WAY 1993 

070CT1992 

03NOV1992 

OlDEC1992 

WAY1993 

070CT1992 

03NOV1992 

OlDECl992 

05MAY1993 

190CT1992 

03NOV1992 

OlDEC1992 

07OCT1992 

03NOV1992 

01 DEC1992 

05MAY1993 

070CT1992 

03NOV1992 

01 DECl992 

osMAY1993 

070CT1992 

03NOV1992 

01 DECl992 

05MAY 1993 

070CT1992 

03NOV1992 

01DECl992 

05MAY1993 

070CT1992 

03NOV1992 


WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

\M. 

WL 

WL 

WL 

WL 

\M. 

WL 

WL 

\M. 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

VK 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

WL 

WL 

WL 

WL 

VK 

WL 

VK 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< N 

< 

c 

< 

< 

< 

< 

< 

< 

< 

< 

< 

UJ 

c 

c 

c 

< 

< 

< 

< 

< 

< 

< 

< 

J 

< 

c 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

ugn 

uglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mg/L 

mglL 

mgfl 

WlL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mgfl 

mglL 

mglL 

mglL 

WlL 

mglL 

wfl 

Wfl 

mglL 

WlL 

uglL 

Wfl 

uglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

Wfl 

mgfl 

WlL 

Wfl 

mgfl 

W/L 

mgfl 

WlL 

mgfl 

mg/L 

WlL 

Wfl 

mgn



DATE TYPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

ANALYTE CAS NUMBER SAMPLE ID 

Silver 7440-22-4 2106-92 01DEC1992 VK O.OOE+OO 

Silver 

Sodium 

Sodium 

Sodium 

Sodium 

Strontium 

Strontium 

Strontium 

Strontium 

Tantalum 

Tantalum 

Tantalum 

Thallium 

Thallium 

Thallium 

Thallium 

Thorium 

Thorium 

Thorium 

Thorium 

Tin 

Tin 

Tin 

Tin 

Tianium 

Tianium 

Tianium 

Tilanium 

Toluene 

Toluene 

Toluene 

Toluene 









Tungsten 

Tungsten 

Tungsten 

Tungsten 

Uranium 

Uranium 

Uranium 

Uranium 

Vanadium 

Vanadium 

Vanadium 

Xylene 

Xylene 

Xylene 

Xylene 

Zinc 

Zinc 

Zinc 

Zinc 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

PH 

PH 

PH 

PH 

PH 

WAG 7, SVWU 8, C746K-E 



7440-22-4 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-25-7 

7440-25-7 

7440-25-7 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-29-1 

7440-29-1 

7440-29-1 

7440-31-5 

7440-31 -5 

7440-31-5 

7440-32-6 

7440-29-1 

7440-31-5 

7440-32-6 

7440-32-6 

7440-32-6 

108-88-3 

108-88-3 

108-88-3 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

79-01 -6 

79-01-6 

79-01-6 

79-01-6 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61 -1 

7440-62-2 

7440-62-2 

7440-62-2 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

7440-66-6 

7440-67-7 

7440-67-7 

I 

0888-3 

7440-66-6 

7440-67-7 

7440-67-7 

so296 

so296 

SO296 

SO296 

SO296 

75-34-3 

75-34-3 

628-93 

1803-92 

2106-92 

628-93 

1803-92 

1941-92 

2106-92 

628-93 

1803-92 

1941-92 

628-93 

1803-92 

1941-92 

628-93 

1803-92 

1941 

-92 

2106-92 

628-93 

1941 

-92 

628-93 

1803-92 

1941 

-92 

2 106-92 

1803-92 

2106-92 

1941-92 

2106-92 

1448-92 

1803-92 

1941-92 

2106-92 

1803-92 

1941-92 

1448-92 

1803-92 

2106-92 

1803-92 

628-93 

I 

448-92 

2106-92 

1941 

-92 

1941-92 

2106-92 

628-93 

1803-92 

1941-92 

2106-92 

1941 

-92 

2106-92 

628-93 

1803-92 

1941 

-92 

2106-92 

1803-92 

1941-92 

2106-92 

1803-92 

1941-92 

628-93 

I 

448-92 

628-93 

2106-92 

628-93 

1803-92 

1971-92 

2106-92 

2142-92 

628-93 

1804-92 

1942-92 

05MAY1993 

070CTI 992 

03NOV1992 

01 DEC1992 

O5MAY 1993 

070CT1992 

03NOV1992 

01DEC1992 

O5MAY 1993 

070CT1992 

03NOV1992 

O5MAY 1993 

070CT1992 

03NOV1992 

01 DEC1992 

(HMAY 1993 

070CT1992 

03NOV1992 

01 DEC1992 

05MAYI 993 

070CT1992 

03NOVl 992 

01 DECl992 

OSMAY 1993 

070CT1992 

03NOV1992 

01DECl992 

OSMAY 1993 

27JULl992 

070CT1992 

03NOV1992 

01 DECl992 

27JUL1992 

070CT1992 

03NOV1992 

01 DEC1992 

27JUL1992 

070CT1992 

03NOV1992 

01DEC1992 

070CT1992 

03NOV1992 

01DECl992 

05MAY 1993 

070CT1992 

03NOVl992 

01 DECl992 

05MAY 1993 

03NOV1992 

01 DEC1992 

05MAY 1993 

27JULl992 

070CT1992 

03NOV1992 

01 DEC1992 

070CT1992 

03NOV1992 

01DEC1992 

05MAY1993 

070CT1992 

03NOV1992 

OlDECl992 

05MAY 1993 

070CT1992 

09NOVl992 

01 DEC1992 

07DEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

WL 

VK 

VK 

WL 

WL 

VK 

VK 

WL 

VK 

WL 

VK 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

WL 

0.00E+00 

l.IOE+OI 

1.80E+01 

1.40E+01 

6.00E+00 

0.00E+00 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OM+OO 

O.OOE+OO 

O.OOE+W 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

5.00E+00 

5.WE+00 

5.00E+00 

O.WE+OO 

O.WE+OO 

O.OOE+OO 

0.00E+00 

5.WE+00 

5.00€+00 

5.00E+W 

5.00E+00 

1.80E+01 

5.00€+00 

5.00€+00 

5.00E+00 

l.OOE+OO 

1.00E+00 

I 

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I 

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0.00E+00 

O.WE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+W 

O.WE+W 

O.WE+OO 

O.WE+W 

O.WE+OO 

0.00E+00 

O.OOE+OO 

l.OOE+OI 

l.OOE+OI 

l.OOE+OI 

l.WE+OI 

0.00E+W 

O.WE+OO 

O.WE+W 

O.OOE+OO 

O.OOE+W 

O.OOE+OO 

0.00E+00 

O.WE+OO 

7.WE+00 

6.00E+00 

7.00E+00 

7.00€+00 

6.00€+00 

5.00E+00 

5.WE+W 

c 

c 

J 

c 

c 

c 

c 

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c 

c 

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N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

wlL 

ugfl 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ug1L 

uglL 

ugfl 

wfl 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mga 

mglL 

mglL 

uglL 

ugfl 

uglL 

ugfl 

mglL 

mgk 

wlL 

wlL 

mglL 

mglL 

wlL 

mglL 

su 

su 

su 

su 

su 

ugfl 

uglL 

Page 99 of 176




1 .l-Dichloroethane 75-34-3 2107-92 01DEC1992 WL 5.00E+00 C N 




Aluminurn 

Aluminum 

Aluminum 

Aluminum 

Antimony 

Antimony 

Antimony 

Antimony 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Barium 

Barium 

Barium 

Barium 

Benzene 

Benzene 

Benzene 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Calcium 

Calcium 

Calcium 

Calcium 

Chromium 

Chromium 

Chromium 

Chromium 

Coban 

Cobalt 

Cobalt 

Cobalt 

Copper 

Copper 

Copper 

Copper 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Iron 

Iron 

Iron 

Iron 

Lead 

Lead 

Lead 

Lead 

Lithium 

Lithiurn 

Lithium 

Lithium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Manganese 

Manganese 

75-35-4 

75-35-4 

75-35-4 

7429-90-5 

7429-90-5 

7429-90-5 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-38-2 

7440-39-3 

7 44 0 - 3 9 - 3 

7429-90-5 

7440-38-2 

7440-39-3 

7440-39-3 

71-43-2 

7 1-43-2 

71-43-2 

7440-41-7 

7440-41-7 

7440-41 -7 

7440-41-7 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-47-3 

7440-47-3 

744047-3 

7440-47-3 

7440-48-4 

7440484 

7440-48-4 

7440-48-4 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

100-41-4 

100-41-4 

100-41-4 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

1804-92 

1942-92 

2 107-92 

1804-92 

1942-92 

2 107-92 

629-93 

1804-92 

1942-92 

2 107-92 

629-93 

1804-92 

1942-92 

629-93 

1804-92 

1942-92 

2107-92 

629-93 

1804-92 

1942-92 

1804-92 

1942-92 

2107-92 

1804-92 

2107-92 

629-93 

1804-92 

2107-92 

629-93 

1804-92 

1942-92 

629-93 

1804-92 

1942-92 

629-93 

1804-92 

1942-92 

629-93 

1804-92 

2 107-92 

629-93 

1804-92 

2107-92 

1804-92 

1942-92 

629-93 

1804-92 

2107-92 

2107-92 

629-93 

1942-92 

1942-92 

2107-92 

2107-92 

2107-92 

1942-92 

1942-92 

2107-92 

1942-92 

2107-92 

629-93 

1804-92 

1942-92 

2107-92 

629-93 

1804-92 

1942-92 

2107-92 

629-93 

1804-92 

1942-92 

070CT1992 

03NOV1992 

OlDEC1992 

070CT1992 

03NOV1992 

01DEC1992 

O5MAY 1993 

070CT1992 

03NOV1992 

01 DEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

01DEC1992 

05MAY1993 

070CT1992 

03NOV1992 

01DECl992 

05MAY1993 

070CT1992 

03NOV1992 

01 DECl992 

070CT1992 

03NOV1992 

01 DECl992 

05MAY 1993 

070CT1992 

03NOV1992 

01DEC1992 

MAY 

1993 

070CT1992 

03NOV1992 

01 DEC1992 

05MAY1993 

070CT1992 

03NOV1992 

01 DEC1992 

05MAYl993 

070CT1992 

03NOV1992 

OlDECl992 

MAY1993 

070CT1992 

03NOV1992 

01 DEC1992 

05MAY1993 

070CT1992 

03NOVl992 

01 DECl992 

05MAY 1993 

070CT1992 

03NOV1992 

OlDEC1992 

070CT1992 

03NOV1992 

OlDECl992 

05MAY1993 

070CT1992 

03NOV1992 

01 DECl992 

MAY 

1993 

070CT1992 

03NOV1992 

01DEC1992 

05MAY1993 

070CT1992 

03NOV1992 

01DEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

WL 

WL 

VM 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

VM 

WL 

WL 

WL 

WL 

WL 

VM 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

VK 

VK 

WL 

WL 

WL 

\IK 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

5.00E+00 

5.00E+00 

5.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

l.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

5.00E+00 

5.00E+00 

5.00E+W 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+W 

O.OOE+OO 

O.OOE+OO 

O.OOE+W 

O.WE+OO 

O.OOE+W 

O.OOE+W 

O.OOE+OO 

O.OOE+W 

1.70E+01 

2.00E+01 

1.80E+Ol 

1.60E+01 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.WE+OO 

O.OOE+W 

O.WE+W 

O.WE+OO 

O.WE+OO 

O.WE+W 

O.WE+OO 

O.OOE+W 

5.WE+00 

5.00E+00 

S.WE+OO 

O.WE+OO 

2.WE+00 

2.WE+W 


O.WE+W 

O.WE+W 

O.OOE+OO 

O.WE+OO 

O.WE+W 

O.WE+W 

O.WE+W 

O.WE+W 


5.WE+W 

5.WE+W 


O.WE+W 

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C 

N 

C 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

uglL 

uglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

uglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mgfl 

mglL 

mg1L 

mg/L 

mgfl 

mgn 

mglL 

mglL 

mglL 

mg1L 

mg1L 

mglL 

mglL 

mglL 

mglL 

mgfl 

mgfl 

mgfl 

uglL 

ugfl 

uglL 

mglL 

mg/L 

mglL 

mgfl 

mg1L 

mg/L 

mglL 

mgfl 

mglL 

mgfl 

mgfl 

mglL 

mgfl 

mgfl 

mglL 

mglL 

mgfl 

mglL 

Page 100 of 176




Manganese 7439 - 96 - 5 2107-92 01DEC1992 VK O.OOE+OO N 

mglL 

Manganese 

Mercury 

7439-96-5 

7439-97-6 

629-93 

1804-92 

O5MAY 1993 

070CT1992 

< 

N 

N 

mglL 

mglL 

Mercury 

Mercury 

Mercury 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Nickel 

Nickel 

Nickel 

Nickel 

Niobium 

Niobium 

Niobium 

Niobium 

PCB 

PCB 

PCB 

7439-97-6 

7439-97-6 

7439-97-6 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

1336-36-3 

1336-36-3 

1336-36-3 

1942-92 

2107-92 

629-93 

1804-92 

1942-92 

2107-92 

629-93 

1804-92 

1942-92 

2107-92 

629-93 

1804-92 

1942-92 

2107-92 

629-93 

1871 -92 

1942-92 

2107-92 

03NOV1992 

01 DEC1992 

O5MAY 1993 

070CT1992 

03NOV1992 

01DEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

01DECl992 

O5MAY 1993 

070CT1992 

03NOV1992 

01DEC1992 

O5MAY 1993 

190CT1992 

03NOV1992 

01 DECl992 

< 

< 

C 

< 

C 

< 

< 

< 

< 

UJ 

C 

< 

c 

C 

C 

< 

C 

C 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mg1L 

uglL 

uglL 

uglL 


7723-14-0 

1804-92 070CT1992 

C 

N 

mglL 


7723-14-0 

1942-92 03NOV1992 

< 

N wfl 



Potassium 

Potassium 

Potassium 

7723-14-0 

7723-14-0 

7440-09-7 

7440-09-7 

7440-09-7 

2107-92 

629-93 

1804-92 

1942-92 

2107-92 

01 DEC1992 

OWAYI 993 

070CTI 992 

03NOVl992 

01 DECl992 

C 

J 

N 

N 

N 

N 

N 

mglL 

mglL 

w/L 

WlL 

mglL 

Potassium 

7440-09-7 

629-93 05MAY 1993 

N 

mglL 

Ruthenium 

7440-188 

1804-92 070CT1992 

C 

N wfl 

Ruthenium 

Ruthenium 

Ruthenium 

Silicon 

Silicon 

Silicon 

Silicon 

Silver 

7440-18-8 

7440-18-8 

7440-18-8 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-22-4 

1942-92 

2107-92 

629-93 

I80492 

1942-92 

2107-92 

629-93 

1804-92 

03NOV1992 

01 DEC1992 

05MAYI993 

070CT1992 

03NOV1992 

01DEC1992 

05MAY 1993 

070CT1992 

< 

< 

< 

< 

J 

c 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mgfl 

mgfl 

mglL 

mgfl 

mglL 

mglL 

Silver 

7440-22-4 

1942-92 03NOV1992 

< 

N 

mgfl 

Silver 

7440-22-4 

2107-92 01DEC1992 

< 

N 

mglL 

Silver 

7440-22-4 

629-93 O5MAY 1993 

C 

N wfl 

Sodium 

Sodium 

Sodium 

Sodium 

Strontium 

Strontium 

Strontium 

Strontium 

Tantalum 

Tantalum 

Tantalum 

Thallium 

Thallium 

Thallium 

Thallium 

Thorium 

Thorium 

Thorium 

Thorium 

Tin 

Tin 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-25-7 

7440-25-7 

7440-25-7 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-31-5 

7440-31-5 

1804-92 

1942-92 

2107-92 

629-93 

18M-92 

1942-92 

2107-92 

629-93 

1804-92 

1942-92 

629-93 

1804-92 

1942-92 

2107-92 

629-93 

1804-92 

1942-92 

2107-92 

629-93 

1804-92 

1942-92 

070CT1992 

03NOV1992 

OlDECl992 

05MAY 1993 

070CT1992 

03NOVI 992 

01DECl992 

05MAY1993 

070CT1992 

03NOV1992 

05MAY 1993 

070CT1992 

03NOV1992 

01 DEC1992 

O5MAY 1993 

070CT1992 

03NOV1992 

01 DECl992 

05MAY 1993 

070CT1992 

03NOV1992 

J 

c 

C 

C 

< 

c 

C 

< 

< 

C 

< 

C 

< 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mgfl 

WlL 

mglL 

mg1L 

WllL 

wlL 

mglL 

mglL 

mgfl 

mglL 

wlL 

mg/L 

wlL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

WlL 

mglL 

Tin 

7440-31-5 

2107-92 01 DECl992 

C 

N 

mgfl 

Tin 

7440-31-5 

629-93 05MAY 1993 

< 

N wfl 

Titanium 

Titanium 

Tiianium 

Titanium 

Toluene 

Toluene 

Toluene 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

108-88-3 

108-88-3 

108-88-3 

1804-92 

1942-92 

2107-92 

629-93 

1804-92 

1942-92 

2107-92 

070CT1992 

03NOV1992 

01 DEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

01DEC1992 

< 

c 

C 

< 

C 

C 

< 

N 

N 

N 

N 

N 

N 

N 

mgfl 

wlL 

wlL 

mgfl 

uglL 

uglL 

u9fl 


1804-92 070CT1992 

< 

N 

uglL 

Page 101 of 176




Trans-I .2-Dichloroethene 156-60-5 1942-92 03NOV1992 WL 5.00E+00 C N uglL 





Tungsten 

Tungsten 

Tungsten 

Tungsten 

Uranium 

Uranium 

Uranium 

Uranium 

Vanadium 

Vanadium 

Vanadium 

Xylene 

Xylene 

Xylene 

Zinc 

Zinc 

Zinc 

Zinc 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

PH 

PH 

PH 

PH 

PH 

WAG 7. SWU 8, C746K-F 


1 .l-Dffihloroethane 

1 .I-Dichloroeihane 


1 .I-Dichloroeihene 


1 ,l-Dihloroethene 

1 ,I -Dichloroethene 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Antimony 

Antimony 

Antimony 

Antimony 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Barium 

Barium 

Barium 

Barium 

Benzene 

Benzene 

Benzene 

Benzene 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Cadmium 

Cadmium 

Cadmium 

156-60-5 

79-01-6 

79-01-6 

79-01-6 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-62-2 

7440-62-2 

7440-62-2 

1330-20-7 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

SO296 

SO296 

SO296 

SO296 

SO296 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

71-43-2 

71-43-2 

71-43-2 

71-43-2 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-43-9 

7440-43-9 

7440-43-9 

2107-92 

1804-92 

1942-92 

2107-92 

1804-92 

1942-92 

2107-92 

629-93 

1804-92 

1942-92 

2107-92 

629-93 

1942-92 

2107-92 

629-93 

1804-92 

1942-92 

2107-92 

1804-92 

1942-92 

2107-92 

629-93 

180492 

1942-92 

2107-92 

629-93 

1804-92 

1972-92 

2107-92 

2143-92 

629-93 

1451-92 

1800-92 

1943-92 

2108-92 

1451-92 

1800-92 

1943-92 

2108-92 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1451-92 

1800-92 

1943-92 

2108-92 

1800-92 

1943-92 

2108-92 

62593 

1800-92 

1943-92 

210592 

625-93 

1800-92 

1943-92 

210592 

01DEC1992 

070CT1992 

03NOV1992 

01 DECl992 

070CT1992 

03NOV1992 

01 DECl992 

O5MAY 1993 

070CT1992 

03NOV1992 

01DECl992 

05MAY 1993 

03NOV1992 

01DEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

01 DEC1992 

070CT1992 

03NOV1992 

OlDEC1992 

05MAYl993 

070CT1992 

03NOV1992 

01DEC1992 

O5MAY 1993 

070CT1992 

09NOV1992 

01DECl992 

07DECl992 

05MAY 1993 

27JUL1992 

070CT1992 

03NOV1992 

01 DEC1992 

27JULl992 

070CT1992 

03NOV1992 

01 DECl992 

070CT1992 

03NOV1992 

OlDECl992 

WAY 1993 

070CT1992 

03NOV1992 

01 DECl992 

05MAY1993 

070CT1992 

03NOV1992 

OlDEC1992 

05MAY 1993 

070CT1992 

03NOVl992 

OlDEC1992 

WAY 1993 

27JUL1992 

070CT1992 

03NOV1992 

OlDECl992 

070CT1992 

03NOVI 992 

01 DECI 992 

OWY 1993 

070CT1992 

OJNOV1992 

01DEC1992 

OSMAY 1993 

070CT1992 

03NOV1992 

01 DECl992 

Page 102 of 176 

C 

c 

c 

c 

C 

C 

C 

C 

c 

C 

C 

c 

C 

C 

c 

C 

C 

C 

C 

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C 

C 

C 

c 

C 

Q 

c 

c 

< 

C 

C 

c 

< 

c 

C 

< 

C 

C 

C 

C 

< 

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N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

uglL 

uglL 

uglL 

uglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

uglL 

mglL 

mglL 

mgfl 

mgfl 

WlL 

mglL 

mglL 

wfl 

su 

su 

su 

su 

su 

ugfl 

ugfl 

ug5 

ugfl 

uglL 

uglL 

uglL 

uglL 

mgfl 

mglL 

mglL 

mglL 

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mglL 

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mglL 

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ugfl 

ugk 

ugfl 

WlL 

wk 

mglL 

mgk 

mglL 

wfl 

mgk 

wR 

wk 

mgfl

Calcium 

Calcium 

Calcium 

Calcium 

Chromium 

Chromium 

Chromium 

Chromium 

Cobalt 

Coban 

Cobalt 

Coban 

Copper 

Copper 

Copper 

Copper 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Iron 

Iron 

Iron 

Iron 

Lead 

Lead 

Lead 

Lead 

Lithium 

Lithium 

Lithium 

Lithium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Manganese 

Manganese 

Manganese 

Manganese 

Mercury 

Mercury 

Mercury 

Mercury 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Nickel 

Nickel 

Nickel 

Nickel 

Niobium 

Niobium 

Niobium 

Niobium 

PCB 

PCB 

PCB 





Potassium 

Potassium 

Potassium 

Potassium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 




Cadmium 7440-43-9 625-93 05MAY1993 WL O.OOE+OO < N 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

100-41-4 

100-41-4 

100-41-4 

100-41-4 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

1336-36-3 

1336-36-3 

1336-36-3 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-18-0 

7440-18-8 

7440-18-8 

7440-18-8 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1451 -92 

1800-92 

1943-92 

2108-92 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1867-92 

1943-92 

2108-92 

1800-92 

1943-92 

2108-92 

62593 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

070CT1992 

03NOV1992 

01 DEC1992 

O5MAYl 993 

070CT1992 

03NOV1992 

01 DEC1992 

O5MAYI 993 

070CT1992 

03NOV1992 

01 DEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

OlDEC1992 

05MAYI 993 

27JULl992 

070CT1992 

03NOV1992 

OlDEC1992 

070CT1992 

03NOV1992 

OlDECl992 

O5MAYl 993 

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OSMAYI993 

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03NOV1992 

01DEC1992 

M Y 1993 

070CT1992 

03NOV1992 

OlDECl992 

05MAY 1993 

070CT1992 

03NOVI 992 

OlDEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

OlDEC1992 

05MAY1993 

070CT1992 

03NOV1992 

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M Y 1993 

070CT1992 

03NOV1992 

01 DEC1992 

05MAY1993 

070CT1992 

03NOV1992 

01 DEC1992 

05MAYI993 

190CT1992 

03NOV1992 

01 DECl992 

070CT1992 

03NOV1992 

01 DECI 992 

05MAY 1993 

070CT1992 

03NOV1992 

01 DECl992 

05MAY 1993 

070CT1992 

03NOV1992 

01 DECl992 

M Y 1993 

Page 103 of 176 

WL 

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WL 

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WL 

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WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

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WL 

WL 

WL 

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mglL 

mg/L 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

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mglL 

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mg1L 

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mglL 

mglL 

mg1L 

mglL 

mgk 

mglL 

mglL 

mglL 

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mg5 

mglL 

mg5 

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mglL 

mgfl 

mgfl 

mglL 

mglL 

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mglL 

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mg/L 

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mg5 

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mglL 

mglL 

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Silicon 7440-21-3 1800-92 070CT1992 WL 5.00E+00 < N mg1L 

Silicon 

Silicon 

Silicon 

Silver 

Silver 

Silver 

Silver 

Sodium 

Sodium 

Sodium 

Sodium 

Strontium 

Strontium 

Strontium 

Strontium 

Tantalum 

Tantalum 

Tantalum 

Thallium 

Thallium 

Thallium 

Thallium 

Thorium 

Thorium 

Thorium 

Thorium 

Tin 

Tin 

Tin 

Tin 

Titanium 

Titanium 

Titanium 

Titanium 

Toluene 

Toluene 

Toluene 

Toluene 









Tungsten 

Tungsten 

Tungsten 

Tungsten 

Uranium 

Uranium 

Uranium 

Uranium 

Vanadium 

Vanadium 

Vanadium 

Xylene 

Xylene 

Xylene 

Xylene 

Zinc 

Zinc 

Zinc 

Zinc 

Zirconium 

Zirconium 

Zirconium 

Zirconium 

PH 

PH 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-25-7 

7440-25-7 

7440-25-7 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-31-5 

7440-31-5 

7440-31-5 

7440-31-5 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

108-88-3 

108-88-3 

108-88-3 

108-88-3 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-61-1 

7440-61 -1 

7440-61-1 

7440-61 -1 

7440-62-2 

7440-62-2 

7440-62-2 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

so296 

so296 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1451 -92 

1800-92 

1943.92 

2108-92 

1451-92 

1800-92 

1943-92 

2108-92 

1451-92 

1800-92 

1943-92 

2108-92 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1943-92 

2108-92 

625-93 

1451 -92 

1800-92 

1943-92 

2108-92 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1943-92 

2108-92 

625-93 

1800-92 

1973-92 

03NOV1992 

OlDECl992 

05MAY 1 993 

070CT1992 

03NOV1992 

01 DEC1992 

O5MAY 1993 

070CT1992 

03NOV1992 

01 DECl992 

O5MAY 1993 

070CT1992 

03NOV1992 

01 DEC1992 

O5MAY 1993 

070CT1992 

03NOV1992 

05MAYl993 

070CT1992 

03NOV1992 

OlDEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

OlDECl992 

05MAYl993 

070CT1992 

03NOV1992 

01DEC1992 

05MAYl993 

070CT1992 

03NOV1992 

01DEC1992 

05MAY1993 

27JULl992 

070CT1992 

03NOV1992 

01 DEC1992 

27JULl992 

070CT1992 

03NOV1992 

01 DECl992 

27JULl992 

070CT1992 

03NOV1992 

01 DECl992 

070CT1992 

03NOV1992 

01 DEC1992 

(HMAY 1 993 

070CT1992 

03NOV1992 

01DEC1992 

05MAY1993 

03NOV1992 

01 DECl992 

(HMAY1993 

27JULl992 

070CT1992 

03NOV1992 

OlDECl992 

070CT1992 

03NOV1992 

01 DEC1992 

osMAYl993 

070CT1992 

03NOV1992 

01DECl992 

05MAY 1993 

070CT1992 

09NOV1992 

Page 104 of 176 

WL 

WL 

WL 

WL 

WL 

VK 

WL 

VK 

WL 

WL 

VK 

WL 

VK 

WL 

WL 

WL 

WL 

WL 

VK 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

WL 

WL 

VK 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

VK 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

WL 

WL 

VK 

VK 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

N 

J 

N 

N 

c 

N 

< N 

< N 

c 

N 

N 

N 

J 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mg/L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mg/L 

mglL 

WlL 

mglL 

mgfl 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mg/L 

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mglL 

mgfl 

mgfl 

mgfl 

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mgfl 

mglL 

uglL 

uglL 

uglL 

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uglL 

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uglL 

uglL 

WlL 

WlL 

mgfl 

mglL 

mglL 

mg/L 

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mglL 

mgfl 

mg1L 

msn 

ugfl 

ug1L 

ugfl 

ugk 

wk 

mgk 

mg/L 

msn 

mgfl 

mgk 

wfl 

mglL 

su 

su




PH SO296 2108-92 01DEC1992 WL 8.00E+00 N su 

PH 

PH 

WAG 7. SWU 8, C746K-G 









Aluminum 

Aluminum 

Aluminum 

Aluminum 

Antimony 

Antimony 

Antimony 

Antimony 

Arsenic 

Arsenic 

Arsenic 

Barium 

Barium 

Barium 

Barium 

Benzene 

Benzene 

Benzene 

Benzene 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Bismuth 

Bismuth 

Bismuth 

Blsmuth 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Calcium 

Calcium 

Calcium 

Calcium 

Chromium 

Chromium 

Chromium 

Chromium 

Cobalt 

Coball 

Coball 

Coball 

Copper 

Copper 

Copper 

Copper 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Iron 

Iron 

Iron 

Iron 

Lead 

Lead 

Lead 

Lead 

Lilhium 

SO296 

SO296 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

71-43-2 

71-43-2 

71-43-2 

71-43-2 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-47-3 

7440-47-3 

744047-3 

7440-47-3 

744048-4 

7440-48-4 

7440-48-4 

7440-484 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

100-41-4 

100-41-4 

10041-4 

100-41-4 

7439-89-6 

7439-89-6 

7439-89-6 

7439-896 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-93-2 

2144-92 

625-93 

1452-92 

1799-92 

1944-92 

2109-92 

1452-92 

1799-92 

1944-92 

2109-92 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1452-92 

1799-92 

1944-92 

2109-92 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1452-92 

1799-92 

1944-92 

2109-92 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

07DEC1992 

O5MAY 1993 

27JUL1992 

070CT1992 

03NOV1992 

01DEC1992 

27JUL1992 

070CT1992 

03NOV1992 

01DEC1992 

070CT1992 

03NOV1992 

01DEC1992 

O5MAY 1993 

070CT1992 

03NOV1992 

01 DEC1992 

OSMAY 1993 

070CT1992 

03NOV1992 

OSMAY 1993 

070CT1992 

03NOV1992 

OlDEC1992 

O5MAY 1993 

27JULl992 

070CT1992 

03NOV1992 

OlDEC1992 

070CT1992 

03NOV1992 

01 DECl992 

MAY 1993 

070CT1992 

03NOV1992 

01 DEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

01DEC1992 

05MAY 1993 

070CT1992 

03NOVl 992 

OlDECl992 

05MAY1993 

070CT1992 

03NOV1992 

01DEC1992 

W Y 1993 

070CT1992 

03NOV1992 

01 DEC1992 

MAY 1993 

070CT1992 

03NOV1992 

01DEC1992 

MAY1993 

27JUL1992 

070CT1992 

03NOV1992 

01DECl992 

070CT1992 

03NOV1992 

01DEC1992 

MAY 1993 

070CT1992 

03NOV1992 

01 DECl992 

W Y 1993 

070CT1992 

Page 105 of 176 

WL 

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WL 

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WL 

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WL 

WL 

WL 

WL 

WL 

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WL 

WL 

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WL 

WL 

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WL 

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WL 

WL 

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WL 

WL 

WL 

WL 

WL 

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uglL 

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mg/L 

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mg/L 

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mgfl 

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mglL 

mg/L 

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mglL 

mglL 

mglL 

mglL 

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ug1L 

uglL 

ugfl 

uglL 

mglL 

mg/L 

mgfl 

mglL 

WlL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

WlL 

WlL 

mgfl 

mglL 

mglL 

mglL 

WlL 

WlL 

WlL 

Wfl 

mglL 

mglL 

uglL 

uglL 

uglL 

uglL 

msk 

mgk 

mgfl 

Wfl 

WlL 

Wfl 

WlL 

Wk 

WlL




Lithium 7439-93-2 1944-92 03NOV1992 VK O.OOE+OO C N mglL 

Lithium 

Lithium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Manganese 

Manganese 

Manganese 

Manganese 

Mercury 

Mercury 

Mercury 

Mercury 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Nickel 

Nickel 

Nickel 

Nickel 

Niobium 

Niobium 

Niobium 

Niobium 

PCB 

PCB 

PCB 





Potassium 

Potassium 

Potassium 

Potassium 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Silicon 

Silicon 

Silicon 

Sillcon 

Silver 

Silver 

Silver 

Silver 

Sodium 

Sodium 

Sodium 

Sodium 

Strontium 

Strontium 

Strontium 

Strontium 

Tantalum 

Tantalum 

Tantalum 

Thallium 

Thallium 

Thallium 

Thallium 

Thorium 

Thorium 

Thorium 

Thorium 

Tin 

Tin 

Tin 

7439-93-2 

7439-93-2 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-90-7 

7439-90-7 

7439-90-7 

7439-90-7 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-03-1 

7440-03-1 

7440-03-1 

7440-03-1 

1336-36-3 

1336-36-3 

1336-36-3 

PHOSPHATEASP 

7723-14-0 

7723-14-0 

7440-09-7 

7440-09-7 

7440-09-7 

7449-10-0 

7440-10-8 

7723-14-0 

7440-09-7 

7440-10-0 

7440-18-8 

7440-21-3 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

7440-24-6 

7440-24-6 

7440-24-6 

7440-25-7 

7440-257 

7440-20-0 

7440-24-6 

7440-25-7 

7440-2ao 

7440-2ao 

7440-2a-o 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-31 -5 

7440-31-5 

7440-31-5 

2109-92 

624-93 

1799-92 

1944-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1944-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1866-92 

1944-92 

21 09-92 

1-92 

624-93 

1944-92 

624-93 

1799-92 

1944-92 

21 09-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

624-93 

1944-92 

624-93 

1799-92 

1944-92 

21 09-92 

624-93 

1799-92 

1944-92 

2109-92 

1799-92 

2109-92 

1799-92 

2109-92 

1799-92 

2109-92 

1799-92 

21 09-92 

2109-92 

01DEC1992 

OSMAY 1993 

070CT1992 

03NOV1992 

01DEC1992 

OSMAY 1993 

070CT1992 

03NOV1992 

01 DEC1992 

05MAY 1993 

070CT1992 

03NOV1992 

01DEC1992 

OSMAY1993 

070CT1992 

03NOV1992 

01DEC1992 

OSMAY 1993 

070CT1992 

03NOV1992 

01 DEC1992 

05MAY1993 

070CT1992 

03NOV1992 

01 DECl992 

OSMAYl993 

19OCTl992 

03NOV1992 

01 DECl992 

070CT1992 

03NOV1992 

OlDEC1992 

05MAYl993 

070CT1992 

03NOV1992 

OlDECl992 

(HMAY 1993 

070CT1992 

03NOV1992 

01 DECl992 

MY1993 

070CT1992 

03NOV1992 

01DEC1992 

MY1993 

070CT1992 

03NOV1992 

OlDECl992 

05MAY1993 

070CT1992 

03NOV1992 

01DECl992 

MY1993 

07OCT1992 

03NOV1992 

OlDECl992 

OSMAY1993 

070CT1992 

03NOV1992 

MAY1993 

070CT1992 

03NOV1992 

01 DECl992 

MAY1993 

070CT1992 

03NOV1992 

01 DEC1992 

OSMAYl993 

070CT1992 

03NOV1992 

01 DEC1992 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

WL 

VK 

WL 

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WL 

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WL 

WL 

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WL 

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WL 

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WL 

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O.OOE+OO 

O.OOE+OO 

3.00E+00 



3.00E+00 

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2.00E+00 

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O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+W 

O.WE+W 

O.WE+W 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 



2.WE+00 

2.00E+00 

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O.WE+OO 

O.WE+W 

5.WE+W 

5.WE+W 

5.WE+W 

6.WE+W 

O.WE+W 

O.WE+W 

O.WE+W 

O.WE+OO 

1.20E+01 

1.80E+01 

I 

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mglL 

mgk 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

ugfl 

ug/L 

ugfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgR 

mglL 

mgfl 

WlL 

mglL 

mglL 

mgfl 

mglL 

mglL 

WlL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

WlL 

mg/L 

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mglL 

mglL 

mglL 

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WlL 

mglL 

WlL 

mglL 

mg1L 

mgfl 

mgfl 

Page 106 of 176




Tin 7440-31 -5 624-93 05MAY1993 VK 5.00E+00 c N mglL 

Titanium 

Titanium 

Titanium 

Titanium 

Toluene 

Toluene 

Toluene 

Toluene 


Trans-l.2-Dichloroethene 







Tungsten 

Tungsten 

Tungsten 

Tungsten 

Uranium 

Uranium 

Uranium 

Uranium 

Vanadium 

Vanadium 

Vanadium 

Xylene 

Xylene 

Xylene 

Xylene 

Zinc 

Zinc 

Zinc 

Zinc 

Zirconium 

Zirconium 

Zirconium 

zirconium 

PH 

PH 

PH 

PH 

PH 

WAG 7, SWdU 8, C746K-GA1 

1.1 .l-Trichloroethane 

1,l.l-Trichloroethane 







Acetone 

Acetone 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminurn 

Aluminum 

Aluminum 

Aluminurn 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

108-88-3 

108-88-3 

108-88-3 

108-88-3 

156-60-5 

156-60-5 

156-60-5 

156-60-5 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-62-2 

7440-62-2 

7440-62-2 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

SO296 

SO296 

SO296 

SO296 

SO296 

71-55-6 

71 -55-6 

75-34-3 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

75-35-4 

67-64-1 

67-64-1 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

1799-92 

1944-92 

2109-92 

624-93 

1452-92 

1799-92 

1944-92 

2109-92 

1452-92 

1799-92 

1944-92 

2109-92 

1452-92 

1799-92 

1944-92 

2109-92 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1944-92 

2109-92 

624-93 

1452-92 

1799-92 

1944-92 

2109-92 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1944-92 

2109-92 

624-93 

1799-92 

1974-92 

2109-92 

2145-92 

624-93 

140-95 

433-95 

1959-92 

2208-92 

433-95 

1959-92 

2208-92 

433-95 

1443-93 

1703-93 

1200-94 

1443-93 

1551-93 

16-95 

1841-93 

1959-92 

21-94 

2156-93 

2857-94 

291-94 

433-95 

510-94 

630-93 

783-95 

811-93 

897-94 

070CT1992 

03NOV1992 

01DECl992 

OSMAYl993 

27JUL1992 

070CT1992 

03NOV1992 

01DEC1992 

27JULl992 

070CT1992 

03NOVl992 

01 DEC1992 

27JULl992 

070CT1992 

03NOV1992 

01DECl992 

070CT1992 

OSNOV1992 

01DEC1992 

05MAY1993 

07OCT1992 

03NOV1992 

01DEC1992 

05MAY 1993 

03NOV1992 

01DECl992 

05MAY1993 

27JUL1992 

070CT1992 

03NOV1992 

01DEC1992 

070CT1992 

03NOV1992 

01 DEC1992 

05MAYl993 

070CT1992 

03NOV1992 

01DEC1992 

OSMAY 1993 

070CT1992 

09NOV1992 

OlDEC1992 

07DEC1992 

05MAYl993 

2OJANl995 

03MAR1995 

05NOV1992 

16DEC1992 

O3MARl995 

05NOV1992 

16DEC1992 

03MAR1995 

15SEPl993 

220CT1993 

05MAY 1994 

15SEPl993 

050CT1993 

05JAN1995 

04NOV1993 

05NOVl992 

WAN1994 

10DEC1993 

02DEC1994 

04FEB1994 

OM1995 

OM1994 

OSMAY 1993 

03MAY1995 

WUN1993 

08APRl994 

Page 107 of 176 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

5.00E+00 

5.00E+00 

5.00€+00 

5.00€+00 

5.00E+00 

5.00E+OO 

5.00E+00 

5.00E+00 

l.OOE+OO 

1.00E+00 

l.OOE+OO 

1 .00E+00 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

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O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

l.OOE+Ol 

1.00E+01 

1.00E+Ol 

1 .00E+01 

0.00E+00 

0.00E+00 

0.00E+00 

O.OOE+OO 

0.00E+00 

0.00€+00 

0.00E+00 

0.00E+00 

7.00E+W 

7.00E+00 

8.00E+00 

7.00E+00 

6.00E+00 

5.00E+OO 

5.00E+00 

5.00€+00 

5.00E+W 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+W 

1.70E+01 

7.00E+OO 

2.14E+02 

1.27E+02 

1.18E+02 

3.50E+02 

1.06E+02 

2.79E+02 

2.98E+02 

2.92E+02 

1.62E+02 

3.35E+02 

3.02€+02 

3.11 E+O2 

3.30E+Ol 

1.80E+01 

2.6M+02 

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N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

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N 

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N 

N 

N 

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N 

N 

N 

N 

N 

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N 

N 

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mglL 

mglL 

mglL 

uglL 

uglL 

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uglL 

uglL 

uglL 

uglL 

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uglL 

uglL 

mglL 

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mglL 

mgk 

mglL 

mglL 

mgk 

mglL 

mg1L 

mg/L 

mglL 

uglL 

uglL 

uglL 

uglL 

mglL 

mgk 

mglL 

mgfl 

mgk 

mglL 

mglL 

mglL 

su 

su 

su 

su 

su 

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uglL 

uglL 

uglL 

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uglL 

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ug/L 

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mglL 

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mgk 

mgk 

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mglL 

WlL 

mgfl 

mgk 

mg/L 

msnmsn


...--.- 


Antimony 7440-36-0 1959-92 05NOV1992 VK O.OOE+OO < N mglL 

Antimony 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Benzene 

Benzene 

Beryllium 

Beryllium 

Bismuth 

Bismuth 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cad m i u m 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Calcium 

Calcium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

7440-36-0 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

71-43-2 

71-43-2 

7440-41-7 

7440-41-7 

7440-69-9 

7440-69-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

744043-9 

744043-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

7440-47-3 

7440-41 -3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

630-93 

1200-94 

1443-93 

1551-93 

16-95 

1841 -93 

1959-92 

21-94 

2156-93 

2857-94 

291-94 

433-95 

510-94 

630-93 

783-95 

811-93 

897-94 

1200-94 

1443-93 

1551-93 

16-95 

1841 -93 

1959-92 

21-94 

2156-93 

2857-94 

291-94 

433-95 

510-94 

630-93 

783-95 

811-93 

897-94 

1959-92 

2208-92 

1959-92 

630-93 

1959-92 

630-93 

1200-94 

1443-93 

1551-93 

16-95 

1841-93 

1959-92 

21-94 

2156-93 

2857-94 

291-94 

433-95 

510-94 

630-93 

783-95 

811-93 

897-94 

952-95 

1959-92 

630-93 

1200-94 

1443-93 

1551-93 

16-95 

1841-93 

1959-92 

21-94 

2156-93 

2857-94 

291-94 

433-95 

510-94 

630-93 

05MAY1993 

O5MAY 1994 

15SEPl993 

050CT1993 

O5JANl995 

04NOV1993 

05NOV1992 

05JAN1994 

10DEC1993 

02DEC1994 

04FEB1994 

03MAR1995 

03MAR 1994 

05MAY 1993 

03MAYl995 

04JUN1993 

08APR1994 

O5MAY 1994 

15SEP1993 

050CT1993 

05JAN1995 

04NOV1993 

05NOV1992 

05JAN1994 

1 ODECl993 

02DEC1994 

04FEB1994 

03MARl995 

03MAR1994 

05MAY1993 

03MAY 1995 

04JUN1993 

OBAPR1994 

05NOV1992 

16DEC1992 

05NOV1992 

OFMAY1993 

05NOV1992 

MAY1993 

05MAY 1994 

15SEPl993 

050CT1993 

WAN1995 

04NOV1993 

05NOVl992 

WAN1994 

10DECl993 

02DEC1994 

04FEB1994 

O3MARl995 

03MARl994 

OSMAY 1993 

03MAY 1995 

04JUN1993 

08APRl994 

01 JUNl995 

05NOV1992 

OSMAYl993 

MAY 1994 

15SEP1993 

05OCT1993 

WAN1995 

04NOV1993 

05NOV1992 

05JAN1994 

10DEC1993 

02DEC1994 

04FEB1994 

03MARl995 

03MARl994 

MAY1993 

Page 108 of 176 

C 

N 

N 

< N 

N 

CS 

N 

c 

N 

N 

C 

N 

X 

N 

4s 

N 

< N 

< N 

N 

< N 




Chromium 

7440-47-3 783-95 03MAY1995 WL O.OOE+OO U N 

mg1L 

Chromium 

7440-47-3 

811-93 04JUN1993 WL 

N 

mglL 

Chromium 

Chromium 

Coban 

Cobalt 

Copper 

Copper 

Estimated Flow 
































































7440-47-3 

7440-47-3 

7440-48-4 

7440-48-4 

7440-50-8 

7440-50-8 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

897-94 

952-95 

1959-92 

630-93 

1959-92 

630-93 

1004-93 

1004-95 

1025-93 

103-95 

1045-95 

1065-94 

1073-95 

1119-95 

1136-95 

1143-95 

1200-94 

1219-95 

1251 -94 

140-95 

1443-93 

1517-93 

1551-93 

1561 -94 

16-95 

1610-94 

1636-93 

1653-94 

1703-93 

1713-94 

176-95 

1777-93 

1786-94 

1833-94 

1841-93 

1895-93 

1916-94 

1967-94 

2003-93 

2022-94 

2094-93 

21-94 

2107-94 

2119-94 

2156-93 

216-95 

2190-93 

2200-94 

2220-93 

224894 

2267-93 

2332-94 

2409-94 

2476-94 

2479-94 

255-95 

2615-94 

2687-94 

2731-94 

276894 

2838-94 

2857-94 

291-94 

2918-94 

2987-94 

3005-94 

301-95 

3087-94 

3101-94 

369-95 

08APR1994 

01JUN1995 

05NOV1992 

05MAY 1993 

05NOV1992 

O5MAY 1993 

01 JUL1993 

08JUN1995 

09JUL1993 

13JAN1995 

13JUN1995 

22APR1994 

20JUN1995 

22JUN1995 

26JUN1995 

06JUL1995 

05MAY1994 

11 JUL1995 

13MAY 1994 

20JAN1995 

15SEP1993 

28SEP1993 

050CT1993 

24JUN1994 

05JAN1995 

OlJUL1994 

150CTl993 

08JUL1994 

220CT1993 

15JULl994 

26JANl995 

28OCT1993 

22JULl994 

29JUL1994 

04NOV1993 

12NOV1993 

05AUG1994 

12AUG1994 

24NOV1993 

19AUGl994 

OSDEC1993 

05JAN1994 

26AUG1994 

02SEP1994 

lODECl993 

03FEB1995 

15DEC1993 

09SEP1994 

22DEC1993 

16SEP1994 

30DEC1993 

3OSEPl994 

070CT1994 

140CT1994 

19OCTl994 

08FEB1995 

280CT1994 

04NOV1994 

11 NOVl994 

17NOV1994 

23NOV1994 

02DEC1994 

04FEB1994 

08DEC1994 

14DEC1994 

23SEPl994 

17FEB1995 

27DECl994 

22DECl994 

24FEB1995 

WL 

WL 

VK 

WL 

WL 

WL 

WL 

WL 

VK 

WL 

WL 

WL 

WL 

VK 

WL 

VK 

WL 

VK 

VK 

VK 

WL 

WL 

VK 

WL 

VK 

WL 

VK 

VK 

WL 

VK 

VK 

VK 

VK 

VK 

WL 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

WL 

VK 

VK 

VK 

WL 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

WL 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

c 

c 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

J 

Q 

Q 

Q 

Q 

Q 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Q 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

FIELD 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

Page 109 of 176




Estimated Flow EST FLOW 417-94 18FEB1994 VM 1.30E+01 N GaVDav 



















Ethylbenzene 

Ethylbenzene 

Flow 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

GCMS Scan 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

100-41-4 

100-41-4 

SO840 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCNS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

GCMS SCAN 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

433-95 

453-94 

470-95 

497-95 

510-94 

543-95 

564-95 

612-94 

629-95 

666-95 

711-95 

743-95 

746-94 

783-95 

813-95 

88495 

919-95 

952-95 

1959-92 

2208-92 

510-94 

1004-95 

1049-95 

1065-94 

1143-95 

1200-94 

1219-95 

140-95 

1517-93 

1551 -93 

16-95 

2479-94 

2768-94 

2857-94 

2987-94 

3005-94 

301-95 

433-95 

497-95 

629-95 

711-95 

783-95 

884-95 

897-94 

952-95 

1200-94 

1443-93 

1551 -93 

16-95 

1841-93 

1959-92 

21-94 

2156-93 

2857-94 

291-94 

433-95 

510-94 

630-93 

783-95 

811-93 

897-94 

109-94 

1200-94 

1443-93 

1551 -93 

16-95 

1841-93 

1959-92 

21-94 

215693 

2857-94 

03MAR1995 

25FEB1994 

1 OMARl995 

17MAR1995 

03MAR1994 

23MAR1995 

28MAR1995 

17MAR1994 

O5APRl995 

13APRl995 

21APR1995 

26APR1995 

31MAR1994 

03MAYl995 

llMAYl995 

17MAY1995 

25MAYl995 

01JUNl995 

05NOV1992 

16DECl992 

03MAR1994 

OBJUNl995 

14JUNl995 

22APR 1994 

06JULl995 

05MAY 1994 

11 JULl995 

20JAN1995 

28SEPl993 

050CT1993 

WAN1995 

190CT1994 

17NOV1994 

02DEC1994 

14DECl994 

23SEPl994 

17FEB1995 

03MAR1995 

17MAR1995 

05APRl995 

2lAPR1995 

03MAY1995 

17MAY1995 

08APRl994 

01JUN1995 

OSMAYl994 

15SEP1993 

050CT1993 

05JANl995 

04NOV1993 

05NOV1992 

WAN1994 

1 ODECl993 

02DEC1994 

04FEBl994 

03MARl995 

03MARl994 

05MAYl993 

03MAY1995 

WUN1993 

08APR1994 

12JAN1994 

OSMAY 1994 

15SEP1993 

050CT1993 

WAN1995 

04NOVl993 

05NOVl992 

05JANl994 

1 ODECl993 

02DECl994 

Page 110 of 176 

VM 

VM 

WL 

VM 

WL 

WL 

VM 

WL 

VM 

VM 

VM 

WL 

VM 

WL 

WL 

WL 

VK 

WL 

WL 

WL 

VM 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

WL 

VK 

WL 

WL 

WL 

WL 

VK 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

WL 

VK 

WL 

WL 

VK 

WL 

WL 

WL 

VK 

VK 

VK 

WL 

VK 

WL 

VK 

VK 

VK 

VK 

WL 

Q 

< 

c 

X 

X 

vx 

X 

V 

X 

X 

V 

V 

X 

V 

V 

V 

X 

V 

X 

X 

X 

X 

X 

X 

X 

V 

X 

B 

c 

< 

c 

< 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Q 

Q 

N 

Q 

Q 

HX 

N 

N 

N 

N 

N 

PGDP 

N 

Q 

N 

Q 

Q 

Q 

Q 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

GaVDay 

GaVDay 

GaVDay 

GaUDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

uglL 

uglL 

MGD 

uglL 

uglL 

uglL 

uglL 

ug5 

uglL 

ugk 

ug/L 

uglL 

uglL 

uglL 

ugk 

uglL 

ug5 

ugk 

uglL 

uglL 

ug1L 

uglL 

ugfl 

ug1L 

ug1L 

uglL 

uglL 

mglL 

mglL 

mglL 

mg5 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgk 

mgk 

mgk 

mglL 

mglL 

mgk 

mgk 

mgk 

maR 

mglL 

mgk 

mglL 

mg5 

mgk




Lead 7439-92-1 291-94 04FEB1994 WL 1.00E+00 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

LIhium 

Lithium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-93-2 

7439-93-2 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

433-95 

510-94 

630-93 

783-95 

811-93 

897-94 

952-95 

1959-92 

630-93 

1200-94 

1443-93 

1551-93 

16-95 

1841-93 

1959-92 

21-94 

2156-93 

2857-94 

291-94 

433-95 

510-94 

630-93 

783-95 

811-93 

897-94 

Manganese ' 

7439-96-5 

1200-94 

7439-96-5 

1443-93 

7439-96-5 

1551-93 

7439-96-5 

16-95 

7439-96-5 

1841 -93 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Mercury 

Mercury 

Mercury 

Molybdenum 

Molybdenum 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Niobium 

Niobium 

PCB 



Potassium 

Potassium 

Potassium 

Potassium 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439 - 96 - 5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7439-97-6 

7439-98-7 

7439-98-7 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-03-1 

7440-03-1 

1336-36-3 

7723-14-0 

7723-14-0 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

1959-92 

21-94 

2156-93 

2857-94 

291-94 

433-95 

510-94 

630-93 

783-95 

811-93 

897-94 

1551-93 

1959-92 

630-93 

1959-92 

630-93 

1200-94 

1443-93 

1551 -93 

16-95 

1841-93 

1959-92 

21-94 

2156-93 

2857-94 

291-94 

433-95 

510-94 

630-93 

783-95 

811-93 

897-94 

1959-92 

630-93 

2132-92 

1959-92 

630-93 

1200-94 

1443-93 

1551 -93 

16-95 

03MAR1995 

03MAR1994 

O5MAY 1993 

O3MAYl 995 

04JUN1993 

08APR1994 

OlJUN1995 

05NOV1992 

05MAY 1993 

O5MAY 1994 

15SEP1993 

050CT1993 

05JAN1995 

04NOV1993 

05NOV1992 

05JANl994 

1 ODECI 993 

02DEC1994 

04FEB1994 

03MAR1995 

03MAR1994 

05MAY 1993 

O3MAY 1995 

04JUN1993 

08APRl994 

05MAY 1994 

15SEP1993 

050CT1993 

05JAN1995 

04NOV1993 

OSNOVI 992 

05JANl994 

10DECl993 

02DEC1994 

04FEB1994 

O3MARl 995 

03MAR 1994 

05MAY 1993 

03MAY 1995 

04JUN1993 

08APR1994 

050CT1993 

05NOV1992 

05MAY 1993 

05NOV1992 

05MAY 1993 

WAY 1994 

15SEPl993 

050CTI993 

O5JANl 995 

04NOV1993 

05NOV1992 

05JANl994 

10DEC1993 

02DEC1994 

MFEB 1994 

03MAR1995 

03MAR1994 

05MAY 1993 

O3MAY 1995 

04JUN1993 

08APR1994 

05NOVI992 

OSMAY 1993 

07DECI 992 

05NOV1992 

OsMAY1993 

WAY1994 

15SEP1993 

050CTI993 

(HJANI 995 

Page 111 of 176 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

WL 

WL 

WL 

WL 

VK 

VK 

WL 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

WL 

VK 

WL 

WL 

WL 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

VK 

VK 

VK 

WL 

VK 

WL 

VK 

VK 

WL 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

O.OOE+OO 

O.OOE+OO 

l.OOE+OO 

O.OOE+OO 

1.20E+01 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

1.00E+02 

7.10E+01 

7.3OE+01 

1 .08E+02 


8.40E+01 

1.06E+02 

9.80E+01 

7.3OE+01 

l.lOE+02 

1.14E+02 

1.08E+02 

1.80E+01 

1.80E+01 

1.38E+02 


1.21 E+02 

8.10E+01 

8.40E+01 

1.48E+02 

5.30E+01 

1.13E+02 

1.25E+02 

1.17E+02 

8.20E+01 

1.21 E+02 

1.00E+02 

1.25E+02 

2.00E+01 

1.40E+01 

1.60E+02 


O.OOE+OO 

0.00E+00 

0.00E+00 

0.00E+00 

O.OOE+OO 

l.OOE+OO 

1 .00E+OO 

O.OOE+OO 

1.00E+00 

O.OOE+OO 

l.OOE+OO 

l.OOE+OO 

1 .00E+00 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

1.00E+00 

0.00E+00 

O.OOE+OO 

l.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.OOE+W 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

5.00E+00 

7 .OOE+ 00 

5.00E+00 

6.00E+00 

N 

N 

< N 

N 

N 

N 

< N 

N 

N 

< N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

< 

< 

< 

< 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mg/L 

mg1L 

mglL 

mg1L 

mglL 

mglL 

mglL 

W/L 

mglL 

mglL 

WlL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

uglL 

mglL 

mglL 

mglL 

mglL 

WR 

mgfl




Potassium 7440-09-7 1841-93 04NOV1993 VK 1.50E+01 N mg1L 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Beta 

Rad Beta 

Rad Beta 

Rad Beta 

Rad Beta 

Ruthenium 

Ruthenium 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silver 

Silver 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-46-1 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

7440-18-8 

7440-10-8 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

1959-92 

21-94 

2156-93 

2857-94 

291-94 

433-95 

510-94 

630-93 

783-95 

811-93 

897-94 

1143-95 

433-95 

783-95 

798-93 

952-95 

1143-95 

433-95 

783-95 

798-93 

952-95 

1959-92 

630-93 

1200-94 

1443-93 

1551-93 

16-95 

1841-93 

1959-92 

21-94 

2156-93 

2857-94 

291-94 

433-95 

510-94 

630-93 

703-95 

811-93 

097-94 

1959-92 

630-93 

1200-94 

1443-93 

1551-93 

16-95 

1041-93 

1959-92 

21-94 

2156-93 

2057-94 

291-94 

433-95 

510-94 

630-93 

703-95 

811-93 

097-94 

1200-94 

1443-93 

1551-93 

16-95 

1041-93 

1959-92 

21-94 

2156-93 

2857-94 

291-94 

433-95 

510-94 

630-93 

703-95 

05NOVI992 

OSJANI 994 

lODECl993 

02DEC1994 

04FEB1994 

03MAR1995 

03MAR1994 

OSMAY 1993 

03MAY I995 

O4JUN1 993 

08APRI994 

06JULl 995 

03MAR1995 

O3MAY 1995 

02JUN1993 

01JUN1995 

06JULl995 

03MAR1995 

03MAY1995 

02JUNl993 

01 JUN1995 

05NOV1992 

05MAY 1993 

05MAY 1994 

15SEPl993 

050CTI993 

05JAN1995 

04NOVl993 

05NOVI992 

OSJANl994 

lODECl993 

02DECl994 

04FEBl994 

03MAR1995 

03MARl994 

05MAYl993 

03MAYl995 

MJUNl993 

OBAPR 1994 

05NOV1992 

WAY 1993 

WAY 1994 

15SEPl993 

050CT1993 

WAN1 995 

04NOV1993 

05NOV1992 

05JAN1994 

lODECl993 

02DEC1994 

04FEBl994 

03MARI995 

03MAR1994 

OSMAY 1993 

03MAY 1995 

04JUNl993 

O0APRl994 

05MAY 1994 

15SEP1993 

OSOCT1993 

OSJAN1995 

04NOV1993 

OSNOV1992 

WAN1994 

10DEC1993 

02DECl994 

04FEBl994 

O3MAR1995 

03MAR1994 

05MAY 1993 

03MAY 1995 

Page 112 of 176 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

vlh 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

vlh 

VK 

WL 

VK 

VK 

VK 

VK 

VK 

VK 

WL 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

\IK 

VK 

VK 

VK 

VK 

VK 

VK 

WL 

VK 

VK 

WL 

VK 

VK 

VK 

WL 

VK 

VK 

WL 

VK 

VK 

VK 

2.00E+00 


3.00E+00 


5.00E+00 

9.00E+00 

6.00E+00 

3.00E+00 

3.00E+00 

8.00E+00 


l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

O.OOE+OO 

O.OOE+OO 




8.00€+01 

2.50E+01 

6.50E+Ol 


5.60E+01 

4.90E+Ol 

6.80E+01 

8.30E+Ol 

5.50E+01 

2.10E+01 

I .40E+01 


5.WE+01 

O.WE+OO 

O.OOE+OO 

3.10E+01 

1.90E+01 

2.50E+01 

3.70E+01 

1 .SOE+Ol 

3.00E+01 

3.20E+01 

3.1OE+O1 

2.40€+01 

3.20E+01 

2.30E+01 

2.90E+01 

5.00E+00 


5.3OE+01 

l.OOE+OI 

l.OOE+OO 

I .00E+00 

O.WE+OO 

l.WE+OO 

O.OOE+OO 

l.WE+W 

I .00E+00 

I .00E+00 

3.00E+W 

l.OOE+OO 

l.OOE+OO 

I .00E+00 

O.WE+OO 

O.OOE+W 

< 

< 

< 

< 

< 

< 

c 

< 

< 

< 

< 

< 

X 

J 

J 

< 

< 

J 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N




Strontium 7440-24-6 811-93 04JUN1993 VK 1.00E+00 N mglL 

Strontium 

Tantalum 

Tantalum 

Thallium 

Thallium 

Thorium 

Thorium 

Tin 

Tin 

Titanium 

Tianium 

Toluene 

Toluene 



















Tungsten 

Tungsten 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Vanadium 

Vanadium 

Xylene 

Xylene 

Zinc 

Zinc 

Zirconium 

Zirconium 


cis-1.2-diihloroethene 

cis-l,2dichloroethene 










7440-24-6 

7440-25-7 

7440-25-7 

7440-28-0 

7440-28-0 

7440-29-1 

7440-29-1 

7440-31 -5 

7440-31 -5 

7440-32-6 

7440-32-6 

108-88-3 

108-88-3 

156-60-5 

156-60-5 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

7440-33-7 

7440-33-7 

7440-61-1 

7440-61 -1 

7440-61-1 

7440-61 -1 

7440-61-1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-62-2 

7440-62-2 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

7440-67-7 

7440-67-7 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

897-94 

1959-92 

630-93 

1959-92 

630-93 

1959-92 

630-93 

1959-92 

630-93 

1959-92 

630-93 

1959-92 

2208-92 

1959-92 

2208-92 

1004-95 

1049-95 

1143-95 

1841-93 

1959-92 

21-94 

2156-93 

2208-92 

2267-93 

241-94 

291-94 

417-94 

433-95 

612-94 

884-95 

952-95 

1959-92 

630-93 

1200-94 

1551-93 

16-95 

1703-93 

1841-93 

1959-92 

21-94 

2132-92 

2156-93 

2857-94 

291-94 

433-95 

510-94 

629-95 

630-93 

783-95 

897-94 

952-95 

1959-92 

630-93 

1959-92 

2208-92 

1959-92 

630-93 

1959-92 

630-93 

1004-95 

1049-95 

1143-95 

1219-95 

1841-93 

21-94 

2156-93 

2267-93 

241-94 

291-94 

417-94 

433-95 

OBAPRl994 

05NOV1992 

O5MAY 1993 

05NOV1992 

05MAYl993 

05NOV1992 

OSMAY 1993 

05NOV1992 

O5MAY 1993 

05NOV1992 

O5MAY 1993 

05NOV1992 

16DEC1992 

05NOV1992 

16DEC1992 

OBJUN1995 

14JUN1995 

06JUL1995 

04NOV1993 

05NOV1992 

05JAN1994 

10DEC1993 

16DEC1992 

3ODEC1993 

21 JANl 994 

04FEB1994 

18FEB1994 

03MARl995 

17MAR1994 

17MAY 1995 

01JUNl995 

05NOV1992 

05MAYl993 

05MAY 1994 

050CT1993 

05JAN1995 

220CT1993 

04NOV1993 

OSNOV1992 

05JAN1994 

07DEC1992 

10DEC1993 

02DECl994 

04FEB1994 

03MAR1995 

03MARl994 

05APR1995 

WAY 1993 

03MAY 1995 

08APR1994 

OlJUNl995 

05NOVl992 

05MAY1993 

05NOV1992 

16DECl992 

05NOV1992 

CHMAY 1993 

OLNOV1992 

WAY 1993 

08JUN1995 

14JUN1995 

06JUL1995 

1 lJULl995 

04NOVl993 

WAN1 994 

10DEC1993 

30DEC1993 

21 JANl 994 

04FEBl994 

18FEBl994 

03MAR1995 

Page 113 of 176 

N 

N 

< N 

N 

< N 

C 

N 

< N 

< N 

< N 

N 

N 

< N 

< N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

JXU 

< 

< 

C 

< 

< 

< 

C 

< 

< 

Q 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

rnglL 

mgfl 

uglL 

uglL 

uglL 

uglL 

uglL 

ug1L 

ug1L 

uglL 

uglL 

uglL 

uglL 

uglL 

ugfl 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

Wfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mglL 

ugfl 

uglL 

uglL 

ugfl 

ugfl 

uglL 

uglL 

uglL 

ugfl 

uglL 

uglL 

ug5

I 




cis-1.2-dichloroethene 156-59-2 510-94 03MAR1994 VK 1.50E+01 N ualL 





PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

so296 

SO296 

SO296 

SO296 

so296 

so296 

SO296 

SO296 

SO296 

SO296 

SO296 

so296 

SO296 

SO296 

SO296 

so296 

SO296 

SO296 

so296 

SO296 

so296 

so296 

so296 

so296 

SO296 

so296 

SO296 

SO296 

SO296 

so296 

so296 

SO296 

SO296 

SO296 

SO296 

so296 

SO296 

SO296 

SO296 

so296 

SO296 

SO296 

SO296 

SO296 

so296 

so296 

so296 

SO296 

629-95 

711-95 

884-95 

952-95 

1004-93 

1004-95 

1025-93 

103-95 

1045-95 

1065-94 

1073-95 

1119-95 

1136-95 

1143-95 

1200-94 

1219-95 

1251-94 

140-95 

1443-93 

1517-93 

1551-93 

1561-94 

16-95 

1610-94 

1636-93 

1653-94 

1703-93 

1713-94 

176-95 

1777-93 

1786-94 

1833-94 

1841-93 

1895-93 

1916-94 

1967-94 

1976-92 

2003-93 

2022-94 

2094-93 

21-94 

2107-94 

2132-92 

2156-93 

216-95 

2187-92 

2190-93 

2200-94 

2220-93 

2221-92 

2238-92 

2248-94 

2267-93 

2332-94 

2409-94 

241-94 

2476-94 

2479-94 

255-95 

261-94 

2615-94 

2687-94 

2731-94 

2768-94 

2838-94 

2857-94 

291-94 

2918-94 

2987-94 

3005-94 

301-95 

05APR1995 

21 APRl995 

17MAY 1995 

01JUN1995 

01 JUL1993 

08JUN1995 

09JUL1993 

13JANl995 

13JUN1995 

22APR1994 

20JUN1995 

22JUN1995 

26JUN1995 

06JUL1995 

05MAY1994 

llJULl995 

13MAY 1994 

20JANl995 

15SEP1993 

28SEPl993 

050CT1993 

24JUNl994 

O5JANl995 

01 JULl994 

150CT1993 

08JULl994 

220CT1993 

15JUL1994 

26JAN1995 

280CT1993 

22JUL1994 

29JUL1994 

04NOVI 993 

12NOV1993 

05AUG1994 

lPAUGl994 

09NOVl992 

24NOV1993 

19AUG 1994 

OSDECl993 

O5JANl 994 

26AUG1994 

07DEC1992 

lODECl993 

03FEB1995 

14DEC1992 

15DECl993 

O9SEP1 994 

22DEC.1993 

21 DECl992 

28MC1992 

16SEPl994 

30DECl993 

3OSEPl994 

070CT1994 

21 JAN1994 

140CTI 994 

190CT1994 

08FEBl995 

28JAN1994 

28OCT1994 

04NOV1994 

1 1 NOVl994 

17NOV1994 

23NOV1994 

02DECl994 

04FEB1994 

08DEC1994 

14DECl994 

23SEP1994 

17FEBl995 

Page 114 of 176 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

J 

Q 

Q 

Q 

Q 

Q 

Q 

N 

N 

N 

N 

N 

N 

Q 

N 

N 

N 

N 

N 

N 

N 

FIELD 

FIELD 

N 

N 

N 

N 

uglL 

uglL 

uglL 

uglL 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su



~~ 


SO296 3087-94 27DEC1994 WL 3.00€+00 su 

, SWU 8, C746K-GA2 



Aluminum 

Antimony 

Arsenic 

Barium 

Benzene 

Beryllium 

Bismuth 

Cadmium 

Calcium 

Chromium 

Coban 

Copper 

Ethylbenzene 

Iron 

Lead 

Lithium 

Magnesium 

Manganese 

Mercury 

Molybdenum 

Nickel 

Niobium 


Potassium 

Ruthenium 

Silicon 

Silver 

Sodium 

Strontium 

Tantalum 

Thallium 

Thorium 

Tin 

litanium 

Toluene 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

so296 

so296 

SO296 

SO296 

SO296 

so296 

SO296 

SO296 

75-34-3 

75-35-4 

7429-90-5 

7440-36-0 

7440-38-2 

7440-39-3 

71 -43-2 

7440-41-7 

7440-69-9 

7440-43-9 

7440-70-2 

7440-47-3 

7440-48-4 

7440-50-8 

100-41-4 

7439-89-6 

7439-92-1 

7439-93-2 

7439-954 

7439-96-5 

7439-97-6 

7439 - 98 - 7 

7440-02-0 

7440-03-1 

7723-14-0 

7440-09-7 

7440-18-8 

7440-21-3 

7440-22-4 

7440-23-5 

7440-24-6 

7440-25-7 

7440-28-0 

7440-29-1 

7440-31 -5 

7440-32-6 

108-88-3 

3101-94 

369-95 

417-94 

433-95 

453-94 

470-95 

497-95 

510-94 

543-95 

564-95 

612-94 

629-95 

630-93 

632-93 

651-93 

661-93 

666-95 

694-94 

711-95 

728-93 

743-95 

746-94 

783-95 

798-93 

813-95 

845-93 

855-93 

884-95 

897-94 

919-95 

935-93 

936-94 

952-95 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

22DEC1994 

24FEB1995 

18FEBl994 

03MAR 1995 

25FEB1994 

10MAR1995 

17MAR1995 

03MAR1994 

23MAR1995 

28MAR1995 

17MAR1994 

05APR1995 

05MAY1993 

OBMAYI 993 

06MAY 1 993 

1 1 MAY 1993 

13APR1995 

25MAR1994 

21APR1995 

2lMAY1993 

26APR1995 

31MAR1994 

03MAY 1995 

O2JUNl 993 

11MAYl995 

lOJUN1993 

14JUN1993 

17MAYI 995 

08APRl994 

25MAY 1995 

23JUN1993 

13APRl994 

01JUNl995 

05NOV1992 

05NOVl992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

O5NOVl 992 

05NOV1992 

05NOV1992 

O5NOVl 992 

05NOVI992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOVI992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOVI992 

05NOV1992 

O5NOVl 992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOVl992 

Page 115 of 176 

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WL 

WL 

WL 

WL 

WL 

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WL 

WL 

\I\h 

WL 

VK 

WL 

WL 

WL 

WL 

WL 

VK 

VK 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

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3.00€+00 

3.00€+00 

3.00€+00 

3.OOE+00 

3.00E+00 

3.00€+00 

3.00€+00 

3.00€+00 

0.00E+00 

2.00E+00 

3.00€+00 

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J.OOE+OO 

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3.00€+00 

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Q 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

ug1L 

ug1L 

mglL 

mg/L 

mglL 

mglL 

uglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

uglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgk 

mglL 

wfl 

mgk 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

uglL




Trans-I .2-Dichloroethene 156-60-5 1960-92 05NOV1992 WS 6.00E+00 N uglL 


Tungsten 

Uranium 

Vanadium 

Xylene 

Zinc 

Zirconium 

PH 

WAG 7. SWU 8. C746K-GA3 









Acetone 

Acetone 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Antimony 

Antimony 

Antimony 

Antimony 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

79-01-6 

7440-33-7 

7440-61 -1 

7440-62-2 

1330-20-7 

7440-66-6 

7440-67-7 

SO296 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

67-64-1 

67-64-1 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1960-92 

1977-92 

1961-92 

2092-92 

2209-92 

784-95 

1961 -92 

2092-92 

2209-92 

784-95 

1442-93 

1704-93 

1201-94 

1518-93 

1552-93 

17-95 

1842-93 

1961-92 

2092-92 

2157-93 

22-94 

2058 - 94 

292-94 

434-95 

511-94 

532-93 

630-95 

631-93 

784-95 

799-93 

89594 

1961-92 

2092-92 

532-93 

631-93 

1201-94 

1518-93 

1552-93 

17-95 

1842-93 

1961-92 

2092-92 

2157-93 

22-94 

2858-94 

292-94 

434-95 

511-94 

532-93 

630-95 

631 -93 

784-95 

799-93 

898-94 

1201-94 

1518-93 

1552-93 

17-95 

1842-93 

1961-92 

2092-92 

2157-93 

22-94 

285594 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

05NOV1992 

09NOV1992 

05NOV1992 

30NOV1992 

16DEC1992 

03MAY 1995 

05NOV1992 

30NOVf992 

16DEC1992 

O3MAY 1995 

15SEP1993 

220CT1993 

OSMAYl994 

28SEP1993 

050CT1993 

O5JANl995 

04NOV1993 

05NOV1992 

3ONOV1992 

10DEC1993 

05JAN1994 

02DEC1994 

04FEB1994 

03MAR1995 

03MAR1994 

19APR1993 

05APR1995 

(HMAY 1993 

03MAY 1995 

02 JUN 1993 

08APR1994 

05NOV1992 

30NOV1992 

19APR1993 

05MAY 1993 

05MAY 1994 

28SEPl993 

050CT1993 

05JAN1995 

04NOVl993 

05NOV1992 

3ONOV1992 

10DEC1993 

05JANl994 

02DEC1994 

04FEB1994 

03MARl995 

03MARl994 

19APR1993 

05APR1995 

OsMAY1993 

03MAYl995 

02JUN1993 

08APR1994 

OMY 1994 

28SEP1993 

050CT1993 

05JAN1995 

04NOV1993 

05NOV1992 

30NOV1992 

10DEC1993 

mAN1994 

O2DEC1 994 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

ws 

VK 

VK 

VK 

VK 

VK 

VK 

WL 

VK 

VK 

VK 

VK 

VK 

VK 

WL 

WL 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

WL 

WL 

VK 

WL 

WL 

WL 

WL 

\IK 

VK 

VK 

WL 

WL 

VK 

WL 

WL 

WL 

VK 

VK 

VK 

WL 

VK 

VK 

WL 

VK 

VK 

WL 

VK 

VK 

VK 

WL 

WL 

VK 

WL 

WL 

VK 

VK 

VK 

VK 

WL 

VK 

< N 

< N 

c 

N 

N 

c 

N 

N 

N 

N 

c 

c 

c 

c 

c 

c 

X 

< 

CS 

< 

< 

< 

cSJ+ 

< 




Barium 7440-39-3 292-94 04FEB1994 WL O.OOE+OO N 

mglL 

Barium 

Barium 

Barium 

7440-39-3 

7440-39-3 

7440-39-3 

434-95 

511-94 

532-93 

03MAR1995 

03MAR1994 

19APR1993 

WL 

WL 

WL 

< N 

N 

N 

mglL 

mglL 

mglL 

Barium 

7440-39-3 

630-95 05APR1995 WL 

< N 

mglL 

Barium 

7440-39-3 

631-93 O5MAY 1993 WL 

< 

N 

mglL 

Barium 

7440-39-3 

784-95 O3MAY 1995 WL 

< N 

mglL 

Barium 

Barium 

7440-39-3 

7440-39-3 

799-93 

898-94 

02JUN1993 

O8APR 1994 

WL 

WL 

< N 

N 

mglL 

mglL 

Benzene 

71 -43-2 

1961 -92 05NOV1992 WL 

< N 

uglL 

Benzene 

Benzene 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Bismuth 

Bismuth 

Bismuth 

Bismuth 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Calcium 

Calcium 

Calcium 

Calcium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

71 -43-2 

71-43-2 

74404 -7 

7440-47 -7 

7440-41-7 

7440-41-7 

7440-69-9 

7440-69-9 

7440-69-9 

7440 - 69 - 9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

2092-92 

2209-92 

1961-92 

2092-92 

532-93 

631 -93 

1961 -92 

2092-92 

532-93 

631-93 

1201-94 

1518-93 

1552-93 

17-95 

1842-93 

1961-92 

2092-92 

2157-93 

22-94 

2858-94 

292-94 

434-95 

511-94 

532-93 

630-95 

631-93 

784-95 

799-93 

898-94 

953-95 

1961-92 

2092-92 

532-93 

631 -93 

1201-94 

1518-93 

1552-93 

17-95 

1842-93 

1961 -92 

2092-92 

2157-93 

22-94 

2858-94 

292-94 

434-95 

511-94 

532-93 

630-95 

631 -93 

784-95 

799-93 

89894 

953-95 

3ONOV1992 

16DECl992 

05NOV1992 

30NOV1992 

19APR1993 

05MAY 1993 

05NOV1992 

30NOV1992 

19APR1993 

05MAYl993 

05MAY1994 

28SEP1993 

05OCT1993 

%JAN1995 

04NOV1993 

05NOV1992 

30NOV1992 

lODEC1993 

05JAN1994 

02DEC1994 

04FEB1994 

03MAR1995 

03MAR1994 

19APR1993 

OSAPR1995 

(HMAY 1993 

03MAY 1995 

O2JUNl 993 

08APR1994 

01 JUN1995 

05NOV1992 

30NOV1992 

19APR1993 

05MAY1993 

05MAY 1994 

28SEP1993 

OSOCTl993 

05JANl995 

04NOVl993 

05NOV1992 

30NOV1992 

10DECl993 

05JAN1994 

02DEC1994 

04FEB1994 

03MAR1995 

03MAR1994 

19APR1993 

O5APR1995 

(HMAY 1993 

03MAY1995 

OZJUN1993 

08APR1994 

01 JUN1995 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

\M. 

WL 

WL 

WL 

WL 

WL 

WL 

< 

< 

< 

< 

< 

< 

< 

< 

< 

c 

< 

< 

UD 

< 

UD 

< 

< 

< 

< 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

uglL 

uglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mg1L 

mglL 

mglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

mg/L 

mglL 

mg1L 

Wfl 

mgfl 

mglL 

mg/L 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

W/L 

mglL 

mglL 

mglL 

mglL 

mglL 

Wfl 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

Coban 

7440-48-4 

1961-92 05NOVl992 WL 

N 

mgn 

Coban 

7440-48-4 

2092-92 3ONOV1992 WL 

N man 

Cobalt 

Cobalt 

Copper 

Copper 

Copper 

Copper 

7440-48-4 

7440-48-4 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

532-93 

631 -93 

1961 -92 

2092-92 

532-93 

631-93 

19APR1993 

OSMAY 1993 

05NOVl992 

3ONOV1992 

19APRI 993 

(HMAY 1993 

WL 

WL 

WL 

WL 

WL 

WL 

N 

N 

N 

N 

N 

N 

mglL 

mg/L 

mgfl 

mgfl 

Wfl 

mgfl 

Page 117 of 176




Estimated Flow EST FLOW 1005-93 OlJUL1993 WL 3.3OE+Ol N GaVDay 

































































Estimated Fbw 







EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

1005-95 

1026-93 

104-95 

1046-95 

1066-94 

1074-95 

1137-95 

1144-95 

1201-94 

1220-95 

1252-94 

1290-94 

1347-94 

141-95 

1442-93 

1518-93 

1552-93 

1562-94 

1611-94 

1637-93 

1654-94 

17-95 

1704-93 

1714-94 

177-95 

177893 

1787-94 

1834-94 

1842-93 

1896-93 

1917-94 

I 96894 

2004-93 

2023-94 

2095-93 

2108-94 

2120-94 

2157-93 

217-95 

2191-93 

22-94 

2201-94 

2221-93 

2249-94 

226893 

2333-94 

2410-94 

2477-94 

2480-94 

256-95 

2616-94 

2688-94 

2732-94 

2769-94 

2839-94 

2858-94 

2919-94 

292-94 

2988-94 

3006-94 

302-95 

3088-94 

3102-94 

370-95 

41894 

434-95 

454-94 

471-95 

49895 

511-94 

544-95 

08JUN1995 

09JUL1993 

13JAN1995 

13JUN1995 

22APR1994 

20JUN1995 

26JUN1995 

06JUL1995 

O5MAY1994 

I1 JUL1995 

13MAY 1994 

19MAY 1994 

27MAY 1994 

20JAN1995 

15SEP1993 

28SEP1993 

05OCT1993 

24JUN1994 

OlJULl994 

I 5OCT1993 

OBJUL1994 

05JAN 1995 

220CT1993 

15JUL1994 

26JAN1995 

280CT1993 

22JUL1994 

29JUL1994 

04NOVl993 

12NOV1993 

O5AUG1994 

12AUG1994 

24NOV1993 

19AUGl994 

05DEC1993 

26AUG1994 

02SEPl994 

10DEC1993 

03FEB1995 

15DEC1993 

WAN1994 

O9SEPl 994 

22DEC1993 

16SEP1994 

30DECl993 

30SEPl994 

070CT1994 

140CT1994 

190CT1994 

08FEBl995 

280CT1994 

04NOVl994 

IlNOVI994 

17NOVI 994 

23NOV1994 

02DECl994 

08DECI994 

04FEB1994 

14DEC 1994 

23SEP1994 

17FEB1995 

27DEC1994 

22DECl994 

24FEBl995 

18FEB1994 

OW1995 

25FEB1994 

loMAR1995 

17MAR1995 

OW1994 

23MAR1995 

Page 118 of 176 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

J 

Q 

Q 

Q 

Q 

Q 

Q 

Q 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

FIELD 

FIELD 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

FIELD 

N 

FIELD 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

FIELD 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaUDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

Gamy 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

Gamy 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

Gamy 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

Gamy 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

Gamy 

GaVDay 

GaVDay 

Gamy 

GaVDay 

Gamy 

GaVDay 

GaVDay 

GaVDay 

Gamy 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

Gamy 

Gamy




Estimated Flow EST FLOW 565-95 28MAR1995 WL 2.90E+01 N GaVDay 












Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

GCNS Scan 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

EST FLOW 

100-41-4 

10041-4 

100-41-4 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCMS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

GCNS SCAN 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439 - 89 - 6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

613-94 

630-95 

667-95 

712-95 

744-95 

747-94 

784-95 

814-95 

885-95 

920-95 

953-95 

1961 -92 

2092-92 

2209-92 

1005-95 

1050-95 

1144-95 

1220-95 

1518-93 

1552-93 

17-95 

2480-94 

2769-94 

2858-94 

2988-94 

434-95 

498-95 

630-95 

712-95 

784-95 

885-95 

953-95 

1201-94 

1518-93 

1552-93 

17-95 

1842-93 

1961-92 

2092-92 

2157-93 

22-94 

2858-94 

292-94 

434-95 

511-94 

532-93 

630-95 

631-93 

784-95 

799-93 

898-94 

110-94 

1201-94 

1518-93 

1552-93 

17-95 

1842-93 

1961-92 

2092-92 

2157-93 

22-94 

2858-94 

292-94 

434-95 

511-94 

532-93 

630-95 

631-93 

784-95 

799-93 

898-94 

17MAR1994 

05APR1995 

13APR1995 

2lAPRl995 

26APR1995 

31MAR1994 

O3MAY 1995 

1 1 MAY 1995 

17MAY 1 995 

25MAYl995 

01JUN1995 

05NOV1992 

30NOV1992 

16DECl992 

08JUN1995 

14JUN1995 

06JULl995 

llJUL1995 

28SEP1993 

050CT1993 

OSJANI 995 

190CT1994 

17NOV1994 

02DECl994 

14DECl994 

O3MAR 1995 

17MARl995 

05APRl995 

21 APRI 995 

03MAY 1995 

17MAY1995 

01 JUN1995 

05MAY1994 

28SEPl993 

050CT1993 

05JAN1995 

04NOVI993 

OSNOV1992 

3ONOV1992 

IODEC1993 

05JAN1994 

02DEC1994 

04FEB1994 

03MAR1995 

03MAR1994 

1 9APRI 993 

05APRl995 

05MAYl993 

03MAY 1995 

02JUN1993 

08APRl994 

12JAN1994 

05MAYI994 

28SEPl993 

050CT1993 

O5JANl995 

04NOV1993 

05NOV1992 

30NOV1992 

1ODECI 993 

05JAN1994 

02DECl994 

MFEBI 994 

03MARl995 

03MAR1994 

19APR1993 

05APRl995 

05MAY 1993 

03MAYl995 

02JUNl993 

08APRl994 

Page 119 of 176 

1.32E+02 

2.10E+01 

2.40E+01 

2.30E+02 

9.50E+01 

8.20E+01 

1.23E+02 

6.30E+01 

1.02E+02 

2.90E+01 


5.00E+00 

5.00E+00 

5.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

3.05E+02 

3.90E+OI 

I.WE+Ol 


5.WE+Ol 

8.10E+01 

9.20E+01 

I .49E+02 

I.OlE+OZ 

2.00E+W 

1.04E+02 

I .48E+02 

I .31E+O2 


1.39E+02 

2.76E+02 

1.59E+02 

3.98E+02 

1.42E+02 

O.WE+OO 

5.00E+W 


3.00E+00 

O.OOE+W 

O.OOE+OO 

O.WE+OO 

O.WE+OO 

O.WE+OO 

5.00E+00 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+W 

O.OOE+OO 

O.OOE+OO 

O.OOE+W 

O.OOE+OO 

9.00E+W 

O.WE+W 

c 

c 

< 

V 

X 

X 

X 

V 

V 

X 

V 

V 

V 

X 

X 

X 

X 

X 

X 

X 

X 

B 

< 

< 

< 

U 

< 

< 

c 

< 

U 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Q 

Q 

Q 

Q 

N 

N 

N 

N 

N 

N 

N 

Q 

Q 

Q 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

GaVDay 

ug1L 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ugfl 

ugfl 

uglL 

uglL 

uglL 

wlL 

mgk 

WlL 

WlL 

mgk 

wfl 

wlL 

mgk 

mglL 

mglL 

mglL 

mgk 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

wk 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

wfl 

mglL 

mgfl 

mgfl 

mgfl 

wfl 

mglL 

mgfl 

wfl 

mg/L 

wfl




Lead 

7439-92-1 953-95 01JUN1995 WL O.OOE+OO N mglL 

Lithium 

Lithium 

Lithium 

Lithium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

7439-93-2 

7439-93-2 

7439-93-2 

7439-93-2 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-965 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

1961-92 

2092-92 

532-93 

631-93 

1201-94 

1518-93 

1552-93 

17-95 

1842-93 

1961 -92 

2092-92 

2157-93 

22-94 

2858-94 

292-94 

434-95 

511-94 

532-93 

630-95 

631-93 

784-95 

799-93 

898-94 

1201-94 

1518-93 

1552-93 

17-95 

1842-93 

1961-92 

2092-92 

2157-93 

22-94 

2858-94 

292-94 

434-95 

511-94 

532-93 

630-95 

631 -93 

784-95 

799-93 

898-94 

1552-93 

1961-92 

2092-92 

532-93 

631 -93 

1961-92 

2092-92 

532-93 

631-93 

05NOV1992 

30NOV1992 

19APRl993 

O5MAY 1993 

05MAYl994 

28SEP1993 

050CT1993 

O5JANl995 

04NOV1993 

05NOV1992 

3ONOV1992 

10DEC1993 

05JAN1994 

02DEC1994 

04FE81994 

03MAR1995 

03MAR1994 

19APR1993 

05APRl995 

05MAY1993 

03MAY 1995 

02JUNl993 

08APR1994 

05MAY1994 

28SEP1993 

050CT1993 

WAN1995 

04NOV1993 

05NOV1992 

30NOV1992 

I ODECl993 

WAN1994 

02DEC1994 

MFEB1994 

03MAR1995 

03MARl994 

19APR 1993 

05APR1995 

05MAY I 993 

03MAY 1995 

O2JUNI 993 

08APRl 994 

050CTl993 

05NOVl992 

3ONOV1992 

19APR1993 

05MAY 1993 

05NOV1992 

30NOV1992 

19APR1993 

osMAY1993 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

8.10E+01 



6.70E+01 

3.20E+01 

5.00E+01 

7.60E+01 

7.00E+01 

7.40E+01 


7.40E+01 

9.00E+01 

7.70E+01 

9.10E+01 

7.80E+01 

6.60E+01 

7.50E+01 

1.40E+02 


1.69E+02 

5.90E+01 

5.70E+01 

8.70E+01 


6.80E+Ol 

1.1 IE+OZ 

9.20E+01 

9.80E+01 


9.60E+01 

9.3OE+01 

1.03E+02 

1.31 E+02 

9.60E+01 

8.70E+01 

8.1OE+Ol 

1.87E+02 


O.WE+OO 

O.WE+W 

O.WE+W 

O.OOE+W 

O.WE+OO 

O.WE+OO 

O.OOE+OO 

O.WE+W 

O.WE+W 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

Nickel 

7440-02-0 

1201-94 W Y 1994 1 .WE+00 

N 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Niobium 

Niobium 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-03-1 

7440-03-1 

1518-93 

1552-93 

17-95 

1842-93 

1961-92 

2092-92 

2157-93 

22-94 

2858-94 

292-94 

434-95 

511-94 

532-93 

631-93 

784-95 

799-93 

898-94 

1961-92 

2092-92 

28SEP1993 

050CT1993 

WAN1995 

MNOV1993 

05NOV1992 

3ONOV1992 

lODECl993 

WAN1994 

02DEC1994 

MFEB1994 

03MARl995 

03MARl994 

19APR1993 

05MAY 1993 

03MAY 1995 

02JUNl993 

08APR1994 

05NOV1992 

30NOV1992 

O.WE+W 

O.WE+OO 

O.WE+W 

O.OOE+W 

O.OOE+OO 

O.WE+W 

O.WE+W 

O.WE+W 

O.WE+W 

O.WE+W 

O.WE+W 

O.WE+W 

1 .WE+00 

O.WE+W 

O.WE+W 

1 .WE+00 

O.OOE+W 

O.OOE+W 

O.WE+W 

J 

< 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Page 120 of 176




Niobium 7440-03-1 532-93 19APR1993 WL O.OOE+OO < N mg1L 

Niobium 

PCB 





Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Alpha 

Rad Beta 

Rad Beta 

Rad Beta 

Rad Beta 

Rad Beta 

Rad Beta 

Ruthenium 

Ruthenium 

Ruthenium 

Ruthenium 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silicon 

Silver 

Silver 

Silver 

Silver 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

7440-03-1 

1336-36-3 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

12587-46-1 

12587-46-1 

12587-461 

12587-46-1 

12587-46-1 

12587-46-1 

1258747-2 

12587-47-2 

12587-47-2 

12587-47-2 

12587-47-2 

1258747-2 

7440-18-8 

7440-18-8 

7440-18-8 

7440-18-8 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21 -3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-21-3 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

631-93 

2133-92 

1961 -92 

2092-92 

532-93 

631-93 

1201-94 

I 518-93 

1552-93 

17-95 

1842-93 

1961 -92 

2092-92 

2157-93 

22-94 

2858-94 

292-94 

434-95 

511-94 

532-93 

630-95 

631-93 

784-95 

799-93 

898-94 

1144-95 

434-95 

630-95 

784-95 

799-93 

953-95 

1144-95 

434-95 

630-95 

784-95 

799-93 

953-95 

1961-92 

2092-92 

532-93 

631-93 

1201-94 

1518-93 

1552-93 

17-95 

1842-93 

1961-92 

2092-92 

2157-93 

22-94 

2858-94 

292-94 

434-95 

511-94 

532-93 

630-95 

631-93 

784-95 

799-93 

898-94 

1961-92 

2092-92 

532-93 

631-93 

1201-94 

1518-93 

1552-93 

17-95 

1842-93 

1961-92 

2092-92 

05MAY 1993 

07DEC1992 

05NOVI 992 

30NOV1992 

19APR 1993 

05MAY1993 

O5MAY 1994 

28SEP1993 

05OCTl 993 

05JAN1995 

04NOV1993 

05NOV1992 

30NOV1992 

10DEC1993 

05JAN1994 

02DEC1994 

04FEBl994 

03MARl995 

03MARl994 

19APR1993 

05APR1995 

O5MAY 1993 

03MAY 1995 

02JUN1993 

08APR1994 

06JUL1995 

03MAR1995 

05APRI995 

03MAY1995 

O2JUNl 993 

01 JUNl995 

06JULl995 

O3MARl 995 

05APR1995 

03MAY 1995 

02JUN1993 

01JUN1995 

05NOV1992 

3ONOV1992 

19APR1993 

05MAY1993 

(HMAY 1994 

28SEPl993 

050CTl993 

05JANl995 

04NOV1993 

05NOV1992 

JONOVI992 

IODECI 993 

05JAN1994 

02DECl994 

04FEB1994 

03MAR1995 

03MAR 1994 

19APR1993 

05APRl995 

OSMAY 1993 

03MAY I995 

02JUN1993 

08APR1994 

05NOV1992 

3ONOV1992 

19APRl993 

(HMAY 1993 

(HMAY 1994 

28SEP1993 

050CT1993 

05JANl995 

04NOV1993 

05NOV1992 

30NOV1992 

Page 121 of 176 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

VK 

WL 

WL 

VK 

< N 

< N 

N 

N 

NT 

< NT 

N 

N 

N 

< 

J 

4 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

X 

J 

J 

B 

J 

J 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N




Sodium 7440-23-5 2157-93 10DEC1993 WL 3.40E+01 N mglL 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Strontium 

Tantalum 

Tantalum 

Tantalum 

Thallium 

Thallium 

Thallium 

Thallium 

Thorium 

Thorium 

Thorium 

Thorium 

Tin 

Tin 

Tin 

Tin 

Titanium 

Titanium 

Titanium 

Titanium 

Toluene 

To I u e n e 

Toluene 

















Trichkroethene 



7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

7440-25-7 

7440-25-7 

7440-25-7 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-29-1 

7440-29-1 

7440-29-1 

7440-29-1 

7440-31-5 

7440-31-5 

7440-31-5 

7440-31-5 

7440-32-6 

7440-32-6 

7440-32-6 

7440-32-6 

108-88-3 

loa-88-3 

I 08-88-3 

156-60-5 

156-60-5 

156-60-5 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

22-94 

2858-94 

292-94 

434-95 

511-94 

532-93 

630-95 

631-93 

784-95 

799-93 

898-94 

1201 -94 

1518-93 

1552-93 

17-95 

1842-93 

1961-92 

2092-92 

2157-93 

22-94 

2858-94 

292-94 

434-95 

511-94 

532-93 

630-95 

631 -93 

784-95 

799-93 

898-94 

1961-92 

532-93 

631-93 

1961-92 

2092-92 

532-93 

631-93 

1961 -92 

2092-92 

532-93 

631 -93 

1961-92 

2092-92 

532-93 

631-93 

1961-92 

2092-92 

532-93 

631-93 

1961-92 

2092-92 

2209-92 

1961-92 

2092-92 

2209-92 

1050-95 

1066-94 

1144-95 

1201-94 

1704-93 

1842-93 

1961-92 

2092-92 

2157-93 

22-94 

2209-92 

2268-93 

242-94 

292-94 

418-94 

434-95 

OSJANI 994 

02DECl994 

04FEBI 994 

O3MARl 995 

03MAR1994 

19APR1993 

DSAPR 1995 

05MAY1993 

03MAY 1995 

02JUN1993 

08APR1994 

OSMAY 1994 

28SEP1993 

050CT1993 

OSJANl995 

04NOV1993 

05NOV1992 

30NOV1992 

10DECl993 

OSJANI994 

02DEC1994 

04FEB1994 

03MARl995 

03MAR1994 

19APRl993 

05APR 1995 

OSMAY 1993 

03MAY 19% 

02JUN1993 

08APR1994 

05NOV1992 

19APR1993 

WAY1993 

05NOV1992 

3ONOVI 992 

19APR 1993 

WAY 1993 

05NOVI992 

30NOV1992 

19APRl993 

OSMAY1993 

05NOV1992 

30NOV1992 

19APRl993 

WAY1993 

OSNOV1992 

30NOV1992 

19APR1993 

05MAY1993 

05NOV1992 

3ONOVl992 

16DECl992 

OSNOV1992 

3ONOV1992 

16DECl992 

14JUN1995 

22APR1994 

06JULl995 

05MAY 1994 

220CT1993 

04NOV1993 

05NOV1992 

3ONOV1992 

lODECl993 

05JAN1994 

16DEC1992 

3ODECl993 

21 JAN1 994 

04FEB1994 

18FEB1994 

03MARl995 

Page 122 of 176 

WL 

VK 

WL 

WL 

WL 

WL 

VK 

WL 

WL 

WL 

VK 

WL 

WL 

WL 

WL 

VK 

VK 

VK 

WL 

VK 

VK 

VK 

VK 

WL 

VK 

WL 

VK 

WL 

VK 

WL 

VK 

VK 

WL 

VK 

WL 

WL 

WL 

WL 

WL 

VK 

WL 

VK 

VK 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

WL 

\IK 

WL 

WL 

WL 

VK 

WL 

VK 

WL 

VK 

VK 

WL 

WL 

WL 

WL 

WL 

WL 

VK 

WL 

WL 

WL 

B 

J 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

< 

c 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

WlL 

mglL 

mglL 

wlL 

mglL 

mgt 

mglL 

mglL 

mglL 

mglL 

mg/L 

wlL 

wlL 

mglL 

mglL 

w5 

mglL 

WlL 

wlL 

mglL 

mglL 

mg1L 

mglL 

wlL 

WlL 

mglL 

mg/L 

mglL 

mglL 

mg1L 

wlL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgIL 

mg/L 

mglL 

mglL 

WlL 

uglL 

w3R 

ugfl 

uglL 

uglL 

ug1L 

ug5 

uglL 

wfl 

uglL 

uglL 

Wfl 

uglL 

ugfl 

ug5 

uglL 

ug1L 

uglL 

w5 

uglL 

UgR 

w35

~~ 




Trichloroethene 79-01-6 511-94 03MAR1994 VK l.OOE+OO N uglL 








Tungsten 

Tungsten 

Tungsten 

Tungsten 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

7440-33-7 

7440-33-7 

7440-33-7 

7440-33-7 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

613-94 

630-95 

712-95 

784-95 

885-95 

898-94 

953-95 

1961-92 

2092-92 

532-93 

631 -93 

1201-94 

1552-93 

17-95 

1704-93 

1842-93 

1961-92 

2092-92 

17MAR1994 

O5APRl 995 

21APR1995 

03MAYl995 

17MAYl995 

08APR1994 

01JUN1995 

05NOVl992 

30NOV1992 

19APR1993 

05MAY 1993 

05MAY 1994 

050CT1993 

05JAN1995 

220CT1993 

04NOV1993 

05NOV1992 

3ONOV1992 

< 

< 

< 

< 

< 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

UglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

Uranium 

Uranium 

7440-61-1 

7440-61 -1 

2133-92 

2157-93 

07DEC1992 

lODEC1993 

N 

N 

w/L 

mglL 

Uranium 

7440-61 -1 

22-94 OSJAN1994 

N 

mglL 

Uranium 

7440-61-1 

2858-94 02DECl994 

N 

mglL 

Uranium 

7440-61 - 1 

292-94 04FEB1994 

N 

mglL 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Xylene 

Xylene 

Xylene 

Zinc 

Zinc 

Zinc 

Zinc 

Zirconium 

Zirconium 

Zirconium 

Zirconium 




cis-l,2dichloroethene 


cis-l,2-dichloroethene 






cis-1.2-dichloroeihene 





cis-l,2-dichloroethene 






7440-61-1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

1330-20-7 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-67-7 

7440-67-7 

7440-67-7 

7440-67-7 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

15659-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

156-59-2 

434-95 

511-94 

532-93 

630-95 

631-93 

784-95 

898-94 

953-95 

1961-92 

2092-92 

532-93 

631-93 

1961-92 

2092-92 

2209-92 

1961-92 

2092-92 

532-93 

631-93 

1961-92 

2092-92 

532-93 

631 -93 

1050-95 

1066-94 

1144-95 

1201-94 

1220-95 

1290-94 

1704-93 

1842-93 

2157-93 

22-94 

2268-93 

242-94 

292-94 

418-94 

434-95 

511-94 

613-94 

630-95 

712-95 

784-95 

885-95 

898-94 

03MARl995 

03MAR1994 

19APR1993 

05APR1995 

05MAYl993 

03MAY1995 

08APR1994 

01 JUN1995 

05NOVI992 

30NOV1992 

19APR1993 

05MAY 1993 

05NOV1992 

30NOV1992 

16DEC1992 

05NOV1992 

3ONOV1992 

19APRl993 

05MAY1993 

05NOV1992 

30NOV1992 

19APR1993 

05MAY1993 

1 AIUN1995 

22APR1994 

06JUL1995 

05MAY 1994 

11 JULl995 

19MAY 1994 

220CT1993 

04NOVl993 

lODECl993 

05JAN1994 

3ODEC1993 

21 JAN1 994 

04FEB1994 

18FEB1994 

03MARl995 

03MAR1994 

17MAR1994 

OSAPR1995 

21 APRl995 

03MAY 1995 

17MAY 1995 

08APRl994 

< 

< 

< 

< 

< 

< 

< 

< 

Q 

Q 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mg1L 

mglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

mglL 

mglL 

mg5 

ug1L 

uglL 

uglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ugfl 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ugfl 

ug1L 

ugfl 

ugfl 

uglL 

uglL 

ugfl 

uglL 

cis-1.2dichloroethene 156-59-2 

953-95 OlJUNl995 

N 

uglL 

PH 

so296 

1005-93 OlJULl993 

N su 

PH 

SO296 

1005-95 08JUN1995 

su 

Page 123 of 176



ANALYTE CAS NUMBER SAMPLE ID DAE TYPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

DH SO296 1026-93 09JUL1993 WL 3.00E+00 N su 

SO296 

104-95 13JANl995 

su 

so296 

1046-95 13JUN1995 

su 

SO296 

1066-94 22APR1994 

su 

SO296 

1074-95 20JUN1995 

su 

SO296 

1137-95 

26JUN1995 

su 

SO296 

1144-95 06JUL1995 

su 

SO296 

1201 -94 05MAY 1994 

su 

SO296 

1220-95 llJUL1995 

su 

SO296 

1252-94 13MAY 1994 

su 

SO296 

1290-94 19MAY 1994 

su 

so296 

1347-94 27MAY 1994 

su 

SO296 

141-95 2OJANl995 

Q 

N su 

SO296 

1442-93 15SEP1993 

N su 

SO296 

1518-93 

28SEP1993 

su 

SO296 

1552-93 050CT1993 

su 

SO296 

1562-94 24JUNI 994 

Q FIELD su 

SO296 

1611-94 01 JULl994 

Q FIELD su 

SO296 

1637-93 150CTl993 

su 

SO296 

1654-94 08JUL1994 

Q 

su 

so296 

17-95 OBJANl995 

su 

SO296 

1704-93 220CT1993 

su 

so296 

1714-94 15JUL1994 

Q 

su 

SO296 

177-95 26JAN1995 

su 

so296 

1778-93 280CT1993 

su 

SO296 

1787-94 22JULl994 

Q 

su 

SO296 

1834-94 29JULl994 

Q 

su 

SO296 

f842-93 04NOW993 

su 

so296 

1896-93 12NOV1993 

su 

SO296 

1917-94 05AUG1994 

Q 

su 

so296 

1968-94 12AUGl994 

Q 

su 

SO296 

1978-92 09NOV1992 

N su 

SO296 

200493 24NOV1993 

su 

SO296 

2023-94 19AUG1994 

Q 

su 

SO296 

2092-92 30NOV1992 

N su 

so296 

2095-93 OSDEC1993 

su 

so296 

2108-94 

26AUG1994 

Q 

su 

so296 

2133-92 07DEC1992 

N su 

so296 

2157-93 10DEC1993 

su 

so296 

217-95 03FEB1995 

Q 

N su 

so296 

2188-92 14DECl992 

N su 

so296 

2191 -93 15DEC1993 

su 

so296 

22-94 05JAN1994 

su 

so296 

2201-94 09SEPl994 

Q 

su 

so296 

2221-93 22DEC1993 

J 

su 

so296 

2222-92 21DECl992 

N su 

so296 

2239-92 28DEC1992 

N su 

so296 

2249-94 16SEPl994 

Q FIELD su 

so296 

2268-93 30DECl993 

su 

SO296 

2333-94 3OSEPl994 

Q FIELD su 

so296 

2410-94 070CT1994 

Q 

N su 

so296 

242-94 21JAN1994 

su 

SO296 

2477-94 140CT1994 

Q 

N su 

SO296 

2480-94 190CTl994 

su 

so296 

256-95 08FEBl995 

su 

so296 

2616-94 280CT1994 

Q 

N su 

SO296 

262-94 28JAN1994 

su 

so296 

2688-94 04NOV1994 

Q 

N su 

so296 

2732-94 11 NOVI 994 

su 

so296 

2769-94 17NOV1994 

su 

so296 

2839-94 23NOV1994 

su 

so296 

2858-94 02DEC1994 

su 

so296 

2919-94 08DECl994 

su 

SO296 

292-94 04FEB1994 

su 

so296 

2988-94 14DEC1994 

su 

SO296 

3006-94 23SEPl994 

Q FIELD su 

so296 

302-95 17FEBl995 

Q 

N su 

so296 

3088-94 27DECl994 

su 

SO296 

3102-94 22DECl994 

su 

so296 

370-95 24FEBl995 

su 

so296 

418-94 18FEBl994 

su 

so296 

434-95 OJMAR1995 

su 

Page 124 of 176




DH SO296 454-94 25FEB1994 WL 3.00E+00 su 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

WAG 7, SVMU 8, H216 

1 ,I,I-Trichloroelhane 

1 .I.I-Trichloroethane 

1 ,I.I-Trichloroethane 

1 .l.l-Trichloroethane 

1 ,I,I-Trichloroelhane 

1 .I,l-Trichloroethane 

1.1 .I-Trichloroethane 

I,l,l-Trichloroethane 


1 .I.2,2-TetrachloroeIhane 

1 ,I.2.2-TeIrachloroelhane 

1 ,I,2,2-Tetrachloroelhane 

l11,2,2-Tetrachloroethane 

1 .I.2.2-Tetrachloroethane 

1 .I,2.2-TetrachloroeIhane 

1 ,I.2,2-Tetrachloroethane 

1 ,I.2.2-Telrachloroethane 

1 .I,2.2-Telrachloroethane 

1 ,I.2-Trichloroelhane 


I .I,2-Trichloroethane 

I .1.2-Trichloroethane 

1 .I,2-Trichloroelhane 

1.1.2-Trichloroelhane 

I .I.2-Trichloroethane 

1 ,I.2-Trichloroethane 



I .I-Dichloroethane 

1 ,I-Dichloroelhane 

1 .I-Dichloroelhane 

I ,l-Dichloroelhane 

1 .I-Dichloroelhane 



I ,I-Dichloroethane 



1 ,l-Dichloroelhene 


1,l-Dichloroelhene 


SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

so296 

71 -55-6 

71-55-6 

71-55-6 

71 -55-6 

71-55-6 

71-55-6 

71-55-6 

71-55-6 

71-55-6 

79-34-5 

79-34-5 

79-34-5 

79-34-5 

79-34-5 

79-34-5 

79-34-5 

79-34-5 

79-34-5 

79-00-5 

79-00-5 

79-00-5 

79-00-5 

79-00-5 

79-00-5 

7 9 - 0 0 - 5 

79-00-5 

79-00-5 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

471-95 

498-95 

51 1-94 

544-95 

565-95 

613-94 

630-95 

631-93 

633-93 

652-93 

662-93 

667-95 

695-94 

71 2-95 

729-93 

744-95 

747-94 

784-95 

799-93 

814-95 

846-93 

856-93 

885-95 

898-94 

920-95 

936-93 

937-94 

953-95 

CH2 13145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH2I 3161 -00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213I 56-00000 

CH213157-00000 

CH213158-OOWO 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH2 13162-OoM)O 

(31-1213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00OOO 

CH213158-00000 

CH2I 3159-00000 

CH213160-DUP 

CH2I 3161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH21316DDUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CHZ13155-00000 

CH21 3156-00000 

CH213157-00000 

CH213158-00000 

CH213159M1000 

10MAR1995 

17MAR1995 

03MAR1994 

23MARl995 

28MAR1995 

17MAR 1994 

05APR 1 995 

05MAY 1993 

OSMAY 1993 

06MAY 1993 

1 1 MAY 1993 

13APR1995 

25MAR 1994 

2lAPRl995 

21MAYl993 

26APRl995 

31 MAR1 994 

O3MAY 1 995 

O2JUNl 993 

llMAYl995 

I OJUNI 993 

14JUN1993 

17MAY1995 

08APR1994 

25MAY1995 

23JUN 1993 

13APRl994 

01JUNl995 

18FEBl991 

18FEBl991 

1 8FEBI 991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBI 991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

Page 125 of 176 

VK 

WL 

VK 

WL 

WL 

WL 

WL 

VK 

VK 

VK 

WL 

WL 

VK 

VK 

WL 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

VK 

WL 

WL 

WL 

VK 

VK 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

SO 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N




1 ,l-Dichloroethene 75-35-4 CH213160-DUP 18FEB1991 SO 6.00E+00 U N 



1,2,4-Trichlorobenzene 


1.2 ,4-Trichlorobenzene 


1,2 ,+Trichlorobenzene 

1.2.4-Trichlorobenzene 


1,2.4-Trichlorobenzene 

1 .2,4-Trichlorobenzene 

1,2-Dichlorobenzene 


1,2-DichIorobenzene 

1.2-Dichlorobenzene 










1,2-Dichloroethane 


1 .Z-Dchloroethane 



1,2-Dchloroethene 

1,2-Dchloroethene 







1.2-Dchloroethene 

1.2-Dichloropropane 



1.2-Dchloropropane 




1 ,Z-Dichloropropane 


1 ,fDichlorobenzene 



1 ,3-Dchlorobenzene 


1,3-Dchlorobenzene 



1 ,J-Dichlorobenzene 

1 ,+Dichlorobenzene 

1 .4-Dchbrobenzene 

1 ,CDichlorobenzene 

1 .CDichlorobenzene 

1 .4-Dchlorobenzene 

1 ,+Dichlorobenzene 

1 A-Dchbrobenzene 


1,4-Dchbrobenzene 

2.4,5-TrichlorophenoI 

2,4,5-TrichlorophenoI 

2,4,!LTrichlorophenoI 

2.4.5-Trichlorophenol 


2,4.5-Trichlorophenol 

75-35-4 

75-35-4 

120-82-1 

120-82-1 

120-82-1 

120-82-1 

120-82-1 

120-82-1 

120-82-1 

120-82-1 

120-82-1 

95-50-1 

95-50-1 

95-50-1 

95-50-1 

95-50-1 

95-50-1 

95-50-1 

95-50-1 

95-50-1 

107-06-2 

107-06-2 

107-06-2 

107-06-2 

107-06-2 

107-06-2 

107-06-2 

107-06-2 

107-06-2 

540-59-0 

540-59-0 

540-59-0 

540-59-0 

540-59-0 

540-59-0 

540-59-0 

540-59-0 

540-59-0 

78-87-5 

78-87-5 

78-87-5 

78-87-5 

78-87-5 

78-87-5 

78-87-5 

78-87-5 

78-87-5 

541-73-1 

541-73-1 

541 -73-1 

541 -73-1 

541-73-1 

541-73-1 

541-73-1 

541-73-1 

541-73-1 

106-46-7 

106-46-7 

106-46-7 

106-46-7 

106-46-7 

10646-7 

106-46-7 

106-46-7 

106-46-7 

95-95-4 

959% 

95-95-4 

95-95-4 

95-95-4 

95-95-4 

CH213161-00000 

CH213162-00000 

CH21 3145-00000 

CH213155-00000 

CH2 13156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-M)000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH21 3161-00000 

CH2I 3162-00000 

CH213145-00000 

CH213155-00000 

CH213156-OW00 

CH213157-00000 

CH213158-00000 

CH213159-OOOOO 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-OOOW 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CHZl3162-ooMx) 

CH213145-00000 

CH213155-00000 

CHZl3156-00000 

CH213157-00000 

CH213158-00000 

CH2I 3159-00000 

CH2131 60-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156MH)oo 

CH213157-00000 

CH21315a00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBI 991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBI 991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

1 8FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

l8FEBl991 

18FEB1991 

I8FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

1 LIFE61 991 

18FEB1991 

CH213162-00000 18FEBl991 

CH2 13145-OO~ 18FEBl991 

CH213155-00000 18FEBl991 

CHZl3156-OooOO 18FEB1991 

CHZl3157-00000 18FEBl991 

CHZl31 sa00000 18FEBl991 

CH213159M)ooo 18FEBl991 

CH2131 60-DUP 18FEB1991 

CH213161 MH)oo 18FEB1991 

CH213162-OOOOO 18FEB1991 

CH21314!5-0OOOO 18FEB1991 

CH213155-00000 18FEB1991 

CH213156-00000 18FEB1991 

CH213157-00000 18FEB1991 

CH213158-00000 18FEB1991 

CH213159-00000 18FEB1991 

Page 126 of 176 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N




2,4,5-Trichlorophenol 95-95-4 CH213160-DUP 18FEB1991 SO 2.00E+03 U N ugh 

2,4,5-Trichlorophenol 








2.4,6-TrichlorophenoI 

2,4.6-TrichlorophenoI 

2,4.6-Trichlorophenol 

2.4-Dichlorophenol 

2,4-Dichlorophenol 

2 ,CDichlorophenol 



2,CDichlorophenol 




2.4-Dimethylphenol 

2,4-Dimethylphenol 



2 ,4-Dimethylphenol 


2 ,4-Dimethylphenol 

2,4Dimethylphenol 


2 ,4-Dinitrophenol 

2,CDinilrophenol 

2 ,+Dinitrophenol 

2.4-Dinitrophenol 

2 +Dinitrophenol 

2,4-Dinitrophenol 


2 ,&Dinitrophenol 


2,CDinitrotoluene 

2 +Dinitrotoluene 

2 ,&Dinitrotoluene 

2 .4-Dinitrotoluene 

2 ,4-Dinitrotoluene 


2.4-Dinitrotoluene 

2 ,4-Dinitrotoluene 

2 .4-Dinitrotoluene 

2 ,B-DinitrotoIuene 


2,6-Dinitrotoluene 







2-Butanone 

2-Butanone 

2-Butanone 

2-Butanone 

95-95-4 

95-95-4 

88-06-2 

88-06-2 

88-06-2 

88-06-2 

88-06-2 

88-06-2 

88-06-2 

88-06-2 

88-06-2 

120-83-2 

120-83-2 

120-83-2 

120-83-2 

120-83-2 

120-83-2 

120-83-2 

120-83-2 

120-83-2 

105-67-9 

105-67-9 

105-67-9 

10547-9 

105-67-9 

105-67-9 

105-67-9 

105-67-9 

105-67-9 

51-28-5 

51-28-5 

51-28-5 

51-28-5 

51-28-5 

51-28-5 

51-285 

51-28-5 

51-28-5 

121-14-2 

121 -14-2 

121 -14-2 

121-14-2 

121-14-2 

121 -14-2 

121-14-2 

121 -14-2 

121 -14-2 

606-20-2 

606-20-2 

606-20-2 

606-20-2 

606-20-2 

606-20-2 

606-20-2 

606-20-2 

606-20-2 

78-93-3 

78-93-3 

78-93-3 

7893-3 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH2 13161 -00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH2 13158-OOOOO 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH2 13145-OOOoO 

CH2I 3155-00000 

CH213156-00000 

CH213157-00000 

CH2 13158-00000 

CH213159-00000 

CH2131 60-DUP 

CH213161-00000 

CH213162-00000 

CH2 13145-0oooO 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213I 45-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH2 13158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-OOMM 

CH213162-00000 

CH213145-M)000 



CH213157-00000 

CH213158-WWO 

CH213159-00000 

CH213160-DUP 

CH2I 3161 -0oooO 

CH213162-00000 

CH213145-00000 

CH21 3155-00000 

CH213156-00000 


18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

J 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

2-Butanone 

78-93-3 

CH213158-~0 18FEB1991 

U 

N 

2 -But anon e 

2-Butanone 

2-Butanone 

2-Butanone 

2-Chloronaphthalene 


2-Chloronaphlhalene 




78-93-3 

78-93-3 

78-93-3 

78-93-3 

91-58-7 

91-587 

91-587 

91 -58-7 

91-58-7 

91-587 

CH213159-00000 

CH2131 60-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-WOW 

CH213157-00000 

CH21315B00000 

CH213159-00000 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Page 127 of 176 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so




2-Chloronaphthalene 91-58-7 CH213160-DUP 18FEB1991 SO 3.90E+02 U N 



2-Chlorophenol 









2-Hexanone 

2-Hexanone 

2-Hexanone 

2-Hexanone 

2-Hexanone 

2-Hexanone 

2-Hexanone 

2-Hexanone 

2-Hexanone 









2-Meth ylnaphthalene 

2-Methylphenol 


2-Meth ylphenol 
















2-Nitrophenol 

2-Nitrophenol 

2-Nitrophenol 

2-Nitrophenol 

2-Nitrophenol 

2-Nitrophenol 

2-Nitrophenol 

2-Nitrophenol 

2-Nitrophenol 

3.3-Dichlorobenzidine 

3,3-Dihlorobenzidine 


3,3-Dihlorobenzidine 

3.3-Dihlorobenzidine 


3.3-Dihlorobenzidine 

3,3’-Dichlorobenzidine 








91 -58-7 

91 -58-7 

95-57-8 

95-57-8 

95-57-8 

95-57-8 

95-57-8 

95-57-8 

95-57-8 

95-57-8 

95-57-8 

591 -78-6 

591-78-6 

591 -78-6 

591-78-6 

591 -78-6 

591-78-6 

591 -78-6 

591-78-6 

591-78-6 

91 -57-6 

91-57-6 

91-57-6 

91-57-6 

91-57-6 

91-57-6 

91-57-6 

91-57-6 

91-57-6 

95-48-7 

95-48-7 

95-48-7 

95-48-7 

95-48-7 

95-48-7 

95-48-7 

95-48-7 

95-48-7 

88-74-4 

88-74-4 

88-74-4 

88-74-4 

88-74-4 

88-74-4 

88-74-4 

88-74-4 

88-744 

88-75-5 

88-75-5 

88-75-5 

88-75-5 

88-75-5 

88-75-5 

88-75-5 

88-75-5 

88-75-5 

91-94-1 

91-94-1 

91-94-1 

91-94-1 

91-94-1 

91-94-1 

91-94-1 

91-94-1 

91-94-1 

99-09-2 

99-09-2 

99-09-2 

99-09-2 

99-09-2 

99-09-2 

CH213161-00000 


CH213145-00000 

CH2 13155-00000 

CH213156-00000 

CH2 13157-00000 

CH2 13158-00000 

CH213159-00000 

CH213160-DUP 


CH213162-00000 

CH213145-00000 

CH213155-00000 

CH2 13156-00000 

CH213157-00000 

CH213158-00000 

CH213159-OoooO 

CHZ13160-DUP 

CH213161-00000 


CH2 13145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH2I 3159-00000 

CH2I 3160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 




CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH2 13145-OoooO 

CH213155-ooOOO 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH2 13159-ooOOO 

CH21316O-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH2 13155-00000 

CH213156-00000 

CH2 13157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 


CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 


CH2 13145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-WOO0 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBI 991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

1 BFEBl991 

18FEB1991 

18FEB1991 

18FEBI 991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBI 991 

1 OFEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

I8FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

Page 128 of 176 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

so 

so 

SO 

SO 

SO 

so 

so 

SO 

SO 

SO 

so 

SO 

SO 

SO 

SO 

SO 

so 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

so 

so 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

3.90E+02 

3.90E+02 

3.90E+02 

4.1 OE+02 


3.60E+02 

3.70E+02 


3.90E+02 

3.90E+02 

6.50E+01 

1.20E+01 

1.20E+01 

l.lOE+Ol 

1.2OE+O1 

l.lOE+Ol 

1.20E+01 

1.20E+01 

1.20E+01 

l.lOE+Ol 

3.90E+02 



3.60E+02 

3.70E+02 


3.90E+02 

3.90E+02 

3.90E+02 

3.90E+02 



3.60E+02 

3.70E+02 


3.90E+02 

3.90E+02 

3.90E+02 

2.00E+03 

2.10E+03 

2.00E+O3 

1.80E+O3 

1.90E+03 

2.00E+03 

2.00E+03 

1.90E+03 

I .90E+O3 

3.90E+02 



3.60E+02 

3.70€+02 


3.9OE+02 

3.90E+02 

3.90E+02 

7.80E+02 

8.20E+02 

8.20E+02 

7.30E+02 

7.40E+02 

8.1 OE+02 

7.80E+02 

7.80E+02 

7.80E+02 

2.00E+O3 

2.1OE+O3 

2.00E+03 

1.80E+O3 

I .90E+03 

2.00E+03 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

J 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N




3-Nitroaniline 99-09-2 CH213160-DUP 18FEB1991 SO 2.00E+03 



4,4-DDD 

4,4-DDD 

4.4-DDD 


4,4-DDD 

4,4-DDD 

4,4-DDD 


4,4-DDD 

4,4-DDE 

4,4-DDE 

4.4-DDE 

4,4-DDE 


4,4-DDE 



4.4-DDT 

4,4'-DDT 

4,4-DDT 

4,4-DDT 

4,4-DDT 

4.4-DDT 

4,4-DDE 

4,4'-DDT 

4.4'-DDT 

4,4'-DDT 

4.6-Dinlro-2-methylphenol 

4,6-Dinitro-2-methylphenol 



4.6-Dinlro-2-met hylphenol 

4,6-Dinlro-2-rnethylphenol 



4.6-Din Wro-2-methylphenol 

4-Bromophenyl-phenylether 




4-Bromophenyl-phen ylether 

CBromophenyl-phenylether 




4-Chloro-3-methylphenol 









4-Chloroaniline 




4Chloroaniline 


QChloroaniline 

CChloroaniline 


4-Chlorophenyl-phenylther 



4ChlorophenyCphenylether 

4-Chlorophenyl-phenylether 

4-Chlorophen yl-phen ylether 

99-09-2 

99-09-2 

72-54-8 

72-54-8 

72-54-8 

72-54-8 

72-54-8 

72-54-8 

72-54-8 

72-54-8 

72-54-8 

72-55-9 

72-55-9 

72-55-9 

72-55-9 

72-55-9 

72-55-9 

72-55-9 

72-55-9 

7 2 - 5 5 - 9 

50-29-3 

50-29-3 

50-29-3 

50-29-3 

50-29-3 

50-29-3 

50-29-3 

50-29-3 

534-52-1 

534-52-1 

534-52-1 

534-52-1 

534-52-1 

534-52-1 

534-52-1 

534-52-1 

534-52-1 

101-55-3 

101-55-3 

101-55-3 

101-55-3 

101 -55-3 

101-55-3 

101-55-3 

101-55-3 

101 -55-3 

59-50-7 

59-50-7 

59-50-7 

59-50-7 

59-50-7 

59-50-7 

59-50-7 

59-50-7 

106-47-8 

106-47-8 

106-47-8 

106-47-8 

106-478 

106-47-8 

106-47-8 

106-47-8 

7005-72-3 

7005-72-3 

7005-72-3 

7005-72-3 

7005-72-3 

50-29-3 

59-50-7 

106-47-8 

7005-72-3 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH2 131 55-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH21316O-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH2131 60-DUP 

CH213161 

-oooOO 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH21316O-DUP 


CH213162-00000 



CH2 13156-00000 

CH213157-00000 

CH21315&00000 

CH2 13159-oooO0 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 


CH213159-oM)OO 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-OWW 

CH2 13157-00000 

CH213156-00000 

CH213159-00000 

CH213156-00000 

CH213162-00000 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

l8FEB1991 

1 8FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

1 8FEBl991 

1 8FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

so 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

so 

so 

so 

so 

SO 

so 

SO 

so 

SO 

so 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

so 

SO 

SO 

so 

so 

so 

SO 

SO 

SO 

SO 

SO 

so 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

J 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

N 

N 

N 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Page 129 of 176




4-Chlorophenyl-phenylether 7005-72-3 CH213160-DUP 18FEB1991 SO 3.90E+02 U N 



4-Methyl-2-pentanone 



























4-Nitrophenol 

4-Nitrophenol 

4-Nitrophenol 

4-Nitrophenol 

4-Nitrophenol 

4-Nitrophenol 

4-Nitrophenol 

4-Nitrophenol 

4-Nitrophenol 

Acenaphthene 

Acenaphthene 

Acenaphthene 

Acenaphthene 

Acenaphthene 

Acenaphthene 

Acenaphthene 

Acenaphthene 

Acenaphthene 










Acetone 

Acetone 

Acetone 

Acetone 

Acetone 

Acetone 

Acetone 

Acetone 

Acetone 

Aldrin 

Aldrin 

Aldrin 

Aldrin 

Aldrin 

Aldrin 

7005-72-3 

7005-72-3 

108-10-1 

108-10-1 

108-10-1 

108-10-1 

108-10-1 

108-10-1 

108-10-1 

108-10-1 

108-10-1 

106-44-5 

106-44-5 

106-44-5 

106-44-5 

106-44-5 

106-44-5 

106-44-5 

106-44-5 

106-44-5 

100-01-6 

100-01 -6 

100-01 -6 

100-01-6 

100-01-6 

100-01-6 

100-01 -6 

100-01-6 

100-01-6 

100-02-7 

100-02-7 

100-02-7 

100-02-7 

100-02-7 

100-02-7 

100-02-7 

100-02-7 

100-02-7 

83-32-9 

83-32-9 

83-32-9 

83-32-9 

83-32-9 

83-32-9 

83-32-9 

83-32-9 

83-32-9 

208-96-8 

208-96-8 

208-96-8 

208-96-8 

208-96-8 

208-96-8 

208-96-8 

208-96-8 

208-96-8 

67-64-1 

67-64-1 

67-64-1 

67-64-1 

67-64-1 

67-64-1 

67-64-1 

67-64-1 

67-64-1 

309-00-2 

309-00-2 

309-00-2 

309-00-2 

309-00-2 

309-00-2 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH2I 3159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH2I 3155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-000W 

CH213156-00000 

CH2I 3157-0oooO 

CH213158-000W 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH2 13157-00000 

CH213158-00000 

CH213159-00000 

CH2I 3160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00OOO 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-oooOO 

CH21 3157-0oooO 

CH213158-00000 

CH213159-00000 

CH21 3160-DUP 

CH21 3161 -00000 

CH2I 3162-ooOOO 

CH213145-00000 

CH213155-00000 

CH213156-OWOO 

CH213157-00000 


CH213159-M)ooo 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH21 3157-00000 

CH213158-00000 

CH2I 3159M)ooo 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBI 991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBI 991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEBI 991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEBI 991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1 991 

Page 130 of 176 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

SO 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

3.90E+02 

3.90E+02 

1.20E+01 

1.20E+01 

l.lOE+Ol 

1.20E+01 

l.lOE+Ol 

1.20E+01 

1.20E+01 

1.20E+01 

I.lOE+OI 

3.90E+02 



3.60E+02 

3.70E+02 


3.90E+02 

3.90E+02 

3.9OE+02 

2.00E+O3 

2.10E+03 

2.00E+O3 

1.80E+O3 

1.90E+03 

2.00E+O3 

2.00E+O3 

1.90E+03 

I .90E+03 

2. WE+03 

2.10E+O3 

2.00E+O3 

I .80E+O3 

I .90E+03 

2.00E+O3 

2.00E+O3 

I .90E+03 

I .90E+03 

3.90E+02 



3.60E+02 

3.70E+02 


3.90E+02 

3.90E+02 

3.90E+02 

3.90E+02 



3.60E+02 

3.70E+02 


3.90E+02 

3.90E+02 

3.90E+02 

8.80E+Ol 

6.30EtOl 

I .00E+02 

8.10E+01 

7.40Et01 

4.3OE+01 

3.80E+01 

9.80E+01 

7.70E+01 

1.00E+Ol 

9.00E+00 

1.00E+01 

9.00E+00 

9.00E+00 

9.00E+00 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

UB 

B 

B 

B 

B 

B 

B 

B 

B 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

NT 

NT 

NT 

NT 

NT



ANALYE CAS NUMBER SAMPLE ID DATE TfPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Aldrin 309 - 00 - 2 CH213160-DUP 18FEB1991 SO 9.00E+00 U 

NT 

Aldrin 

Aldrin 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Anthracene 

Anthracene 

Anthracene 

Anthracene 

Anthracene 

Anthracene 

Anthracene 

Anthracene 

Anthracene 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

309-00-2 

309-00-2 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

120-12-7 

120-12-7 

120-12-7 

120-12-7 

120-12-7 

120-12-7 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH2 13159-00000 

CH2131 60-DUP 

CH213161-00000 

CH213162-00000 

CH2 13145-OOOW 

CH213155-00000 

CH213156-00000 

CH213157-00000 


Antimony ' 

Antimony 

Antimony 

Antimony 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 

Benzene 
















120-12-7 

120-12-7 

120-12-7 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

71-43-2 

71-43-2 

71-43-2 

71-43-2 

71-43-2 

71-43-2 

71-43-2 

71-43-2 

71-43-2 

56-55-3 

56-55-3 

56-55-3 

56-55-3 

56-55-3 

56-55-3 

56-55-3 

56-55-3 

56-55-3 

50-32-8 

50-32-8 

50-32-8 

50-32-8 

50-32-8 

50-32-8 


CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 


CH213158-00000 

CH2 13159-00000 

CH213160-DUP 


CH213162-00000 

CH213145-00000 

CH213155-00OOO 


CH213157-00000 

CH213158-00000 

CH213159-00000 

CH2131 60-DUP 

CH213161 -OOO00 

CH213162-00000 


CH213155-00000 

CH213156WOW 


CH213158-00000 


CH2131 60-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 



CH213158-00000 

CH213159-WOO0 

CH21316O-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CHZ13158-00000 

CH213159-00000 

18FEB1991 

18FEB1991 

1 8FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

1 8FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

Page 131 of 176 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

U 

U 

E 

E 

E 

E 

E 

E 

E 

E 

E 

U 

U 

U 

U 

U 

U 

U 

U 

J 

UN 

UN 

UN 

UN 

UN 

UN 

UN 

UN 

UN 

N 

BN 

BN 

N 

UNW 

BN 

UN 

U W 

BNW 

B' 

B' 

B' 

B' 

B' 

B' 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

J 

U 

J 

U 

U 

U 

U 

U 

U 

NT 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N



ANALME CAS NUMBER SAMPLE ID DATE WPE RESULT ERROR QUALIFIER QUALIFIER UNITS 


. ... 

50-32-8 CH213160-DUP 18FEB1991 SO 3.90E+02 












Benzo(g,h.i)perylene 

Benzo(g.h.i)perylene 

















Benzoic Acid 

Benzoic Acid 

Benzoic Acid 

Benzoic Acid 

Benzoic Acid 

Benzoic Acid 

Benzoic Acid 

Benzoic Acid 

Benzoic Acid 

Benzyl Alcohol 









Benzyl Butyl Phthalate 









Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 


Bromodichlorornethane 


Bromodichbrornethane 



50-32-8 

50-32-8 

205-99-2 

205-99-2 

205-99-2 

205-99-2 

205-99-2 

205-99-2 

205-99-2 

205-99-2 

205-99-2 

191 -24-2 

191 -24-2 

191 -24-2 

191 -24-2 

191-24-2 

191 -24-2 

191 -24-2 

191-24-2 

191-24-2 

207-08-9 

207-08-9 

207-08-9 

207-08-9 

207-08-9 

207-08-9 

207-08-9 

207-08-9 

207-08-9 

65-85-0 

6585-0 

65-85-0 

65-85-0 

65-85-0 

65-85-0 

65-85-0 

65-85-0 

65-85-0 

100-51-6 

100-51-6 

100-51-6 

100-51-6 

100-516 

100-51 -6 

100-51-6 

100-51-6 

100-51-6 

85-68-7 

85-68-7 

85-68-7 

85-68-7 

85-68-7 

85-68-7 

85-68-7 

85-68-7 

85-68-7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41 -7 

7440-41-7 

7440-41 -7 

7440-41 -7 

7440-41-7 

75-274 

75-27-4 

75-27-4 

75-274 

75-274 

75-274 

CH213161-00000 

CH213162-00000 

CH2 13145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 


CH213145-00000 


CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH21316O-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 



CH213157-M)(xM 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161 -oooOO 

CH213162-oooO0 


CH2 13155-00000 

CH213156-00000 

CH213157-00000 

CH213158-WOW 

CH213159-00000 

CH21316O-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH21315sMK)o 

CH213156-00000 

CH213157-00000 

CH2 13158-WWO 

CH2 13159-00000 

CH213160-DUP 

CH213161-WOOO 

CH213162-00000 

CH213145-00000 

CH2 13155-00000 

CH2 13156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 


CH213155-00000 

CH213156MKXW1 

CH213157-00000 

CH2 13158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-M)oO 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-M)o 

CH213159-00000 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

l8FEBl991 

18FEBl991 

18FEBl991 

18FEBI991 

18FEBI991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

1 8FEBl 991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

Page 132 of 176 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

so 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

so 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

so 

so 

so 

SO 

SO 

so 

so 

SO 

so 

so 

SO 

SO 

SO 

SO 

SO 

so 

so 

SO 

SO 

SO 

SO 

SO 

so 

so 

SO 

so 

SO 

SO 

SO 

SO 

so 

SO 

SO 

SO 

3.90E+02 

3.90E+02 

3.90E+02 



3.60E+02 

3,70E+02 


3.90E+02 

3.9OE+02 

3.90E+02 

3.90E+02 



3.60E+02 

3.70E+02 


3.90E+02 

3.90E+02 

3.90E+02 

3.90E+02 



3.60E+02 

3.70E+02 


3.90E+02 

3.90E+02 

3.90E+02 

2.00E+O3 

2.10E+O3 

2.00E+03 

1.80E+03 

I .90E+03 

2.00E+03 

2.00E+03 

I .90E+03 

I .90E+03 

3.90E+02 



3.60E+02 

3.70E+02 


3.90E+02 

3.90E+02 

3.90E+02 

3.90E+02 




3.70E+02 


5.00E+01 

3.90E+02 

I .00E+02 

1 .00E+00 

I.WE+OO 

0.00E+00 

0.00E+00 

O.WE+OO 

0.00E+00 

1.00E+00 

0.00E+00 

0.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.WE+00 

6.00E+00 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

J 

U 

J 

U 

J 

J 

U 

J 

B 

B 

B 

B 

B 

B 

B 

B 

B 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N




Bromodichloromet hane 75-27-4 CH213160-DUP 18FEB1991 SO 6.00€+00 U N udkg 

Bromodichloromet hane 75-27-4 

CH213161-00000 18FEB1991 6.00E+00 

U 

N 

Bromodichloromet hane 75-27-4 

CH213162-00000 18FEB1991 6.00E+00 

U 

N 

Bromoform 

75-25-2 

CH213145-OOOOO 18FEB1991 6.00€+00 

U 

N 

Bromoform 

75-25-2 

CH213155-00000 18FEB1991 6.00E+00 

U 

N 

Bromoform 

75-25-2 

CH213156-00000 18FEB1991 6.00E+00 

U 

N 

Bromoform 

75-25-2 

CH213157-00000 18FEB1991 6.00E+00 

U 

N 

Bromoform 

75-25-2 

CH213158-00000 18FEB1991 

6.00E+00 

U 

N 

Bromoform 

75-25-2 

CH213159-00000 18FEB1991 

6.00E+00 

U 

N 

Bromoform 

75-25-2 

CH213160-DUP 18FEB1991 

6.00E+00 

U 

N 

Bromoform 

75-25-2 

CH213161-00000 18FEB1991 

6.00E+00 

U 

N 

Bromoform 

75-25-2 

CH213162-00000 18FEB1991 

6.00€+00 

U 

N 

Bromomethane 

74-83-9 

CH213145-00000 18FEB1991 1.20E+01 

U 

N 

Bromomethane 

74-83-9 

CH213155-00000 18FEB1991 1.20E+01 

U 

N 

Bromornethane 

74-83-9 

CH213156-00000 18FEB1991 l.lOE+Ol 

U 

N 

Bromomethane 

74-83-9 

CH213157-00000 18FEB1991 1.20€+01 

U 

N 

Bromomethane 

74-83-9 

CH213158-OOOOO 18FEB1991 l.lOE+Ol 

U 

N 

Bromomeihane 

74-83-9 

CH213159-00000 18FEB1991 1.20E+01 

U 

N 

Bromomethane 

74-83-9 

CH2131 60-DUP 18FEBl991 

1.20E+01 

U 

N 

Bromomethane 

74-83-9 

CH213161-00000 18FEB1991 1.20E+01 

U 

N 

Bromomefhane 

74-83-9 


18FEB1991 l.lOE+Ol 

U 

N 

Cadmium 

7440-43-9 

CH213145-00000 18FEBl991 

1.00E+00 

U 

N 

Cadmium 

7440-43-9 

CH213155-00000 18FEB1991 l.OOE+OO 

U 

N 

Cadmium 

7440-43-9 

CH213156-00000 18FEB1991 l.OOE+OO 

U 

N 

Cadmium 

7440-43-9 

CH213157-00000 18FEB1991 1 .OOE+OO 

U 

N 

Cadmium 

7440-43-9 

CH213158-00000 18FEB1991 l.OOE+OO 

U 

N 

Cadmium 

7440-43-9 

CH213159-OoooO 18FEB1991 l.OOE+OO 

U 

N 

Cadmium 

7440-43-9 

CH2 13160-DUP 

18FEB1991 1 .OOE+OO 

U 

N 

Cadmium 

7440-43-9 

CH213161 -00OOO 18FEB1991 l.OOE+OO 

U 

N 

Cadmium 

7440-43-9 

CH213162-00000 18FEB1991 I .00E+00 

U 

N 

Calcium 

7440-70-2 

CH213145-00000 18FEB1991 l.llE+04 

'E 

N 

Calcium 

7440-70-2 

CH213155-00000 18FEB1991 1.35E+03 

E' 

N 

Calcium 

7440-70-2 

CH213156OoooO 18FEB1991 1.22E+O3 

'E 

N 

Calcium 

7440-70-2 

CH2I 3157-00000 

18FEB1991 6.90€+02 

B'E 

N 

Calcium 

7440-70-2 

CH213158-00000 18FEB1991 1.07€+03 

E' 

N 

Calcium 

7440-70-2 

CH213159-00000 18FEB1991 9.14E+02 

B'E 

N 

Calcium 

7440-70-2 

CH21316O-DUP 18FEB1991 8.66E+02 

E' 

N 

Calcium 

7440-70-2 

CH213161-00000 18FEB1991 8.86E+02 

BE. 

N 

Calcium 

7440-70-2 

CH213162-OoooO 18FEB1991 5.72E+02 

BE' 

N 

Carbon Disulfide 

75-15-0 

CH213145-00000 18FEB1991 6.00E+00 

U 

N 


75-15-0 

CH213155-00000 18FEB1991 2.00E+00 

JB 

N 


75-15-0 

CH213156-00OOO 18FEB1991 2.00E+00 

JB 

N 


75-15-0 

CH213157-00000 18FEB1991 2.00E+00 

JB 

N 


75-15-0 

CH213158-00000 18FEB1991 2.00E+00 

JB 

N 


75-15-0 

CH213159-00000 18FEBI991 2.00E+00 

JB 

N 


75-15-0 

CH213160-DUP 18FEB1991 2.00€+00 

JB 

N 


75-15-0 

CHZI 3161 -00000 18FEBI 991 

2.00E+00 

BJ 

N 


75-15-0 

CH213162-00000 18FEB1991 6.00E+00 

U 

N 

Carbon Tetrachloride 56-23-5 

CH213145-00000 18FEB1991 6.00E+00 

U 

N 


CH213155-WOO0 18FEB1991 6.00E+00 

U 

N 


CH213156-00000 18FEB1991 6.00E+00 

U 

N 


CH213157-00000 18FEB1991 6.00E+W 

U 

N 


CH213158-WOW 18FEB1991 6.00E+00 

U 

N 


CH213159-00000 18FEB1991 6.00E+00 

U 

N 


CH213160-DUP 18FEB1991 6.00E+00 

U 

N 


CH2 1316 1 -oooOO 18FEBl991 

6.00E+00 

U 

N 


CH213162-00000 18FEB I99 I 

6.00€+00 

U 

N 

Chlorobenzene 

108-90-7 

CH213145-oooOO 18FEB1991 6.00E+00 

U 

N 

Chlorobenzene 

108-90-7 

CH213155-00000 18FEB1991 6.00E+00 

U 

N 

Chlorobenzene 

108-90-7 

CH213156-00000 18FEB1991 6.WE+00 

U 

N 

Chlorobenzene 

108-90-7 

CH213157-00000 18FEB1991 6.00E+00 

U 

N 

Chlorobenzene 

108-90-7 

CH213158-00000 18FEB1991 

6.00€+00 

U 

N 

Chlorobenzene 

108-90-7 

CHZl3159-00000 18FEB1991 6.00E+00 

U 

N 

Chlorobenzene 

108-90-7 

CH213160-DUP 18FEB1991 6.00E+00 

U N 

Chlorobenzene 

108-90-7 

CH213161-00000 18FEBl991 

6.00E+00 

U 

N 

Chlorobenzene 

108-90-7 

CH213162-oooO0 18FEB1991 6.00E+00 

U 

N 

Chloroethane 

75-00-3 

CH213145-00000 18FEB1991 

1.20E+01 

U 

N 

Chloroethane 

75-00-3 

CH213155-00000 18FEB1991 

1 .ZOE+Ol 

U 

N 

Chloroeihane 

75-00-3 

CH2 13156-00000 

18FEBl991 

l.lOE+Ol 

U 

N 

Chloroeihane 

75-00-3 

CH2 13157-00000 

18FEB1991 1.20E+01 

U 

N 

Chloroethane 

75-00-3 

CH2 13158-oooW 

I 8FEB 1991 

1.10E+01 

U 

N 

Chloroethane 

75-00-3 

CH213159-00000 18FEB1991 

1.20E+01 

U 

N 

Page 133 of 176 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so




Chloroethane 75-00-3 CH213160-DUP 18FEB1991 SO 1.2OE+Ol U N 

Chloroethane 

Chloroethane 

Chloroform 

Chloroform 

Chloroform 

Chloroform 

Chloroform 

Chloroform 

Chloroform 

Chloroform 

Chloroform 

Chloromethane 

Chloromethane 

Chloromethane 

Chloromethane 

Chloromethane 

Chloromethane 

Chloromethane 

Chloromethane 

Chloromethane 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chrysene 

Chrysene 

Chrysene 

Chrysene 

Chrysene 

Chrysene 

Chrysene 

Chrysene 

Chrysene 

Coban 

Coban 

Cobalt 

Coban 

Coban 

Coban 

Coban 

Cobalt 

Coban 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Cyanide 

Cyanide 

Cyanide 

Cyanide 

Cyanide 

Cyanide 

Cyanide 

Cyanide 

Cyanide 

Di-n-butylphthalate 





Dbn-butylphthalate 

75-00-3 

75-00-3 

67-66-3 

67-66-3 

67-66-3 

67-66-3 

67-66-3 

67-66-3 

67-66-3 

67-66-3 

67-66-3 

74-87-3 

74-87-3 

74-87-3 

74-87-3 

74-87-3 

74-87-3 

74-87-3 

74-87-3 

74-87-3 

7440-47-3 

7440-47-3 

744047-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

218-01-9 

218-01 -9 

218-01-9 

218-01 -9 

218-01 -9 

218-01-9 

218-01 -9 

218-01 -9 

218-01 -9 

744048-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

744048-4 

7440-484 

7440-48-4 

7440-48-4 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

57-12-5 

57-12-5 

57-12-5 

57-12-5 

57-12-5 

57- 12-5 

57-12-5 

57-12-5 

57-12-5 

84-74-2 

84-74-2 

84-74-2 

84-74-2 

84-74-2 

84-74-2 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CHZl316O-DUP 

CH213161-00000 

CH213162-00000 

CH213145-OW00 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-'00000 

CHZl3160-DUP 

CHZl3161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-OOoOO 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-OWOO 

CH213145-00000 

CHZI 3155-00000 

CH213156-00000 

CH213157-00000 

CH21315g00000 

CH213159-00000 

CHZl3160-DUP 

CH213161-00000 

CH2 13162-WWO 

CH213145-00000 

CH213155Mxxw) 


CHZI 3157-00000 

CH213158-WOW 

CH2I 3159-00000 

CH2131 60-DUP 

CH213161 -00000 

CH213162-00000 

CH213145-00000 

CHZl3155-00000 

CH213156-00000 


CHZl3158-00000 

CHZI 3159-00000 

CHZI316O-DUP 

CHZl3161MK)00 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159MHHH) 

CH2 131 GQDUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155M)oO 

CH2 131 sM)o 

CHZI3157-00000 

CH21315800000 

CHZ 13159-00000 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBI 991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

1 OFEB1991 

18FEBl991 

18FEB 199 1 

18FEB1991 

18FEBl991 

18FEB199 1 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBI 991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEBl 991 

18FEB1991 

18FEBl991 

18FEB199 1 

18FEBI991 

Page 134 of 176 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

SO 

so 

so 

so 

so 

so 

U 

U 

U 

U 

U 

U 

U 

U 

U 

u 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

B 

B 

B 

B 

B 

U 

U 

U 

U 

U 

U 

U 

U 

J 

B 

B 

B 

B 

B 

B 

B 

B 

B 

B 

B 

B 

B 

B 

B 

B 

U 

U 

U 

U 

U 

U 

U 

U 

U 

UJB 

JB 

JB 

JB 

JB 

JB 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N




Di-n-butylphthalate 84-74-2 CH213160-DUP 18FEB1991 SO 9.20E+01 JB 



Di-n-octylphthalate 










Dibenzo(a ,h)anthracene 






Dibenzo(a.h)anthracene 


Dibenzofuran 

Dibenzofuran 

Dibenzofuran 

Dibenzofuran 

Dibenzofuran 

Dibenzofuran 

Dibenzofuran 

Dibenzofuran 

Dibenzofuran 




Dibromochlorornet hane 





Dibromochlorornethane 

Dieldrin 

Dieldrin 

Dieldrin 

Dieldrin 

Dieldrin 

Dieldrin 

Dieldrin 

Dieldrin 

Dieldrin 

Diethylphthalate 









Dimethylphthalate 









Endosulfan I 

Endosulfan I 

Endosulfan I 

Endosulfan I 

Endosulfan I 

Endosulfan I 

84-74-2 

84-74-2 

117-84-0 

117-84-0 

117-84-0 

117-84-0 

117-84-0 

117-84-0 

117-84-0 

117-84-0 

117-84-0 

53-70-3 

53-70-3 

53-70-3 

53-70-3 

53-70-3 

53-70-3 

53-70-3 

53-70-3 

53-70-3 

132-64-9 

132-64-9 

132-64-9 

132-64-9 

132-64-9 

132-64-9 

132-64-9 

132-64-9 

132-64-9 

124-48-1 

124-48-1 

124-48-1 

124-48-1 

124-48-1 

124-48-1 

124-48-1 

124-48-1 

124-48-1 

60-57-1 

60-57-1 

60-57-1 

60-57-1 

60-57-1 

60-57-1 

60-57-1 

60-57-1 

60-57-1 

84-662 

84-66-2 

84-66-2 

84-66-2 

84-66-2 

84-66-2 

84-66-2 

84-66-2 

84-66-2 

131 -11-3 

131-11-3 

131 -11-3 

131 -11-3 

131 -11-3 

131-11-3 

131 -11-3 

131-11-3 

131-11-3 

959-98-8 

959-98-8 

959-98-8 

959-98-8 

959-988 

959-988 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH2 13160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH2 13157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH2 13161 -00000 

CH2 13162-0oooO 

CH213145-~00 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH2 13158-00000 

CH213159-00000 

CH2I 3160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH2 13158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH2 13145-00000 

CH213155-00000 

CH213156-00000 


CH213158-00000 

CH2 13159-00000 

CH213160-DUP 

CH213161-00000 

CH2I 3162-OOOOO 


CH213155-WOO0 

CH213156-00000 

CH213157-00000 

CH21315RWOO0 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-WOO0 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213156-00000 

CH213159-00000 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBI 991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBI 991 

18FEBl991 

18FEB1991 

18FEB1991 

1 8FEBI 991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBI 991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBI 991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

Page 135 of 176 

so 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

so 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

so 

SO 

SO 

SO 

SO 

so 

SO 

so 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

so 

so 

SO 

SO 

SO 

so 

so 

SO 

SO 

SO 

SO 

so 

SO 

so 

so 

so 

so 

8.00E+01 

2.20E+02 

3.90E+02 

4. I OE+02 


3.60E+02 

3.70€+02 


3.90€+02 

3.90E+02 

3.90E+02 

3.90E+02 



3.60E+02 

3.70E+02 


3.90E+02 

3.90E+02 

3.90E+02 

3.90E+02 



3.60E+02 

3.70E+02 


3.90E+02 

3.90E+02 

3.90E+02 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

2.00E+01 

I .90E+01 

1.90E+01 

1.70E+01 

1.70E+01 

1.80E+01 

I .90E+01 

1.80E+01 

I .90E+01 

3.90E+02 



3.60E+02 

3.70E+02 


3.90E+02 

3.90E+02 

6.80E+01 

3.90E+02 



3.60E+02 

3.70E+02 


3.90E+02 

3.9OE+O2 

3.9OE+02 

1 .OOE+OI 

9.00E+00 

1.00E+Ol 

9.00E+00 

9.00€+00 

9.00E+00 

JB 

JB 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

J 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

NT 

NT 

NT 

NT 

NT




Endosulfan I 959-98-8 CH213160-DUP 18FEB1991 SO 9.00E+00 U 

NT 

Endosulfan I 

Endosulfan I 

Endosulfan II 

959-98-8 

959-98-8 

33213-65-9 

CH213161-00000 

CH213162-00000 

CH213145-00000 

18FEB1991 

18FEBl991 

18FEB1991 

9.00E+00 

9.00E+00 

2.00E+01 

U 

U 

U 

NT 

NT 

NT 

Endosulfan II 

33213-65-9 

CH21 3155-00000 

18FEB1991 I .90E+01 

U 

NT 

Endosulfan II 

Endosulfan II 

Endosulfan II 

Endosulfan II 

Endosulfan II 

Endosulfan II 

Endosulfan II 










Endrin 

Endrin 

Endrin 

Endrin 

Endrin 

Endrin 

Endrin 

Endrin 

Endrin 

Endrin Ketone 

Endrin Ketone 

Endrin Ketone 

Endrin Ketone 

Endrin Ketone 

Endrin Ketone 

Endrin Ketone 

Endrin Ketone 

Endrin Ketone 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Ethylbenzene 

Fluoranthene 

Fluoranthene 

Fluoranlhene 

Fluoranthene 

Fluoranthene 

Fluoranthene 

Fluoranthene 

Fluoranthene 

Fluoranthene 

Fluorene 

Fluorene 

Fluorene 

Fluorene 

Fluorene 

Fluorene 

Fluorene 

Fluorene 

Fluorene 

Heptachlor 

Heptachlor 

Heptachlor 

Heptachlor 

Heptachlor 

Heptachlor 

33213-65-9 

33213-65-9 

33213-65-9 

33213-65-9 

33213-65-9 

33213-65-9 

33213-65-9 

1031-07-8 

1031-07-8 

1031-07-8 

1031 -07-8 

1031 -07-8 

1031-07-8 

1031-07-8 

1031-07-8 

1031 -07-8 

72-20-8 

72-20-8 

72-20-8 

72-20-8 

72-20-8 

72-20-8 

72-20-8 

72-20-8 

72-20-8 

53494-70-5 

53494-70-5 

53494-70-5 

53494-70-5 

53494-70-5 

53494-70-5 

53494-70-5 

53494-70-5 

53494-70-5 

100-414 

100-414 

100-414 

100-41-4 

100-41-4 

100-41-4 

100-414 

100-414 

100414 

20644-0 

20644-0 

20644-0 

20644-0 

206-44-0 

20644-0 

20644-0 

20644-0 

206-44-0 

86-73-7 

86-73-7 

86-73-7 

86-73-7 

86-73-7 

86-73-7 

86-73-7 

86-73-7 

86-73-7 

7644-8 

76448 

76448 

7644-8 

7644-8 

7644-8 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH2 13162-00000 

CH2I 3145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH2 13155-00000 

CH213156-OO000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213I 45-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 


CH213159-00000 

CH21316dDUP 

CH2I 3161 -00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 


CH2I 3159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH21315MH)o 

CH213157-00000 

CH213158-00000 

CH2 13159-00000 

CH213160-DUP 

CH2 13161 -oooOO 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH2 13156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161M)o 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 


CH21315800000 

CH213159-00000 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBI 991 

18FEBI 991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBI991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

I8FEBl99I 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

1.90E+01 

1.70E+01 

1.70€+01 

1.80E+01 

1.90E+01 

1.80€+01 

I .90E+01 

2.00E+01 

1.90E+01 

1.90E+01 

1.70E+01 

1.70E+01 

1.80E+01 

1.90E+01 

1.80E+01 

1.90E+01 

2.00E+01 

1.90E+01 

1.90E+01 

1.70E+01 

1.70E+01 

1.80E+01 

1.90E+01 

1.80E+01 

1.90E+01 

2.00E+01 

1.90E+01 

1.90E+OI 

1.70E+01 

1.70E+01 

I .80E+01 

I .90E+OI 

I .80E+Ol 

I .90E+01 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.WE+00 

6.00E+W 

6.00E+00 

6.WE+W 

6.00E+00 

3.90E+02 

6.10E+01 


6.3OE+01 

3.70E+02 

6.50E+01 

7.00E+01 

5.00E+OI 

1.40E+02 

3.90E+02 



3.60E+O2 

3.70E+02 


3.90E+02 

3.90E+02 

3.90E+02 

I.WE+Ol 

9.00E+00 

1 .00E+01 

9.00E+00 

9.00E+00 

9.00E+00 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

J 

J 

J 

U 

J 

J 

J 

J 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

NT 

NT 

NT 

NT 

NT 

Page 136 of 176 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so




HeDtachlor 76-44-8 CH213160-DUP 18FEB1991 SO 9.00E+00 U 

NT 

Heptachlor 

Heptachlor 

Heptachlor Epoxide 









Hexachlorobenzene 









Hexachlorobutadiene 









Hexachlorocyclopentadiene 

76-44-8 

76-44-8 

1024-57-3 

1024-57-3 

1024-57-3 

1024-57-3 

1024-57-3 

1024-57-3 

1024-57-3 

1024-57-3 

1024-57-3 

118-74-1 

118-74-1 

118-74-1 

118-74-1 

118-74-1 

118-74-1 

118-74-1 

118-74-1 

118-74-1 

87-68-3 

87-68-3 

87-68-3 

87-68-3 

87-68-3 

87-68-3 

87-68-3 

87-68-3 

87-68-3 

77-47-4 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 


CH213159-00000 

CH213160-DUP 

CH213161-00000 


CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Hexachlorocyclopentadiene 77-47-4 

CH213155-~0 18FEB1991 

U 

N 








Hexachloroethane 








77-47-4 

77-47-4 

77-47-4 

77-47-4 

77-47-4 

77-47-4 

77-47-4 

67-72-1 

67-72-1 

67-72-1 

67-72-1 

67-72-1 

67-72-1 

67-72-1 

67-72-1 



CH213158-00000 


CH21316O-DUP 

CH2I 3161 -0oOOO 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-OOOW 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

18FEBI 991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 


67-72-1 

CH213162-~0 18FEB1991 

U 

N 

Indeno(l.2.3-cd)pyrene 

Indeno(l,2.3-cd)pyrene 

Indeno(l,2,3-cd)pyrene 

Indeno(1,2,bcd)pyrene 

Indeno(l.2,3-cd)pyrene 

Indeno(l.2,3-cd)pyrene 

Indeno(l.2 ,J-cd)pyrene 

Indeno(l.2 ,bcd)pyrene 


Iron 

Iron 

Iron 

Iron 

193-39-5 

193-39-5 

193-39-5 

193-39-5 

193-39-5 

193-39-5 

193-39-5 

193-39-5 

193-39-5 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

CH213145-00000 

CH2I 3155-00000 

CH213156-00000 

CH213157-00000 

CH213158-WOO0 

CH213159-00000 

CH2I 3160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-OOO00 

CH213155-00000 

CH213156-OOO00 

CH213157-00000 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

U 

U 

U 

U 

U 

U 

U 

U 

U 

E 

E 

E 

E 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Iron 

7439-89-6 

CH2I 3158-00000 

18FEB1991 

E 

N 

Iron 

Iron 

Iron 

Iron 

lsophorone 

lsophorone 

lsophorone 

lsophorone 

lsophorone 

lsophorone 

7439-896 

7439-89-6 

7439-89-6 

7439-89-6 

78-59-1 

78-59-1 

78-59-1 

78-59-1 

78-59-1 

78-59-1 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH2I 3145-00000 

CH213155-00000 

CH213156-00000 

CH2 13157-00000 

CH213158-00000 

CH213159-00000 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

E 

E 

E 

E 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Page 137 of 176 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so




lsophorone 78-59-1 CH213160-DUP 18FEB1991 SO 3.90E+02 

U 

N 

lsophorone 

78-59-1 

CH213161-00000 18FEB1991 SO 

U 

N 

lsophorone 

78-59-1 

CH2 13162-00000 18FEB1991 SO 

U 

N 

Lead 

7439-92-1 

CH213145-00000 18FEB1991 so 

v\n\r 

N 

Lead 

7439-92-1 

CH213155-00000 18FEBI 991 SO 

N 

N 

Lead 

7439-92-1 

CH2 13156-00000 

18FEB1991 SO 

N 

N 

Lead 

7439-92-1 

CH213157-00000 18FEB1991 so 

NS 

N 

Lead 

Lead 

Lead 

7439-92-1 

7439-92-1 

7439-92-1 

CH213158-00000 

CH2I 3159-OW00 

CH2 13160-DUP 

18FEB1991 

18FEB1991 

18FEB1991 

SO 

SO 

SO 

N 

NW 

NW 

N 

N 

N 

Lead 

7439-92-1 

CH213161-00000 18FEB1991 SO 

NW 

N 

Lead 

7439-92-1 

CH213162-00000 18FEB1991 so 

NW 

N 

Magnesium 

7439-95-4 

CH213145-00000 18FEB1991 so 

N 

Magnesium 

7439 - 95 -4 

CH213155-00000 18FEB1991 SO 

N 

Magnesium 

Magnesium 

7439-95-4 

7439-95-4 

CH213156-00000 


18FEB1991 

18FEB1991 

SO 

SO 

B 

N 

N 

Magnesium 

7439-95-4 

CH2 13158-WOOO 

18FEB1991 SO 

B 

N 

Magnesium 

7439-95-4 

CH213159-00000 18FEBI 991 so 

B 

N 

Magnesium 

7439-95-4 

CH213160-DUP 18FEB1991 so 

B 

N 

Magnesium 

7439-95-4 

CH213161-00000 18FEB1991 so 

B 

N 

Magnesium 

Manganese 

Manganese 

Manganese 

Manganese 

7439-95-4 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 


18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

SO 

SO 

SO 

SO 

SO 

B 

N'E 

NE' 

'NE 

NE' 

N 

N 

N 

N 

N 

Manganese 

Manganese 

Manganese 

7439-96-5 

7439-96-5 

7439-96-5 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

18FEB1991 

18FEB1991 

18FEB1991 

SO 

SO 

SO 

NE' 

NE' 

NE' 

N 

N 

N 

Manganese 

7439-96-5 

CH213161-00000 18FEB1991 SO 

NE' 

N 

Manganese 

7439-96-5 

CH213162-WOO0 18FEB1991 so 

NE' 

N 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

SO 

SO 

SO 

SO 

SO 

SO 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

Mercury 

7439-97-6 

CH21316O-DUP 18FEB1991 SO 

U 

N 

Mercury 

7439-97-6 

CH213161-00000 18FEB1991 so 

U 

N 

Mercury 

7439-97-6 

CH213162-00000 18FEB1991 so 

U 

N 

Methoxychlor 

Methoxychlor 

Methoxychlor 

72-43-5 

72-43-5 

72-43-5 

CH213145-00000 

CH213155-00000 

CH2131 

18FEB1991 

18FEB1991 

18FEB1991 

SO 

SO 

SO 

U 

U 

U 

NT 

NT 

NT 

Methoxychlor 

72-43-5 

CH213157-00000 18FEB 1991 SO 

U 

NT 

Methoxychlor 

72-43-5 

CH213158-00000 18FEB1991 so 

U 

NT 

Methoxychlor 

72-43-5 

CH213159-00000 18FEBI 991 so 

U 

NT 

Methoxychlor 

72-43-5 

CH213160-DUP 18FEB1991 SO 

U 

NT 

Methoxychlor 

72-43-5 

CH213161 -oooOO 18FEB1991 SO 

U 

NT 

Methoxychlor 

72-43-5 

CH213162-00OOO 18FEB1991 so 

U 

NT 


75-09-2 

CH213145-00000 18FEB1991 SO 

UB 

N 


75-09-2 

CH213155-00000 18FEB1991 so 

B 

N 


75-09-2 

CH213156-00000 18FEB1991 so 

B 

N 





75-09-2 

75-09-2 

75-09-2 

75-09-2 

CH2 13157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

SO 

SO 

SO 

SO 

B 

B 

B 

B 

N 

N 

N 

N 


75-09-2 

CH213161-00000 18FEB1991 SO 

B 

N 


75-09-2 

CH213162-00000 18FEBl991 SO 

B 

N 

N-Nilrosodi-n-propylamine 621 -64-7 

CHZI 3145-00000 

18FEB1991 so 

U 

N 

N-Nilroso-di-n-propyhmine 

N-Nitroso-di-n-propyhrnine 

621 -64-7 

621-64-7 

CH213155-00000 

CHPI 31 

18FEBI 991 

18FEB1991 

SO 

SO 

U 

U 

N 

N 

N-Nitroso-di-n-propylarnine 621 -64-7 

CHZI 3157-00000 

18FEB1991 SO 

U 

N 

N-Nitroso-di-n-propylamine 62164-7 

CH213158-00000 18FEB1991 so 

U 

N 

N-Nilroso-di-n-propylamine 

N-Nilroso-di-n-propylamine 

N-Nilroro-di-n-propyhmine 

N-Nitroso-di-n-propybmine 

N-Nitrosodiphenyhmine 

N-Nitrosdiphenylamine 

N-Nitrosodiphenylamine 

N-Nitrosodiphen yhmine 

N-Nitrosdiphenylamine 

N-Nitrosodiphenyhmine 

621-64-7 

621-64-7 

621-64-7 

62164-7 

86-30-6 

86-30-6 

86-30-6 

86-30-6 

86-30-6 

86-30-6 

CH213159-00000 

CH213160-DUP 

CH213161-MX)o 

CH213162-00000 

CH213145-00000 

CH21 3155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 


18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

SO 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

Page 138 of 176




N-Nitrosodiphenylamine . . 

86-30-6 CH213160-DUP 18FEB1991 SO 3.90E+02 U 

CH2 13161 -00000 

N-Nitrosodiphenylamine 

N-Nlrosodiphenylamine 

Naphthalene 

Naphthalene 

Naphthalene 

Naphthalene 

Naphthalene 

Naphthalene 

Naphthalene 

Naphthalene 

Naphthalene 

Neptunium-237 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nitrobenzene 

Nitrobenzene 

Nitrobenzene 

Nitrobenzene 

Nitrobenzene 

Nitrobenzene 

Nitrobenzene 

Nitrobenzene 

Nitrobenzene 

PCB-1016 

PCB-1016 

PCB-1016 

PCB-1016 

PCB-I 016 

PCB-1016 

PCB-1016 

PCB-1016 

PCB-1016 

PCB-1221 

PCB-1221 

PCB-122 1 

PCB-1221 

PCB-1221 

PCB-1221 

PCB-1221 

PCB-I221 

PCB-1221 

PCB-1232 

PCB-1232 

PCB-1232 

PCB-1232 

PCB-1232 

PCB-1232 

PCB-1232 

PCB-1232 

PCB-1232 

PCB-1242 

PCB-1242 

PCB-1242 

PCB-1242 

PCB-1242 

PCB-1242 

PCB-1242 

PCB-1242 

PCB-1242 

PCB-1248 

PCB-1248 

PCB-1248 

PCB-1248 

PCB-I 248 

86-30-6 

86-30-6 

91-20-3 

91-20-3 

91-20-3 

91-20-3 

91-20-3 

91-20-3 

91-20-3 

91-20-3 

91-20-3 

13994-20-2 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

98-95-3 

98-95-3 

98-95-3 

98-95-3 

98-95-3 

98-95-3 

98-95-3 

98-95-3 

98-95-3 

12674-1 .2 

12674-1 -2 

12674-1 .2 

12674-1 .2 

12674-1 .2 

12674-11-2 

12674-11-2 

12674-11-2 

12674-11-2 

11104-28-2 

11104-28-2 

11104-28-2 

1 I 104-28-2 

11104-28-2 

11104-28-2 

11104-28-2 

11104-28-2 

11104-28-2 

11141 -16-5 

11141-16-5 

11141-16-5 

11141-16-5 

11141-16-5 

11141-16-5 

11141-16-5 

11141-16-5 

11141-16-5 

53469-21-9 

53469-21-9 

53469-21-9 

53469-21-9 

53469-21 -9 

52469-21-9 

53469-21-9 

53469-21-9 

53469-21-9 

12672-29-6 

12672-29-6 

12672-29-6 

12672-29-6 

12672-29-6 

CH21 3162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-MXX)O 

CH213162-00000 

CH21 3145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH223159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 


CH213157-00000 

~~2131 58-00000 

CH21 3159-00000 

CH213160-DUP 

CH213161-00000 

CH2I 3162-00000 



CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH2131 60-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH2 13158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 


CH213145-00000 

CH21315500000 

CH2 13156-00000 

CH213157-00000 

CH213158-00000 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FE61991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FE61991 

18FEB1991 

18FEB1991 

18FEB1991 

18FE61991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB 1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

I8FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBI 991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

Page 139 of 176 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

U 

J 

U 

U 

U 

U 

U 

U 

U 

U 

U 

B 

U 

B 

B 

B 

U 

B 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT




PCB-1248 12672-29-6 CH2 13159-00000 18FEB1991 SO 9.1 OE+01 U NT ug/kg 

PCB-1248 

PCB-1248 

PCB-1248 

PCB-1254 

PCB-1254 

PCB-1254 

PCB-1254 

PCB-1254 

PCB-1254 

PCB-1254 

PCB-1254 

PCB-1254 

PCB-1260 

PCB-1260 

PCB-1260 

PCB-1260 

PCB-1260 

PCB-1260 

PCB-1260 

PCB-1260 

PCB-1260 

Pentachlorophenol 









Phenanthrene 

Phenanthrene 

Phenanthrene 

Phenanthrene 

Phenanthrene 

Phenanthrene 

Phenanthrene 

Phenanthrene 

Phenanthrene 

Phenol 

Phenol 

Phenol 

Phenol 

Phenol 

Phenol 

Phenol 

Phenol 

Phenol 

Plutonium-239 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Pyrene 

Pyrene 

Pyrene 

Pyrene 

Pyrene 

Pyrene 

Pyrene 

Pyrene 

Pyrene 

Selenium 

Selenium 

Selenium 

Selenium 

12672-29-6 

12672-29-6 

12672-29-6 

11097-69-1 

11097-69-1 

11097-69-1 

11097-69-1 

11097-69-1 

11097-69-1 

11097-69-1 

11097-69-1 

11097-69-1 

11096-82-5 

11096-82-5 

11096-82-5 

11096-82-5 

11096-82-5 

11096-82-5 

11096-82-5 

11096-82-5 

11096-82-5 

87-86-5 

87-86-5 

87-86-5 

87-86-5 

87-86-5 

87-86-5 

87-86-5 

87-86-5 

87-86-5 

85-01-8 

85-01-8 

85-01-8 

85-01 -8 

85-01-8 

85-01-8 

85-01-8 

85-01-8 

85-01-8 

108-95-2 

108-95-2 

108-95-2 

108-95-2 

108-95-2 

108-95-2 

108-95-2 

108-95-2 

108-95-2 

15117-48-3 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

129-00-0 

129-00-0 

129-00-0 

129-00-0 

129-00-0 

129-00-0 

129-00-0 

129-00-0 

129-00-0 

7782-49-2 

7782-49-2 

na2-49-2 

778249-2 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 


CH213156-00000 

CH213157-00000 

CH213158-00000 

CH2 13159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH2 13145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-OOOM) 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 


CH213158-OOO00 

CH213159-00000 

CH213160-DUP 

CHZl3161-OOOOO 

CH213162-00000 

CH213145-00000 


CH213156-00000 


cn21315a00000 

CH213159-00000 

CH2 13160-DUP 

CHZ13161-00000 

CH213162-00000 

CH213145-00000 


CH213156-00000 

CH213157-00000 

CH21315a00000 

CH213159-00000 

CH2131 60-DUP 

CH213161 -OOO00 

CH213162-00000 

CH213145-00OOO 

CH213145-00000 

CH2 13155-00000 

CH213156-00000 

CH213157-00000 

cH21315a00000 

CH213159-00000 

CH21316O-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH2 13157-00000 

CH2 13158M)ooo 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-0oooO 

CH213155-00000 

CH2131 %-WOO0 

CH213157-00000 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

lSFEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

Page 140 of 176 

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so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

J 

U 

U 

U 

U 

U 

U 

U 

U 

J 

U 

U 

U 

U 

U 

U 

U 

U 

J 

U 

B 

B 

U 

U 

U 

U 

B 

U 

J 

J 

J 

J 

J 

J 

J 

J 

J 

BW 

U 

U 

U 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N




Selenium 7782-49-2 CH213158-00000 18FEB1991 SO O.OOE+OO 

U 

N mglKG 

Selenium 

Selenium 

Selenium 

Selenium 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Styrene 

Styrene 

Styrene 

Styrene 

Styrene 

Styrene 

Styrene 

Styrene 

Styrene 

Technetium99 








7782-49-2 

7782 2 

7782-49-2 

7782-49-2 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440 - 23- 5 

7440-23-5 

7440-23-5 

100-42-5 

100-42-5 

100-42-5 

100-42-5 

100-42-5 

100-42-5 

100-42-5 

100-42-5 

100-42-5 

14133-767 

I 27-18-4 

127-18-4 

i 27-18-4 

127-18-4 

127-18-4 

127-18-4 

i 27-18-4 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH2 13162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 


CH2I 3158-00000 

CH213159-00000 

CH2131 60-DUP 

CH213161-OOO00 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-MWXM 

CH213145-00000 

CH213145-00000 

CH213155-00000 

CH2 13156-MWXM 

CH213157-00000 

CH213158-00000 

CH2 13159-00000 

CH2 13160-DUP 

18FEB1991 

18FEB1991 

1 BFEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

1 OFEBI 991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

I 8FEBl991 

18FEBI 991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEBl991 

O.OOE+OO 

O.OOE+OO 

O.OoE+OO 

O.OOE+OO 

2.00E+00 

l.OOE+OO 

1.00E+00 

l.OOE+OO 

1.00E+00 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

2.20E+02 

2.28~+02 

2.45E+02 

1.81E+02 

2.52E+02 

2.11E+02 

i.a5~+02 

1.79€+02 

1.18E+02 

6.00E+00 

6.00E+00 

6.00€+00 

6.00€+00 

6.00E+00 

6.00E+00 

6.00€+00 

6.00€+00 

6.00E+00 

1.60E+02 7.24E+02 

6.00E+00 

6.00E+00 

6.00€+00 

6.00€+00 

6.00E+00 

6.00E+00 

6.00€+00 

U 

U 

U 

U 

B 

U 

U 

U 

U 

U 

B 

U 

U 

UB 

0 

B 

B 

B 

B 

B 

B 

B 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 



127-18-4 

127-18-4 

CH213161-00000 

CH213162-00000 

18FEB1991 

18FEB1991 

6.00€+00 

6.00€+00 

U 

U 

N 

N 

Thallium 

7440-28-0 

CH213145-00000 18FEB1991 I .00E+00 

UN 

N 

Thallium 

7440-28-0 

CH2 13155-OOOW 18FEBl991 

1 .WE+OO w N 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thorium-230 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toluene 

Toxaphene 

Toxaphene 

Toxaphene 

Toxaphene 

Toxaphene 

Toxaphene 

Toxaphene 

Toxaphene 

Toxaphene 


Trichbroeihene 

7440-250 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

14269-63-7 

108-88-3 

108-88-3 

I 08-88-3 

108-88-3 

I 08-88-3 

108-88-3 

108-88-3 

108-88-3 

ioa-aa-3 

8001-35-2 

8001-35-2 

8001-35-2 

8001-35-2 

8001 -35-2 

8001 -35-2 

8001-35-2 

8001-35-2 

8001 -35-2 

79-01-6 

79-01-6 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH2 13145-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH2 131 sMKK)oo 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH2131 6QDUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

l8FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

1 BFEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl 991 

18FEBl991 

I 8FEB1991 

1.00E+00 

1 .00E+00 

1.00E+00 

I.WE+OO 

I.WE+W 

1.00E+00 

1 .00E+00 

5.20€+02 4.00E+01 

6.00E+00 

6.00E+00 

6.00€+00 

6.00€+00 

6.00€+00 

6.00€+00 

6.00€+00 

6.00€+00 

6.00E+00 

2.00E+02 

I .90E+02 

1.90E+02 

I .70E+02 

1.70E+02 

i .a0~+02 

I .90E+02 

I .80~+02 

I .90E+02 

l.WE+OO 

I.WE+W 

UN 

UN 

UNW 

UN 

UN 

UMN 

UWN 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

N 

N 

Page 141 of 176 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so




Trichloroethene 79-01-6 CH213156-00000 18FEB1991 SO 1.00€+00 U N 







Uranium234 

Uranium235 

Uranium238 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vinyl Acetate 

Vinyl Acetate 

Vinyl Acetate 

Vinyl Acetate 

Vinyl Acetate 

Vinyl Acetate 

Vinyl Acetate 

Vinyl Acetate 

Vinyl Acetate 










Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Xylene 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

alpha-BHC 

alpha-BHC 

alpha-BHC 

alpha-BHC 

alpha-BHC 

alpha-BHC 

alpha-BHC 

alpha-BHC 

alpha-BHC 

alphachlordane 

alphachlordane 

alpha-Chlordane 






79-01 -6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

13966-29-5 

15117-96-1 

24678-82-8 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

108-05-4 

I 0805-4 

108-05-4 

108-05-4 

ioao5-4 

108-05-4 

108-05-4 

108-05-4 

108-05-4 

75-01-4 

75-01-4 

75-01-4 

75-01-4 

75-01-4 

75-01-4 

75-01-4 

75-01-4 

75-01-4 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

319-84-6 

319-84-6 

319-84-6 

319-84-6 

319-84-6 

319-84-6 

319-84-6 

319-84-6 

319-84-6 

5103-71-9 

5103-7 1-9 

5103-71-9 

5103-7 1-9 

5103-71 -9 

5103-71 -9 

5103-71 -9 

5103-71 -9 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH21316O-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213145-00000 

CH213145-00000 

CH213145-00000 

CH213155-00000 

CH2I 3156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH2 13160-DUP 

CH2 13161 -00000 

CH213162-00000 

CH213145-00000 

CH2 13155-00000 

CH213156-00000 

CH21 3157-00000 

CH213158-00000 

CH2 13159-~00 

CH2 13160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155MHMO 

CH213156-00000 

CH21 3157-00000 

CH213158-00000 

CH213159-00000 

CH2131 60-DUP 

CH213161 -00000 

CH213162-OW00 

CH213145-00000 

CH213155-00000 

CH2 13156-oooO 

CH213157-00000 

CH2 131580oWO 

CH2 13159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-000OO 

CH213159-00000 

CH213160-DUP 

CH213161-00OOO 

CH213162-OWOO 

CH213145-00000 

CH213155-oMxK) 

CH213156-oMxK) 

CH213157-000(W 

CH21315800000 


CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH2 13145M)o 

CH2 13155-00000 

CH213156-000OO 

CHZl3157-OOOOO 

CH21315800000 

CH213159-00000 

CH2131 60-DUP 

CH213I 61 -00000 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

I SFEBI 991 

18FEB1991 

18FEB1991 

18FEB1991 

1 OFEBI 991 

1 SFEBI 991 

18FEB1991 

18FEBI 991 

18FEBl991 

18FEBl991 

lSFEBl991 

18FEB1991 

lSFEB1991 

lSFEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

I8FEB1991 

18FEB1991 

-16FEB1991 

18FEBl991 

18FEBl991 

ISFEBI991 

I 8FEB 1991 

18FEBl991 

1 SFEBI 991 

18FEB1991 

18FEBl991 

18FEB1991 

1 SFEBI 991 

18FEB1991 

18FEB1991 

18FEBI991 

Page 142 of 176 

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SO 

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so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

SO 

SO 

so 

so 

so 

so 

so 

so 

so 

SO 

so 

so 

so 

so 

so 

so 

so 

so 

so 

SO 

so 

so 

so 

so 

so 

50 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

1.90E+02 6.00E+01 

1.50E+01 1.50€+01 

2.50E+02 6.00E+01 

1.80E+01 

1.60E+01 

1.70€+01 

1.50E+01 

1.50E+01 

2.70E+01 

3.30E+01 

1.60E+01 

1.90E+01 

1.20E+01 

1.20E+01 

l.lOE+Ol 

1.20E+01 

l.lOE+Ol 

I .20E+Ol 

I .20E+01 

1.20E+01 

l.lOE+Ol 

I .00E+00 

1.00€+00 

l.WE+OO 

1 .WE+00 

l.OOE+OO 

I .WE+00 

I .00E+00 

l.OOE+OO 

I .WE+OO 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 


3.20E+01 

1.3OE+OI 



5.00E+00 

5.00E+00 

9.00E+00 

9.00E+00 

l.WE+Ol 

9.00E+00 

1.00E+Ol 

9.OoE+80 

9.00E+00 

9.00E+00 

9.00E+00 

9.00E+00 

9.00E+W 

9.80E+01 

9.30E+01 

9.60E+01 

8.70E+01 

8.60E+01 

9.10E+01 

9.30E+01 

8.90E+01 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

B 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT




alpha-Chlordane 5103-71-9 CH213162-00000 18FEB1991 SO 9.30E+01 

U NT uglkg 

beta-BHC 

beta-BHC 

beta-BHC 

beta-BHC 

beta-BHC 

beta-BHC 

beta-BHC 

beta-BHC 

beta-BHC 

bis(2-Chloroethoxy)methane 



bis(2-Chloroe1hoxy)methane 

bis(2-Ch1oroethoxy)methane 



bs(2-Chloroethoxy)methane 


bis(2-Ch1oroethyl)ether 

bis(26hloroethyl)ether 



bis(2-Ch1oroethyl)elher 





bs(2-ChloroisopropyI)ether 

bis(2-ChloroisopropyI)ether 

bis(2-Chloroisopropyl)elher 

bis(2-Chloroisopropyl)ether 



bis(2-Chloroisopropyl)t?ther 




bs(2-Ethylhexyl)phthalale 



bs(2-Ethy1hexyl)phthalate 



bis(2-Ethy1hexyI)phthalate 


cis-I ,3-Dichloropropene 


cis-I .3-Dichloropropene 



cis-1.3-Dichloropropene 




delta-BHC 

delta-BHC 

delta-BHC 

delta-BHC 

delta-BHC 

delta-BHC 

delta-BHC 

delta-BHC 

delta-BHC 

gamma-BHC(Lindane) 






garnma-BHC(Lindane) 


319-85-7 

319-85-7 

319-85-7 

319-85-7 

319-85-7 

319-85-7 

319-85-7 

319-85-7 

319-85-7 

111-91-1 

1 I 1-91 -1 

111-91-1 

111-91-1 

111-91-1 

111-91-1 

111-91-1 

111-91-1 

111-91-1 

111-44-4 

111-44-4 

111-44-4 

111-44-4 

111-44-4 

111-44-4 

111-44-4 

111-44-4 

111-44-4 

108-60- 1 

108-60-1 

108-60-1 

108-60-1 

10860-1 

108-60-1 

108-60-1 

108-60-1 

108-60-1 

117-81-7 

117-81 -7 

117-81-7 

117-81-7 

117-81 -7 

117-81 -7 

117-81 -7 

117-81-7 

117-81-7 

10061 -01-5 

10061 -01-5 

10061-01-5 

10061-01 -5 

10061-01-5 

10061-01-5 

10061 -01-5 

10061-01-5 

10061 -01-5 

319-86-8 

319-86-8 

319-86-8 

319-86-8 

319-86-8 

319-86-8 

319-86-8 

319-86-8 

319-86-8 

58-89-9 

58-89-9 

58-89-9 

58-89-9 

58-89-9 

58-89-9 

58-89-9 

5889-9 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH2 13157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213 159-00000 

CH213160-DUP 

CH2 13161 -00000 

CH213162-00000 

CH213145-00000 

CH2 13155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH2I 3159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-OW00 

CH213155-00000 

CH213156-0OO00 

CH2I 3157-ooOO0 

CH213158-00000 

CH213159-00000 

CH2131 60-DUP 


CH213162-00000 

CH213145-WOO0 

CH213155-00000 

CH213156-WOO0 

CH213157-WOO0 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH2 13145-WOO0 

CH213155-WOO0 

CH213156-00000 

CH213157-00000 

CH213158-ooOO0 

CH213159-00000 

CH21316O-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-00000 

CH2 13156-00000 

CH213157-00000 


CH213159-00000 

CH213160-DUP 

CH213161-00000 

CH213162-00000 

CH213145-00000 

CH213155-WOO0 

CH2I 3156-WWO 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH21316O-DUP 

CH213161-00000 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

16FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

UJB 

JB 

JB 

JB 

JB 

JB 

JB 

JB 

JB 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

NT 

Page 143 of 176 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so




gamrna-BHC(Lindane) 58-89-9 CH213162-00000 18FEB1991 SO 9.00E+00 U NT 

gamma-Chlordane 



gamrna-Chlordane 





gamrna-Chlordane 

trans-1.3-Dichloropropene 





trans-I .3-Dichloropropene 




WAG 7, SWU 8. MWI 84 




1 ,I,2.2-Tetrachloroethane 

1 ,I.2.2-Tetrachloroethane 

1 ,I.2.2-Tetrachloroethane 



1,1.2-Trichloroethane 









1.2 .4-Trichlorobenzene 

1.2 .4-Trichlorobenzene 

1.2 .CTrichlorobenzene 






1 .Z-Dichloroethane 

1.2-Dchloroethene 

1.2-Dehloroethene 

1 .2-Dichloroethene 











2.4,5-Trichlorophenol 

2.4,5-Trichlorophenol 



2.4 .6-Tric hlorop henol 

2 ,4-Dichlorophenol 


2.4-Dchlorophenol 

2 .CDimethylphenol 



2.4-Dinitrophenol 

2 .CDinitrophenol 

5103-74-2 

5103-74-2 

5103-74-2 

5103-74-2 

5103-74-2 

5103-74-2 

5103-74-2 

5103-74-2 

5103-74-2 

10061-02-6 

10061-02-6 

10061 -02-6 

10061-02-6 

10061 -02-6 

10061-02-6 

10061-02-6 

10061 -02-6 

10061 -02-6 

71 -55-6 

71-55-6 

71-55-6 

79-34-5 

79-34-5 

79-34-5 

79-00-5 

79-00-5 

79-00-5 

75-34-3 

75-34-3 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

75-35-4 

75-35-4 

120-82-1 

120-82-1 

120-82-1 

95-50-1 

95-50-1 

95-50-1 

107-06-2 

107-06-2 

107-06-2 

540-59-0 

540-59-0 

540-59-0 

78-87-5 

78-87-5 

78-87-5 

541 -73-1 

541 -73-1 

541-73-1 

106-46-7 

106-46-7 

106-46-7 

95-95-4 

95-95-4 

95-95-4 

88-06-2 

88-06-2 

88-06-2 

12083-2 

120-83-2 

120-83-2 

105-67-9 

10567-9 

105-67-9 

51-28-5 

51-28-5 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH2 13160-DUP 

CH213161-00000 

CH2 13162-00000 

CH213145-00000 

CH213155-00000 

CH213156-00000 

CH213157-00000 

CH213158-00000 

CH213159-00000 

CH213160-DUP 

CH2 13161 -00000 

CH213162-00000 

CH2 10144-00000 

CH2 10223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-ooOo0 

CH210224-DUP 

6028-92 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

6028-92 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CHZ10144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH2 10144-00000 

CH210223-OW00 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH21014e00000 

CH210223-00000 

CH21022CDUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144MKxx) 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH2 I01 4400000 

CH21022300000 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

l8FEBl 991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEBl991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEB1991 

18FEBl991 

18FEB1991 

1 8FEB1 991 

03APRI 991 

03MAY1991 

03MAY 1991 

03APR1991 

O3MAY 1991 

03MAY I991 

03APR1991 

03MAY I991 

03MAYI991 

1 9OCTl 992 

03APRl991 

03MAYl991 

03MAY 1991 

19OCTl992 

03APRl991 

03MAY 199 1 

03MAYl991 

03APR1991 

03MAYl991 

03MAYl991 

O3APRl 991 

03MAYl991 

03MAY1991 

03APR1991 

03MAY1991 

03MAYl991 

O3APR1991 

03MAY1991 

OMAYl991 

03APR1991 

03MAY1991 

03MAY 1991 

03APRl991 

03MAYl991 

03MAY 1991 

03APRl991 

03MAYI 991 

03MAYI99I 

03APR1991 

03MAYl991 

03MAYl991 

03APR1991 

03MAY 1991 

03MAYI991 

03APR1991 

03MAY1991 

03MAY 1991 

03APRI 991 

O3MAYlDDl 

03MAY1991 

03APR1991 

03MAYl991 

Page 144 of 176 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

so 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

9.80E+01 

9.30E+01 

9.60E+01 

8.70E+01 

8.60E+01 

9.10E+01 

9.30E+01 

8.90E+01 

9.30E+01 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

6.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.WE+OO 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.OOE+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

l.lOE+Ol 

I .00E+01 

1.00E+01 

1.10E+01 

1.00E+01 

1 .00E+01 

5.00E+00 

5.00E+00 

B.WE+W 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00€+00 

5.00E+00 

l.lOE+01 

1 .00E+01 

1 .00E+01 

l.lOE+Ol 

1.00E+Ol 

I.WE+Ol 

5.50E+01 

5.00E+01 

5.00E+O1 

l.lOE+Ol 

1.00E+01 

l.OOE+Ol 

l.lOE+Ol 

1 .00E+01 

1.00E+01 

l.lOE+Ol 

1.00E+01 

1 .00E+01 

5.50E+OI 

5.00E+OI 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

< 

U 

U 

U 

< 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U




2,CDinitrophenol 51-28-5 CH210224-DUP 03MAY1991 WG 5.00E+01 U UdL 

2 ,4-Dinitroioluene 






2-Butanone 

121-14-2 

121 -14-2 

121-14-2 

606-20-2 

606-20-2 

606-20-2 

78-93-3 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210I 44-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

OJAPR1991 

03MAY1991 

03MAYl991 

03APRI 991 

03MAYl991 

03MAYl991 

O3APRl 991 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

1.10E+01 

1.00E+01 

1.00E+01 

l.lOE+Ol 

l.OOE+Ol 

l.OOE+Ol 

l.OOE+Ol 

U 

U 

U 

U 

U 

U 

U 

R 

UilL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

2-Butanone 

2-Butanone 







2-Hexanone 

2-Hexanone 

2-Hexanone 




2-Melhylphenol 






2-Nitrophenol 

2-Nitrophenol 

2-Nitrophenol 



78-93-3 

78-93-3 

91-58-7 

91-58-7 

91-58-7 

95-57-8 

95-57-8 

95-57-8 

591 -78-6 

591-78-6 

591-78-6 

91-57-6 

91-57-6 

91-57-6 

95-48-7 

95-48-7 

95-48-7 

88-74-4 

88-74-4 

88-74-4 

8875-5 

88-75-5 

88-75-5 

91 -94-1 

91-94-1 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH2 10223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH2 10224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH2101 44-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

O3MAY 1991 

OJMAY 1991 

03APRl991 

O3MAY 1991 

O3MAY 1991 

03APRl991 

03MAYl991 

03MAY1991 

03APRl991 

03MAY I991 

03MAY1991 

03APRI991 

OMAY 1991 

03MAY1991 

O3APRl 991 

03MAY I991 

03MAY 1991 

03APR 1991 

03MAY1991 

03MAY1991 

03APR1991 

03MAY1991 

03MAYI 991 

03APRl991 

03MAY I991 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

l.OOE+OI 

l.OOE+Ol 

l.lOE+Ol 

l.OOE+Ol 

l.OOE+OI 

I.lOE+OI 

l.OOE+OI 

l.OOE+Ol 

1.00E+01 

1.00E+01 

l.OOE+OI 

l.lOE+Ol 

1 .00E+01 

l.OOE+Ol 

l.lOE+Ol 

l.OOE+OI 

l.OOE+OI 

5.5OE+O1 

5 .OOE+O 1 

5.00E+01 

l.lOE+Ol 

1 .OOE+OI 

l.OOE+Ol 

2.20€+01 

2.00E+01 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

uglL 

ug1L 

uglL 

uglL 

uglL 

ug/L 

uglL 

uglL 

uglL 

ugn 

u9R 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ugfl 

ugR 

uglL 

uglL 

uglL 

uglL 

uglL 

3,3’-Dichlorobenzidine 91-94-1 

CH210224-DUP 03MAYI991 WG 2.00E+01 

U 

Ug/L 


99-09-2 

CH210144-00000 03APR1991 WG S.SOE+OI 

U 

uglL 



99-09-2 

99-09-2 

CH210223-00000 

CH210224-DUP 

03MAYl991 

03MAYl991 

WG 

WG 

5.00E+01 

5.00E+01 

U 

U 

uglL 

ugfl 

4,6-Dinitro-2-methylphenol 534-52-1 

CH2lOi 44-00000 03APRI 991 WG 5.50E+01 

U 

uglL 


4,6-Dinlro-2-methylphenol 


534-52-1 

53452-1 

101-55-3 

CH210223-00000 

CH210224DUP 

CH210144-00000 

03MAY1991 

03MAYl991 

03APRl991 

WG 

WG 

WG 

5.00E+01 

5.00€+01 

l.lOE+OI 

U 

U 

U 

ugR 

ugk 

ug/L 

4-Bromophenyl-phenylether 101-55-3 

CH2 10223-~003MAYI991 

WG 1.00E+01 

U 

ugfl 


4-Chloro-3-met hylphenol 





CChloroaniline 

4-Chlorophen yl-phenylether 

4-Chlorophenyl-phen ylelher 


Methyl-2-pentanone 

4-Melhyl-2-pentanone 





QNitroaniline 



4-Nitrophenol 

4-Nitrophenol 

4-Nitrophenol 

101 -55-3 

59-50-7 

59-50-7 

59-50-7 

106-47-8 

106-47-8 

106-47-8 

7005-72-3 

7005-72-3 

7005-72-3 

108-10-1 

108-10-1 

108-10-1 

106-44-5 

106-44-5 

10644-5 

100-01 -6 

100-01-6 

100-01-6 

100-02-7 

100-02-7 

100-02-7 

CH210224DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH21014400000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH2 10223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH2 1014440000 

CH210223-00000 

CH210224-DUP 

03MAY1991 

03APR 1991 

03MAYl991 

03MAY1991 

O3APRl99l 

03MAY1991 

03MAY 1991 

03APR1991 

03MAY1991 

OWY1991 

03APRl991 

03MAYI 991 

03MAY1991 

03APRl991 

03MAY1991 

03MAY1991 

03APRl991 

03MAY1991 

03MAYl991 

03APR1991 

03MAYl991 

03MAY I99 1 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

I .00E+01 

l.lOE+Ol 

I .OOE+OI 

I .00E+01 

l.lOE+Ol 

1 .00E+01 

1.00E+01 

l.lOE+OI 

1.00E+01 

1.00E+01 

1.00E+01 

l.WE+OI 

1.00E+01 

I .10E+01 

1.00E+01 

l.OOE+OI 

5.50E+01 

5.00E+01 

5.00E+Ol 

5.50E+01 

5.00E+OI 

5.00E+01 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ug1L 

uglL 

uglL 

ug1L 

uglL 

uglL 

uglL 

Acenaphthene 

83-32-9 

CH21 0144-00000 

03APR1991 WG l.IOE+OI 

U 

ugfl 

Acenaphthene 

Acenaphthene 



83-32-9 

83-32-9 

208-96-8 

208-96-8 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

03MAY 1991 

03MAY I99 1 

03APR1991 

03MAY1991 

WG 

WG 

WG 

WG 

1 .OOE+OI 

I .00E+01 

l.lOE+Ol 

1.00E+01 

U 

U 

U 

U 

uglL 

ugfl 

uglL 

uglL 

Acenaphthykne 

208-96-8 

CH210224-DUP 03MAY1991 WG 1 .00E+01 

U 

ugfl 

Acetone 

67-64-1 

CH21014400000 03APRl991 WG 1.70€+01 

UB 

J 

ugfl 

Acetone 

67-64-1 

CH21022500000 03MAYI 991 WG 1.50E+01 

UB 

JB 

ugfl 

Page 145 of 176




Acetone 67-64-1 CH210224-DUP 03MAY1991 WG 1.20E+01 UB JB uglL 

Alkalinity 

Alkalinity 

Alkalinity 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum 

Aluminum, Dissolved 

Aluminum, Dissolved 

Anthracene 

Anthracene 

Anthracene 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 

Antimony 




Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 

Arsenic 




Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 

Barium 



Barium, dissolved 

Benzene 

Benzene 

Benzene 









Benzo(b)Ruoranthene 







Benzoic Acii 

471-34-1 

471-34-1 

471-34-1 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

120-12-7 

120-12-7 

120-12-7 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

7440-39-3 

71-43-2 

71-43-2 

71-43-2 

56-55-3 

56-55-3 

56-55-3 

50-32-8 

50-32-8 

50-32-8 

205-99-2 

20599-2 

20599-2 

191-24-2 

191 -24-2 

191-24-2 

207-08-9 

207-08-9 

207-06-9 

65-85-0 

4097-92 

4821-94 

5569 - 93 

4097-92 

4686-92 

4821 -94 

5569-93 

6028-92 

CH210144-00000 

CH210144-DIS 

CH210223-DIS 

CH210224-DUPDI 

4821-94 

5569-93 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

4686-92 

4821-94 

5569-93 

6028-92 

CH210144-00000 

CH210144-DIS 

CH210223-DIS 


4097-92 

4821-94 

5569-93 

4097-92 

4686-92 

4821-94 

5569-93 

6028-92 


CH210144-DIS 

CH210223-DIS 


4097-92 

4821-94 

5569-93 

4097-92 

4686-92 

4821 -94 

5569-93 

6028-92 

CH210144-00000 

CH210144-DIS 

CH210223-DIS 


4821-94 

5569-93 

4097-92 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH21014e00000 

CH210223-00000 

CH2 10224-DUP 

CH21014400000 

CH2 10223-00000 

CH210224-DUP 


CH210223-00000 

CH2 10224DUP 


CH210223-00000 

CH210224-DUP 

CH21014400000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

31JAN1992 

14MAR1994 

23JUN1993 

31JAN1992 

3OMAR1992 

14MAR1994 

23JUNl993 

190CT1992 

03APR1991 

03APR1991 

03MAY1991 

03MAY1991 

14MAR1994 

23JUNl993 

03APRl991 

03MAYl991 

03MAYl991 

30MAR1992 

14MAR1994 

23JUNl993 

19OCTl992 

03APRl991 

03APRl991 

03MAY1991 

03MAY 1991 

31 JAN1992 

14MAR 1994 

23JUN1993 

31JAN1992 

3OMAR1992 

14MAR1994 

23JUNl993 

190CT1992 

03APR1991 

03APRl991 

03MAY1991 

03MAYl991 

31JANl992 

14MAR1994 

23JUN1993 

3lJANl992 

3oMAR1992 

14MAR1994 

23JUN1993 

190CT1992 

03APR1991 

03APR1991 

03MAY1991 

03MAY 1991 

14MARl994 

23JUN1993 

31JAN1992 

03APRl991 

03MAY 1991 

03MAYl991 

03APRl991 

03MAYl991 

03MAYl991 

03APR1991 

03MAY 1991 

03MAY 1991 

03APRI991 

03MAY 1991 

03MAYl991 

O3APR 1991 

03MAY1991 

03MAY 1991 

03APRl991 

03MAY 199 1 

03MAYl991 

03APR1991 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

\M3 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

5.40E+02 

2.70E+02 

5.52E+02 

l.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

2.30E+01 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

l.lOE+Ol 

l.OOE+Ol 

l.OOE+Ol 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

0.00E+00 

O.OOE+OO 

0.00E+00 

0.00E+00 

O.OOE+OO 

0.00E+00 

0.00E+00 

0.00E+00 

0.00E+00 

O.OOE+OO 

0.00E+00 

0.00E+00 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

0.00E+00 

O.WE+W 

O.WE+W 

0.00E+00 

0.00E+00 

0.00E+00 

O.OOE+W 

O.WE+OO 

0.00E+00 

0.00E+00 

5.00E+00 

S.OOE+OO 

5.00E+OO 

l.lOE+Ol 

l.WE+Ol 

l.OOE+Ol 

1.10E+01 

l.OOE+Ol 

1 .00E+01 

l.lOE+Ol 

1 .OOE+01 

1.00E+Ol 

l.lOE+Ol 

1.00E+01 

l.OOE+Ol 

l.lOE+Ol 

1 .WE+Ol 

l.WE+Ol 

5.50E+01 

E 

UE 

U' 

U' 

U 

U 

U 

< 

< 

< 

< 

U 

U 

UN 

UN 

< 

< 

< 

BNS 

BNS 

BWN 

BWN 

E 

BE 

B 

B 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

N 

H 

N 

N 

N 

H 

H 

N 

JE 

E 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

H 

N 

N 

JBNS 

JBNS 

JBWN 

JBW 

N 

N 

N 

N 

N 

H 

H 

N 

JE 

JBE 

B 

B 

N 

N 

N 

Page 146 of 176




Benzoic Acid 65-85-0 CH210223-00000 03MAY1991 WG 5.00E+01 U uglL 

Benzoic Acid 







Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 

Beryllium 




Bismuth 

Bismuth 

Bismuth 

Bismuth, Dissolved 




Bromoform 

Bromoform 

Bromoform 

Bromomethane 

Bromomethane 

Bromomethane 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 




Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 




Calcium.Dissolved 







Chloride 

Chloride 

Chloride 

Chloride 

Chloride 

Chloride 

Chlorobenzene 

Chlorobenzene 

65-85-0 

100-51-6 

100-51 -6 

100-51 -6 

85-68-7 

85-68-7 

85-68-7 

7440-41 -7 

7440-41 -7 

7440-41 -7 

7440-41 -7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41-7 

7440-41 -7 

7440-69-9 

7440-69-9 

7440-69-9 

7440-69-9 

75-27-4 

75-27-4 

75-27-4 

75-25-2 

75-25-2 

75-25-2 

74-83-9 

74-83-9 

74-83-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

744043-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

75-15-0 

75-15-0 

75-15-0 

56-23-5 

56-23-5 

56-23-5 

16887-00-6 

16887-00-6 

16887-00-6 

16887-00-6 

16887-00-6 

16887-00-6 

108-90-7 

108-90-7 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

4097-92 

4686-92 

4821-94 

5569-93 

6028-92 

CH210144-00000 

CH2 10144-DIS 

CH2 10223-DIS 


4097-92 

4821-94 

5569-93 

4097-92 

4686-92 

6028-92 

4097-92 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH2 10223-00000 

CH2 10224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

4097-92 

4686-92 

4821-94 

5569-93 

6028-92 


CH210144-DIS 

CH210223-DIS 


4097-92 

4821-94 

5569-93 

4097-92 

4686-92 

4821-94 

5569-93 

6028-92 

CH210144-00000 

CH210144-DIS 

CH210223-DIS 

CH2I 0224-DUPDI 

4097-92 

4821 -94 

5569-93 

4821 -94 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224DUP 

4097-92 

4821-94 

5569-93 

CH21014400000 

CH210223-00000 

CH210224DUP 

CH210144-00000 

CH210223-00000 

O3MAY 1991 

03APR1991 

03MAY 1 991 

O3MAY 1991 

03APR1991 

O3MAY 1991 

03MAY 1991 

31 JANl 992 

3OMAR1992 

14MAR1994 

23JUN1993 

190CT1992 

03APRl991 

03APR1991 

03MAY1991 

03MAY1991 

31 JAN1992 

14MAR1994 

23JUN1993 

31 JANl 992 

30MAR1992 

190CT1992 

31 JANl 992 

03APRl991 

03MAY 1991 

03MAY1991 

03APRl991 

03MAYl991 

03MAYl991 

03APRI 991 

03MAY 1991 

03MAYI 991 

31 JANl 992 

3OMAR1992 

14MARl994 

23JUN1993 

190CTl992 

O3APRl 991 

O3APRl 991 

03MAY 1991 

03MAY I991 

31 JAN1992 

14MAR1994 

23JUN1993 

31JAN1992 

30MAR1992 

14MAR1994 

23JUN1993 

190CT1992 

03APR1991 

03APR1991 

03MAY1991 

03MAY 1991 

31JAN1992 

14MAR1994 

23JUN1993 

14MAR1994 

O3APRl 99 1 

03MAY 1991 

O3MAY1991 

03APRl991 

03MAY1991 

03MAY1991 

31 JANl 992 

14MAR1994 

23JUN1993 

03APR199 1 

03MAY 1991 

03MAY1991 

03APR1991 

03MAYi991 

Page 147 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

wc, 

WG 

WG 

WG 

WG 

wc, 

WG 

wc, 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

wc, 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

VIII; 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

\NG 

WG 

5.00E+01 

1.10E+01 

l.OOE+Ol 

l.OOE+Ol 

l.IOE+Ol 

l.OOE+Ol 

l.OOE+Ol 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00€+00 

0.00€+00 

5.00E+00 

5.00€+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00€+00 

l.OOE+Ol 

l.OOE+Ol 

I .00€+01 

0.00E+00 

0.00€+00 

0.00€+00 

0.00E+00 

0.00€+00 

0.00€+00 

0.00E+00 

0.00E+00 

0.00E+00 

0.00E+00 

0.00E+00 

0.00E+00 

1.15E+02 

1.09E+02 

1.26E+02 

1.18E+02 

9.80E+01 

2.12E+02 

2.09E+02 

I .85E+02 

1.82E+02 

1.14E+02 

1.39€+02 

1.17€+02 

1.39E+02 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+OO 

5.00€+00 

1.40E+OI 

7.00€+00 

8.00E+00 

I .60€+01 

1.60€+01 

1.60€+01 

5.00E+00 

5.00€+00 

U 

U 

U 

U 

U 

U 

U 

C 

< 

C 

< 

C 

B 

U 

U 

U 

< 

C 

C 

< 

< 

C 

< 

U 

U 

U 

U 

U 

U 

U 

U 

U 

c 

C 

< 

< 

U 

U 

U 

U 

< 

C 

E 

E 

U 

U 

N 

N 

N 

B 

N 

N 

H 

N 

N 

N 

N 

N 

N 

H 

H 

N 

JE 

JE 

N 

N 

N 

N 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ug1L 

mg1L 

mg1L 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mg/L 

mg1L 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

ugfl 

uglL 

uglL 

uglL 

ug1L 

uglL 

uglL 

uglL 

uglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mgk 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgk 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

ug1L 

uglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mglL 

mgk 

mglL 

uglL 

ugfl




Chlorobenzene 10890-7 CH210224-DUP 03MAY1991 WG 5.00E+00 U uglL 

Chloroethane 

Chloroethane 

Chloroethane 

Chloroform 

Chloroform 

Chloroform 

Chloromethane 

Chloromethane 

Chloromethane 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 




Chrysene 

Chrysene 

Chrysene 

Cobalt 

Cobalt 

Coban 

Cobalt 

Cobalt 

Cobalt 

Coban 

Cobalt 

Cobalt 




Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

copper 




Cyanide 

Cyanide 

Cyanide 

Cyanide 

Cyanide 

Cyanide 












Di-noctylphthalale 



Dibenzo(a,h)anlhracene 



Dibenzofuran 

Dibenzofuran 

75-00-3 

75-00-3 

75-00-3 

67-66-3 

67-66-3 

67-66-3 

74-87-3 

74-87-3 

74-87-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

216-01 -9 

218-01-9 

218-01-9 

7440-48-4 

7440-48-4 

7440-48-4 

7440-48-4 

7440-4a-4 

744048-4 

7440-48-4 

740-48-4 

7440-48-4 

7440-484 

7440-4a-4 

7440-484 

7440-50-8 

7440-50-8 

740-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

57-12-5 

57-12-5 

57-12-5 

57-12-5 

57-12-5 

57-12-5 

DTW 

DTW 

DTW 

DTW 

DTW 

DTW 

DTW 

DTW 

84-74-2 

84-74-2 

04-74-2 

117840 

117-84-0 

117840 

53-70-3 

53-70-3 

53-70-3 

132-64-9 

132-64-9 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

4686-92 

4821 -94 

5569-93 

6028-92 

CH210144-00000 

CH210144-DIS 

CH2 10223-DIS 


4097-92 

4821-94 

5569-93 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

4097-92 

4686-92 

4821-94 

5569-93 

6028-92 

CH2I 0144-OoooO 

CH210144-DIS 

CH210223-DIS 

CH2 10224-DUPD I 

4097-92 

4821 -94 

5569-93 

4686-92 

4821-94 

5569-93 

6028-92 

CH210144-00000 

CH210144-DIS 

CH210223-DIS 


4097-92 

4821-94 

5569-93 

CH210144-00000 

CH210144-00000 

CH210223-00000 

CH210223-DIS 

CH210226DUP 


4686-92 

4821-94 

5569-93 

5877-94 

6028-92 

6703-94 

6796-93 

7756-93 

CH21014440000 

CH210223-00000 

CH210224-DUP 

CH21014400000 

CH21022J-00000 

CH210224DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

03APR1991 

OMAY 1991 

03MAY1991 

03APR1991 

O3MAYl 991 

03MAY1991 

03APR1991 

03MAY1991 

03MAY1991 

30MAR1992 

14MAR1994 

23JUNl993 

190CT1992 

03APRI 991 

03APR1991 

O3MAY I991 

03MAY1991 

3lJAN1992 

14MAR1994 

23JUN1993 

03APR1991 

03MAY 1991 

OWY1991 

31 JAN1 992 

30MAR1992 

14MARI 994 

23JUN1993 

190CT1992 

O3APR 1991 

O3APRl 991 

OMAY 1991 

03MAYI 991 

31JAN1992 

14MAR1994 

23JUN1993 

30MAR1992 

14MAR1994 

23JUN1993 

190CT1992 

03APRl991 

O3APRl 991 

03MAY 1991 

OjMAYl991 

31 JAN1992 

14MAR1994 

23JUN1993 

03APR 1991 

03APR1991 

03MAY 1991 

03MAYl991 

03MAYI 991 

03MAY1991 

3OMARI 992 

14MAR1994 

23JUNl993 

29JUN1994 

190CT1992 

O6SEP1 994 

21SEP1993 

08DECl993 

O3APRI991 

OJMAYI99I 

OWY I991 

03APRI 991 

03MAY I991 

OWYl991 

03APR1991 

OWAYI 991 

03MAYl991 

03APR1991 

03MAY 1991 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

U 

U 

U 

U 

U 

U 

U 

U 

U 

< 

c 

< 

< 

U 

U 

U 

< 

< 

< 

U 

U 

U 

< 

< 

< 

< 

< 

B 

B 

B 

B 

< 

< 

< 

< 

< 

< 

< 

UN 

UN 

U 

U 

< 

< 

< 

U 

U 

U 

U 

U 

U 

UJB 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

N 

N 

N 

N 

N 

N 

N 

H 

N 

N 

N 

N 

Page 148 of 176




Dibenzofuran 132-64-9 CH210224-DUP 03MAY1991 WG 1.00E+01 U ug1L 


Dibromochloromet hane 















Ethylbenzene 

Elhylbenzene 

Ethylbenzene 

Fluoranthene 

Fluoranthene 

Fluoranthene 

Fluorene 

Fluorene 

Fluorene 

Fluoride ' 

Fluoride 

GC/MS Scan 


Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Alpha 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 

Gross Beta 



















Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 


124-40-1 

124-48-1 

124-40-1 

04-66-2 

04-66-2 

84-664 

131-11-3 

131 -11-3 

131-11-3 

OXYGEN DIS 

OXYGEN DIS 

OXYGEN DIS 

OXYGEN DIS 

OXYGEN DIS 

SO266 

SO266 

100-41 -4 

100-41 -4 

100-41 -4 

206-44-0 

206-44-0 

206-44-0 

06-73-7 

06-73-7 

06-73-7 

16904-40-0 

16904-40-0 

GCNS SCAN 

GAMMA 

12587-46-1 

12507-46-1 

12507-46-1 

12507-46-1 

12507-46-1 

12507-46-1 

12507-46-1 

12507-47-2 

12587-47-2 

12507-47-2 

12587-47-2 

12507-47-2 

12507-47-2 

12507-47-2 

CACO3HARDNES 

CAC03HARDNES 

CACOJHARDNES 

118-74-1 

110-74-1 

110-74-1 

07-60-3 

07-60-3 

87-60-3 

77-47-4 

77-47-4 

77-47-4 

67-72-1 

67 -72- 1 

67-72-1 

193-39-5 

193-39-5 

193-39-5 

7439-09-6 

7439-89-6 

7439-89-6 

7439-09-6 

7439-89-6 

7439-89-6 

7439-09-6 

7439-09-6 

7439-89-6 

7439-09-6 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 


CH210224-DUP 

CH210144-00000 

CH2 10223-00000 

CH2 10224-DUP 

4821-94 

5569-93 

6703-94 

6796-93 

7756-93 

4021-94 

5569-93 

CH210144-00000 

CH2 10223-00000 

CH2 10224-DUP 

CH2I 0144-00000 

CH210223-00000 

CH210224-DUP 

CH2 10144-00000 

CH2 10223-00000 

CH210224-DUP 

4821-94 

5569-93 

4686-92 

4686-92 

4097-92 

4686-92 

4821-94 

5569-93 

6703-94 

6796-93 

7756-93 

4097-92 

4606-92 

4821-94 

5569-93 

6703-94 

6796-93 

7756-93 

CH210144-00000 


CH210224-DUP 

CH2101 44-00000 

CH210223-00000 

CH2 10224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

4097-92 

4686-92 

4021-94 

5569-93 

6028-92 

CH210144-00000 

CH210144-DIS 

CH210223-DIS 


4097-92 

03APR1991 

O3MAY1 991 

O3MAYl99l 

03APR1991 

03MAY1991 

03MAY 1 99 1 

03APR1991 

03MAY 1991 

03MAY1991 

14MARI 994 

23JUN1993 

O6SEPl 994 

21 SEP1993 

O8DEC1993 

14MAR1994 

23JUN1993 

03APR1991 

03MAY 1991 

03MAY 1991 

03APR1991 

03MAY 1991 

03MAY I99 1 

03APR1991 

03MAY1991 

03MAY 1991 

14MARI 994 

23JUN1993 

30MAR1992 

30MARI 992 

31 JAN1992 

3OMAR1992 

14MAR 1994 

23JUN1993 

06SEP1994 

21 SEPl993 

08DECI993 

31JAN1992 

30MARl992 

14MAR1994 

23JUN1993 

06SEPI 994 

2lSEP1993 

08DEC1993 

03APRl991 

03MAYl991 

03MAY1991 

03APRl991 

03MAY 1991 

03MAY1991 

OWR1991 

03MAYl991 

03MAY1991 

03APR1991 

03MAY1991 

03MAY 199 1 

03APR1991 

03MAY 1991 

03MAY1991 

03APR1991 

03MAYI 991 

03MAY 1991 

31 JAN1992 

30MAR1992 

14MAR1994 

23JUN1993 

190CT1992 

03APRl991 

03APR1991 

03MAYI 991 

03MAY 1991 

31JAN1992 

Page 149 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

ViG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

nG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

Q 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

E 

E 

N 

N 

N 

N 

N 

N 

NT 

J 

J 

J 

N 

N 

N 

H 

N 

N 

N 

N 

N 

N 

H 

N 

JE 

JE 

N 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ug/L 

uglL 

uglL 

mglL 

mg/L 

mglL 

mglL 

w/L 

mglL 

mglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ugfl 

ug/L 

uglL 

uglL 

mglL 

mglL 

uglL 

pCi 

pCiL 

pCilL 

pCilL 

pCilL 

pCilL 

pCiL 

pCilL 

pCiL 

pCiL 

pCiL 

pCiL 

pCiL 

pciR 

pCiL 

mglL CaC03 

mglL CaC03 

mglL CaC03 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

0gIL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

mglL 

mSn 

mg1L 

mglL 

WlL 

mgk 

mglL 

WlL 

WlL 

WlL



ANALWE CAS NUMBER SAMPLE ID DATE TYPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Iron. Dissolved 7439-89-6 4821 -94 14MAR1994 WG 8.10E+01 N mglL 


lsophorone 

lsophorone 

lsophorone 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 


Lithium 

Lithium 

Lithium, Dissolved 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 




Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 




Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury 

Mercury. Dissolved 




Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum 

Molybdenum, Dissolved 



N-Nitroso-di-n-propyhmine 

N-Nitroso-di-n-propybmine 

N-Nitroso-di-n-propylamine 

N-Nitrosodiphenybrnine 

N-Nlrosodiphenylamine 

N-Nitrosodiphenylarnine 

Naphthalene 

Naphthalene 

Naphthalene 

Neptunium-237 

Neptunium-237 

Neptunium237 

Nickel 

Nickel 

Nickel 

7439-89-6 

78-59-1 

78-59-1 

78-59-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-93-2 

7439-93-2 

7439-93-2 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-954 

7439-95-4 

7439-96-5 

7439-96-5 

7439-965 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

7439-97-6 

75-09-2 

75-09-2 

75-09-2 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

7439-98-7 

621 -64-7 

621-64-7 

621-64-7 

86-30-6 

86-30-6 

86-30-6 

91-20-3 

91-20-3 

91-20-3 

13994-20-2 

13994-20-2 

13994-20-2 

7440-02-0 

7440-02-0 

7440-02-0 

5569-93 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

4097-92 

4686 - 92 

6028-92 

CH210144-00000 

CH210144-DIS 

CH210223-DIS 

CH2 10224-DUPDI 

4097-92 

4097-92 

6028-92 

4097-92 

4097-92 

4821-94 

5569 - 93 

602892 

CH210144-OOOW 

CH210144-DIS 

CH210223-DIS 


4097-92 

4821-94 

5569-93 

4097-92 

4686-92 

4821-94 

5569-93 

6028-92 

CH210144-00000 

CH210144-DIS 

CH210223-DIS 


4097-92 

4821-94 

5569-93 

4686-92 

6028-92 

CH210144-00000 

CH210144-DIS 

CH210223-DIS 


4097-92 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

4097-92 

4686-92 

4821-94 

5569-93 

6028-92 

4097-92 

4821-94 

5569-93 

CH21014400000 

CH210223-00000 

CH210224-DUP 

CH2I 0144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-DIS 


4097-92 

468692 

4821-94 

23JUN1993 

O3APRl 991 

03MAYI 991 

O3MAY 1991 

31JANl992 

30MAR1992 

190CT1992 

03APR1991 

03APR1991 

O3MAY 1991 

O3MAY 1991 

31JAN1992 

31 JANl 992 

190CT1992 

31JAN1992 

3lJANl992 

14MAR1994 

23JUNl993 

190CT1992 

03APR1991 

O3APRl99l 

O3MAY 1991 

O3MAY 1991 

31 JANl 992 

14MAR1994 

23JUN1993 

31JANl992 

3OMARl992 

14MAR1994 

23JUN1993 

190CT1992 

03APR1991 

03APR 199 1 

03MAYl991 

03MAYl991 

31JAN1992 

14MAR1994 

23JUN1993 

3OMAR1992 

190CT1992 

03APR1991 

03APRl991 

03MAY1991 

03MAY1991 

31JAN1992 

03APR1991 

03MAY 1991 

03MAY 1991 

31 JAN1992 

3OMAR1992 

14MAR1994 

23JUN1993 

190CT1992 

31JAN1992 

14MAR1994 

23JUN1993 

03APR1991 

03MAY1991 

03MAYl991 

03APRl991 

03MAY1991 

03MAY 1991 

03APR1991 

03MAYl991 

03MAY1991 

03APR1991 

03MAY 1991 

03MAY 1991 

31 JAN1992 

3OMAR1992 

1-1994 

Page 150 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WI; 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

6.60E+01 

l.lOE+Ol 

l.OOE+Ol 

l.OOE+Ol 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

3.70E+01 

3.10E+01 

3.60E+01 

3.30€+01 

4.50E+OI 




3.60E+01 

3.20E+01 

3.60E+01 

6.00E+00 

6.WE+00 

6.WE+W 

7.00E+00 

5.00E+00 

9.00E+00 

8.00E+00 

7.00E+00 

7.00E+00 

6.WE+W 

6.00E+W 

7.00E+00 

0.00E+00 

O.OOE+W 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.OOE+W 

5.00E+00 

2.20E+01 

1.60E+01 

0.00E+00 

0.00E+00 

O.WE+W 

0.00E+00 

0.00E+00 

0.00E+W 

O.WE+W 

0.00E+00 

l.lOE+Ol 

1 .WE+Ol 

l.OOE+Ol 

1 .IOE+OI 

1 .00E+01 

1.00E+Ol 

1 .lOE+Ol 

l.OOE+Ol 

1.00E+Ol 

O.OOE+W 1.01E+00 

0.00E+00 9.00E-02 

O.OOE+OO 9.00E-02 

O.OOE+OO 

O.WE+W 

O.OOE+W 

U 

U 

U 

< 

c 

< 

NS 

NW 

UWN 

UWN 

c 

< 

E 

E 

NE 

NE 

< 

< 

U 

U 

U 

U 

< 

UJB 

UB 

UB 

< 

< 

< 

< 

< 

< 

< 

< 

U 

U 

U 

U 

U 

U 

U 

U 

U 

< 

< 

< 

N 

N 

N 

N 

JNS 

JNW 

WN 

WN 

N 

N 

N 

N 

N 

H 

H 

N 

JE 

JE 

N 

N 

N 

N 

N 

H 

N 

JNE 

JNE 

N 

N 

N 

N 

N 

N 

J 

JB 

JB 

N 

N 

N 

N 

N 

N




Nickel 7440-02-0 5569-93 23JUN1993 WG O.OOE+OO c mglL 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel. Dissolved 



Niobium 

Niobium 

Niobium, Dissolved 

Nitrate 

Nitrate 

Nitrate 




Nitrobenzene 

Nitrobenzene 

Nitrobenzene 

PCB-1016 

PCB-1016 

PCB-1221 

PCB-1221 

PCB-1232 

PCB-1232 

PCB-I 242 

PCB-1242 

PCB-1248 

PCB-1248 

PCB-1254 

PCB-1254 

PCB-1260 

PCB-1260 




Phenanthrene 

Phenanthrene 

Phenanthrene 

Phenol 

Phenol 

Phenol 

Phosphate 




Phosphorus, Dissolved 

Plutonium-239 

Plutonium-239 

Plutonium-239 

Plutonium239 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 

Potassium 




Pyrene 

Pyrene 

Pyrene 

RAD Alpha 

RAD Beta 

Ruthenium 

Ruthenium 

Ruthenium 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-03-1 

7440-03-1 

7440-03-1 

14797-55-8 

14797-55-8 

14797-55-8 

NITRATEASNIT 

NITRATEASNIT 


98 - 95 - 3 

98-95-3 

98-95-3 

12674-11-2 

12674-11-2 

I1 104-28-2 

11104-28-2 

11141 -16-5 

11141-16-5 

53469-21-9 

53469-21-9 

12672-29-6 

12672-29-6 

11097-69-1 

11097-69-1 

11096-82-5 

11096-82-5 

87-86-5 

87-86-5 

87-86-5 

85-01-8 

85-01-8 

85-01 -8 

108-95-2 

108-95-2 

108-95-2 

14265-44-2 

7723-14-0 

7723-14-0 

7723-14-0 

7723-14-0 

15117-48-3 

15117-48-3 

15117-48-3 

15117-48-3 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

129-00-0 

129-00-0 

129-00-0 

12587-46-1 

12587-47-2 

7440-18-8 

7440-18-8 

7440-18-8 

6028-92 

CH210144-00000 

CH210144-DlS 

CH210223-DIS 


4097-92 

4821-94 

5569-93 

4097-92 

6028-92 

4097-92 

CH210144-00000 

CH210223-00000 

CH2 10224-DUP 

4097-92 

4821-94 

5569-93 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH2 10223-OW00 

CH210224-DUP 

CH210223-00000 

CH210224-DUP 

CH210223-00000 

CH210224-DUP 

CH210223-00000 

CH210224-DUP 

CH210223-00000 

CH210224-DUP 

CH2 10223-00000 

CH210224-DUP 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 


CH210223-00000 

CH210224DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

4097-92 

4097-92 

4686-92 

6028-92 

4097-92 

CH210144-00000 

CH210144-DIS 

CH210223-DIS 

CH21022CDUPDI 

4686-92 

4821-94 

5569-93 

6028-92 

CH210144-00000 

CH210144-DIS 

CH210223-DIS 


4097-92 

4821 -94 

5569-93 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

5569-93 

5569-93 

4097-92 

4686-92 

6028-92 

190CT1992 

03APR1991 

03APRl991 

03MAY1991 

03MAY1991 

31 JAN1 992 

14MARl994 

23JUNl993 

31 JANl 992 

190CT1992 

31JAN1992 

03APR1991 

OMAY 1991 

03MAY1991 

31JANl992 

14MAR1994 

23JUN1993 

03APR1991 

OMAYI 991 

03MAY1991 

03MAY 1991 

03MAY1991 

03MAY1991 

O3MAY 1991 

03MAY1991 

03MAY1991 

03MAY 1991 

03MAY 1991 

03MAY 1991 

03MAY 1991 

03MAYI 991 

03MAYI 991 

03MAY I991 

03MAY1991 

O3APRl 991 

03MAY1991 

03MAY1991 

03APR1991 

03MAY1991 

03MAY I991 

03APRI991 

03MAYl991 

03MAY1991 

31 JANl 992 

31JAN1992 

3OMAR1992 

190CTl992 

31JAN1992 

O3APRl 991 

03APRl991 

03MAY1991 

03MAYl991 

3OMARl 992 

14MAR1994 

23JUN1993 

190CT1992 

O3APRl 991 

03APR1991 

03MAYl991 

03MAYI 991 

31 JAN1992 

14MAR1994 

23JUN1993 

03APR1991 

03MAY 1991 

OJMAY1991 

2UUN1993 

2UUN1993 

31JAN1992 

3OMAR1992 

190CT1992 

Page 151 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

v\EG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

w.3 

WG 

WG 

WG 

WG 

WG 

w.3 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

I .00E+00 

l.OOE+OO 

l.OOE+OO 

l.lOE+Ol 

1.00E+01 

l.OOE+OI 

3.00E+00 

3.00E+00 

3.OOE+00 

3.OOE+00 

3.00E+00 

3.WE+00 

3.00E+00 

3.00E+00 

3.00E+00 

3.00E+00 

5.00E+00 

5.00E+00 

5.WE+00 

5.00E+W 

S.SOE+Ol 

5.00E+01 

5.00E+01 

l.lOE+OI 

1.00E+00 

1.00E+00 

l.lOE+Ol 

l.OOE+OI 

l.OOE+OI 

2.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 9.11E-02 

O.OOE+OO 7.40E-02 

O.OOE+OO 2.00E-01 

O.WE+OO 1.30E-01 

1.20E+01 

1.20E+01 

1.20E+01 

1.20E+Ol 

1.50E+01 

1.30E+01 

1.30E+01 

1.30E+01 

1.40E+01 

1.20E+01 

I .2OE+O1 

I .00E+00 

1.00E+01 

l.WE+Ol 

l.OOE+OO 

l.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

e 

B 

U 

U 

U 

< 

< 

< 

e 

Q 

< 

U 

U 

U 

< 

c 

e 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

J 

J 

U 

U 

U 

< 

< 

< 

< 

< 

N 

B 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

J 

J 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

H 

H 

N 

N 

N 

N 

J 

mglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ugfl 

uglL 

uglL 

uglL 

UgR 

uglL 

UdL 

ugk 

ug1L 

uglL 

ug1L 

uglL 

ug1L 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

mglL 

mglL 

mglL 

WIL 

mg1L 

pCiL 

pCiL 

pCUL 

pCUL 

mglL 

mgk 

mgk 

W L 

mglL 

mglL 

mglL 

mgfl 

mg/L 

mg/L 

mg/L 

Usn 

ugfl 

ugk 

pCilml 

pCi/ml 

mgk 

mgk 

mgk




Ruthenium, Dissolved 7440-18-8 4097-92 31JAN1992 WG O.OOE+OO < N mglL 

Selenium 

Selenium 

Selenium 

Selenium 

Selenium 

Selenium 


Semi-Volatile Organic Qual 

Silica 

Silica 

Silicon 

Silicon 

Silicon, Dissolved 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver 

Silver, dissolved 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

























Strontium 

Strontium 

Strontium 

Strontium, Dissolved 

Styrene 

Styrene 

Styrene 

Sulfate 

Sulfate 

Sulfate 

Sulfate 

Sulfate 

Sulfate 

Sulfide 

Sulfide 

Sulfide 

Tantalum 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

SVOL 

7631 -86-9 

7631 -86-9 

7440-21-3 

7440-21-3 

7440-21-3 

7440-22-4 

7440-22-4 

7440-22-4 

7440-22-4. 

7440-224 

7440-22-4 

7440-22-4 

7440-22-4 

7440 - 23 - 5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

7440-24-6 

7440-24-6 

7440-24-6 

7440-24-6 

100-42-5 

100-42-5 

100-42-5 

12143-45-2 

12143-45-2 

12143-45-2 

1214345-2 

1214345-2 

12143-45-2 

18496-25-8 

18496-25-8 

18496-25-8 

7440-25-7 

4097-92 

4686-92 

CH210144-00000 

CH210144-DIS 

CH210223-DIS 


4097-92 

4097-92 

4821-94 

5569-93 

4097-92 

6028-92 

4097-92 

4097-92 

4686-92 

6028-92 

CH210144-00000 

CH210144-DIS 

CH2 10223-DIS 


4097-92 

4097-92 

4686-92 

4821-94 

5569-93 

6028-92 

CH210144-00000 

CH210144-DIS 

CH210223-DIS 


4097-92 

4821 -94 

5569-93 

4686-92 

4821-94 

4822-94 

4823-94 

4824-94 

5569-93 

5570-93 

5571-93 

5572-93 

6703-94 

6704-94 

6705-94 

6706-94 

6796-93 

6797-93 

6798-93 

6799-93 

7756-93 

7757-93 

7758-93 

7759-93 

4097-92 

4686-92 

6028-92 

4097-92 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

4097-92 

482 1-94 

5569-93 

CH210144MX)o 

CH21022J-00000 

CH210224DUP 

CH2 101 44-00000 

CH210223-00000 

CH210224DUP 

4097-92 

31 JANl 992 

30MAR1992 

03APRl991 

03APRl991 

O3MAY 1991 

03MAY1991 

31 JANl 992 

31JAN1992 

14MAR1994 

23JUN1993 

31 JANl 992 

190CT1992 

31 JANl 992 

31 JANl 992 

3OMAR1992 

190CT1992 

03APRl991 

03APRl991 

03MAY1991 

03MAY1991 

31 JAN1992 

31JANl992 

30MAR1992 

1 MAR1994 

23JUN1993 

19OCTl992 

03APR1991 

03APR199 1 

03MAYl991 

03MAY1991 

31 JAN1992 

14MAR1994 

23JUN1993 

3OMAR1992 

14MAR1994 

14MAR1994 

14MARl994 

14MAR1994 

23JUN1993 

23JUN1993 

23JUN1993 

23JUN1993 

06SEPl994 

06SEPl994 

06SEP1994 

06SEP1994 

21 SEP1993 

21 SEPl993 

21SEPl993 

2lSEP1993 

08DEC1993 

08DECl993 

08DECl993 

08DECl993 

31 JAN1992 

3OMAR1992 

190CTl992 

31 JAN1992 

03APRl991 

03MAY 1991 

03MAYl991 

31JAN1992 

14MAR1994 

23JUN1993 

03APR1991 

03MAYl991 

03MAY1991 

03APR1991 

03MAY 1991 

03MAY 1991 

31 JAN1992 

Page 152 of 176 

w 

WG 

WG 

w 

w 

w 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

w 

w 

WG 

WG 

WG 

WG 

WG 

w 

w 

WG 

w 

WG 

w 

w 

w 

w 

w 

w 

w 

WG 

WG 

w 

w 

w 

w 

w 

WG 

WG 

WG 

WG 

WG 

w 

w 

w 

w 

w 

w 

w 

w 

w 

w 

w 

w 

w 

WG 

w 

w 

w 

w 

w 

w 

w 

w 

w 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

5.02E+02 

2.40E+01 

1.20E+01 

1.20E+01 

l.lOE+Ol 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.OOE+OO 

O.OOE+W 

O.WE+W 

O.WE+OO 

O.OOE+OO 

2.70E+01 

2.60E+01 

l.OOE+Ol 

2.50E+01 

2.50E+01 

2.60E+Ol 

2.60E+Ol 

3.00E+01 

2.90E+Ol 

2.80E+01 

1 .WE+Ol 

2.40E+01 

1.23E+03 

1.26E+03 

1.25E+O3 

1.25E+03 

1.23E+03 

1.27E+O3 

1.24E+03 

1.24E+03 

1.24E+O3 

1.02€+03 

1 .O2E+O3 

1.03E+03 

1.03E+03 

1.09E+03 

1.09E+03 

1.11E+O3 

1.10E+03 

1.13E+03 

1 .11E+O3 

l.llE+O3 

1 .lE+O3 

l.OOE+OO 

l.WE+W 

l.OOE+W 

1 .WE+W 

5.WE+00 

5.WE+W 

S.WE+W 

1.32E+02 

2.53E+02 

1.77E+02 

2.61E+02 

2.18E+02 

2.11E+02 

O.WE+W 

O.WE+W 

O.WE+W 

O.WE+OO 

C 

c 

UNW 

UNW 

UN 

UN 

C 

R 

< 

C 

UB 

UN 

UN 

C 

E 

E 

U 

U 

U 

U 

U 

U 

< 

N 

N 

NW 

NW 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

JB 

N 

N 

N 

N 

N 

H 

H 

N 

JE 

JE 

N 

N 

N 

N 

N 

N 

N 

N 

H 

H 

H 

H 

H 

H 

H 

H 

H 

H 

H 

H 

N 

N 

N 

N 

N 

H 

N 

N 

N 

N 

N 

N 

N 

N 

m& 

mglL 

wfl 

mglL 

mglL 

mglL 

mglL 

uglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mgfl 

mgfl 

mgfl 

mgfl 

mgfl 

umhodcm 

umhodcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhodcm 

umhoslcm 

umhoslcm 

umhodcm 

umhos/cm 

umhoslcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhos/cm 

umhodcm 

umhoslcm 

umhodcm 

urnhoslcm 

mglL 

mglL 

wfl 

mglL 

ug/L 

ugfl 

ug/L 

mgfl 

mgfl 

mgfl 

wfl 

mgfl 

mgfl 

mglL 

mglL 

mgfl 

wfl



ANALYTE CAS NUMBER SPMPLE ID DATE TYPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Tantalum 7440-25-7 4686-92 30MAR1992 WG O.OOE+OO N malL 

Tantalum 

Technetium-99 

Technetium-99 

Technetium-99 

Technetium-99 

Technetium-99 

Technetium-99 

Technetium-99 

Technetium-99 

Technetium-99 

Technetium-99 

Technetium-99 

Technetium-99 

Temperature 

Temperature 

Temperature 

Temperature 

Temperature 

Temperature 

Temperature 

Telrachloroethene 


Tetrachloroelhene 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium 

Thallium, Dissolved 



Thorium 

Thorium, Dissolved 

Thorium-230 

Thorium-230 

Thorium-230 

Thorium-230 

Tin 

Tin 

Tin 

Tin, Dissolved 

Tiianium 

Titanium 

Tiianium. Dissolved 

Toluene 

Toluene 

Toluene 



















Trichloroelhene 

Tungsten 

Tungsten, Dissolved 

7440-25-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

SO835 

SO835 

SO835 

SO835 

SO835 

SO835 

SO835 

127-18-4 

127-18-4 

127-18-4 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-2a-o 

7440-28-0 

7440-28-0 

7440-28-0 

7440-2a-o 

7440-28-0 

7440-28-0 

7440-29-1 

7440-29-1 

14269-63-7 

14269-63-7 

14269-63-7 

14269-63-7 

7440-31-5 

7440-31 -5 

7440-31 -5 

7440-31 -5 

7440-32-6 

7440-32-6 

7440-34-6 

108-88-3 

108-88-3 

108-88-3 

7440-44-0 

7440-44-0 

744044-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

156-60-5 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

7440-33-7 

7440-33-7 

6028-92 

1110-91 

4686 - 92 

4821-94 

5569-93 

6028-92 

6703-94 

6796-93 

7756-93 

CH210144-OW00 

CH210144-DIS 

CH210223-DIS 


4686-92 

4821-94 

5569-93 

6028-92 

6703-94 

6796-93 

7756-93 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

4686-92 

4821-94 

5569-93 

6028-92 

CH210144-M)oO 

CHZlO144-DIS 

CH2 10223-DIS 


4097-92 

482 1-94 

5569-93 

6028-92 

4097-92 

CH210144-00000 

CH210144-DIS 

CH210223-DIS 


4097-92 

4686-92 

6028-92 

4097-92 

4097-92 

6028-92 

4097-92 

CH2 lO144oooOO 


CH21022CDUP 

4821-94 

4822-94 

4823-94 

4824-94 

5569-93 

5570-93 

5571-93 

5572-93 

6028-92 

1110-91 

4821-94 

5569-93 

6028-92 

6703-94 

6796-93 

7756-93 

CH2 10144-00000 

CH210223-WOO0 

CH210224-DUP 

6028-92 

4097-92 

190CT1992 

03APR1991 

3OMAR1992 

14MAR1994 

23JUN1993 

190CT1992 

06SEP1994 

21 SEP1993 

08DEC1993 

03APR1991 

03APR1991 

03MAY1991 

03MAY1991 

30MAR1992 

14MAR1994 

23JUN1993 

190CT1992 

06SEP1994 

21SEPl993 

08DEC1993 

03APR1991 

03MAY1991 

03MAYl991 

3OMAR1992 

14MAR1994 

23JUN1993 

190CT1992 

03APRl991 

03APR1991 

03MAY 1991 

03MAY 1991 

31JAN1992 

14MARl994 

23JUN1993 

190CT1992 

3lJAN1992 

03APR1991 

03APRl991 

03MAYl991 

03MAY1991 

31JAN1992 

3OMAR1992 

190CT1992 

31JAN1992 

31 JANl 992 

190CT1992 

3lJAN1992 

03APRl991 

03MAY1991 

03MAY1991 

1 MAR1994 

1 MAR1 994 

14MAR1994 

14MAR1994 

23JUN1993 

23JUN1993 

23JUN1993 

23JUN1993 

190CT1992 

03APR1991 

14MAR1994 

23JUN1993 

190CT1992 

06SEP1994 

21SEP1993 

OBDEC1993 

03APRl991 

03MAY1991 

03MAY1991 

190CTl992 

31 JANl 992 

Page 153 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

\M; 

WG 

WG 

WG 

WG 

Q 

U 

U 

U 

< 

< 

c 

UNW 

UNW 

u\MJ 

U W 

< 

c 

< 

< 

< 

< 

U 

U 

U 

< 

< 

U 

UJ 

< 

ux 

UJ 

U 

U 

U 

U 

< 

N 

N 

N 

H 

N 

N 

H 

H 

N 

N 

N 

H 

N 

NW 

NW 

W 

WIN 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

H 

H 

H 

H 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

pCiL 

pCilL 

pCilL 

pCilL 

pCVL 

pCilL 

pCVL 

pCilL 

pCVL 

pCilL 

pCilL 

pCVL 

F 

F 

F 

F 

F 

F 

F 

uglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

WlL 

mglL 

mg1L 

mglL 

mglL 

mglL 

pCilL 

pCA 

pCiL 

pCilL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

uglL 

mg/L 

mglL 

WlL 

mglL 

mglL 

mglL 

mglL 

mg1L 

uglL 

uglL 

uglL 

uglL 

uglL 

ugfl 

uglL 

uglL 

ugfl 

uglL 

uglL 

WlL 

WlL



ANALYTE CAS NUMBER SAMPLE ID DATE NPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Turbidity SO278 4097-92 31JAN1992 WG 1.52E+02 N NTU 

Turbidity 

Turbidity 

Turbidity 

Turbidity 

Turbidity 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 


Uranium-234 

Uranium-234 

Uranium-234 

Uranium-234 

Uranium-235 

Uranium235 

Uranium-235 

Uranium-235 

Uranium238 

Uranium-238 

Uranium-238 

Uranium-238 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium 

Vanadium, Dissolved 



Vinyl Acetate 

Vinyl Acetate 

Vinyl Acetate 




Xylene 

Xylene 

Xylene 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc. Dissolved 



Zirconium 

Zirconium 

Zirconium, Dissolved 




bis(2-Chloroethy Qether 


bis(2-ChloroethyQether 

bis(2-ChloroisopropyQether 


bis(2-ChloroisopropyQether 

bk(2-EthylhexyQphthabte 

bis(2-EthylhexyQphthalate 

bis(2-EthylhexyQphthabte 

cis-I .Z-dichloroethene 



SO278 

SO278 

SO278 

SO278 

SO278 

7440-61-1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61-1 

DIS U 

13966-29-5 

13966-29-5 

13966-29-5 

13966-29-5 

15117-96-1 

15117-96-1 

15117-96-1 

15117-96-1 

24678-82-8 

24678-82-8 

24678-82-8 

24678-82-8 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

I 08-05-4 

108-05-4 

108-05-4 

75-01-4 

75-01-4 

75-01-4 

1330-20-7 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-67-7 

7440-67-7 

7440-67-7 

111-91-1 

111-91-1 

111-91-1 

111-44-4 

111-44-4 

111-44-4 

108-60-1 

108-60-1 

108-60-1 

117-81-7 

117-81-7 

117-81-7 

156-59-2 

10061 -01-5 

10061 -01-5 

4821-94 

5569-93 

6703-94 

6796-93 

7756-93 

4097-92 

4686-92 

4821-94 

5569-93 

6028-92 

4097-92 

CH210144-00000 

CH210144-DIS 

CH210223-DIS 


CH210144-00000 

CH21014CDIS 

CH210223DIS 


CH210144-00000 

CH2 I01 44-DIS 

CH210223-DIS 

CH2 10226DUPDI 

4686-92 

4821-94 

5569-93 

CH210144-00000 

CH210144-DIS 

CH210223-DIS 


4097-92 

4821-94 

5569-93 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH210224-DUP 

CH2I 0144-00000 

CH210223-00000 

CH210224-DUP 

4097-92 

4821-94 

5569-93 

6028-92 


CH2I 0144-DIS 

CH210223-DIS 


4097-92 

4821 -94 

5569-93 

4686-92 

6028-92 

4097-92 

CH210144-00000 

CH2 10223-00000 

CH210224DUP 

CH2 1014440000 

CH210223-00000 

CH210224-DUP 

CH210144-00000 

CH210223-00000 

CH21022CDUP 

CH21014400000 

CH210223-00000 

CH210224-DUP 

6026-92 

CH21014400000 

CH210223-00000 

14MAR1994 

23JUN1993 

O6SEPI 994 

21SEP1993 

08DEC1993 

31JAN1992 

3OMAR1992 

14MAR1994 

23JUN1993 

190CT1992 

31 JAN 1992 

03APRl991 

03APR1991 

03MAY1991 

03MAYl991 

03APR1991 

O3APRl 991 

03MAY I991 

03MAYl991 

03APR199.1 

O3APR1 991 

03MAY1991 

03MAY 1991 

30MAR1992 

14MARl994 

23JUN1993 

O3APRl 991 

03APRI 991 

03MAY 1991 

03MAY 1991 

31 JAN1992 

14MAR1994 

23JUNl993 

03APRl991 

03MAY I991 

03MAY 1991 

03APRl991 

03MAY 1991 

03MAYl991 

03APR I991 

03MAYl991 

03MAY 1991 

31 JAN1992 

14MAR1994 

23JUNI993 

190CT1992 

03APR1991 

OBAPRI 991 

WAY I991 

03MAY 1991 

31 JAN1992 

14MARl994 

23JUN1993 

30MARI 992 

190CT1992 

31JAN1992 

03APRl991 

03MAY1991 

03MAYI991 

O3APR 1991 

03MAY I99 I 

03MAYl991 

O3APRI99I 

03MAYl991 

03MAY I99 1 

03APR1991 

03MAYl991 

03MAYl991 

190CTI 992 

03APRI991 

03MAY1991 

Page 154 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

w 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

w 

w 

WG 

WG 

w 

WG 

w 

WG 

w 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

Irw; 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

2.70E+02 

3.80E+02 

2.50E+02 

1.70E+02 

3.30€+02 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00€+00 

O.OOE+OO 

O.OOE+OO 

1.00E+00 7.40E-01 

O.OOE+OO 2.60E-01 

O.OOE+OO 5.00E-02 

O.OOE+OO 7.00E-02 

O.OOE+OO 4.61E-01 

O.OOE+OO 1.20E-01 

O.OOE+OO 2.00E-02 

O.OOE+OO 2.00E-02 

1.00E+00 7.00E-01 

1.00E+00 3.60E-01 

0.00E+00 8.00E-02 

O.OOE+OO 8.00E-02 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

l.OOE+Ol 

1.00E+01 

I .00E+01 

l.OOE+OO 

1.00E+00 

1 .00E+00 

5.00E+00 

5.WE+00 

5.00E+W 

O.WE+OO 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.WE+W 

O.OOE+OO 

0.00E+00 

0.00E+00 

O.OOE+OO 

0.00E+00 

O.WE+W 

0.00E+00 

O.OOE+OO 

l.lOE+Ol 

1.00€+01 

I.OOE+Ol 

l.lOE+Ol 

1 .OOE+OI 

1 .00E+01 

I.IOE+OI 

l.WE+OI 

l.OOE+OI 

l.lOE+Ol 

I.WE+Ol 

l.OOE+Ol 

I .00E+01 

5.00E+00 

5.00E+00 

c 

< 

C 

c 

c 

U 

U 

U 

UB 

UB 

UB 

< 

< 

U 

U 

U 

U 

U 

U 

U 

U 

U 

UJB 

U 

U 

J 

U 

U 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

JB 

N 

N 

N 

N 

H 

N 

JB 

JB 

JB 

N 

N 

N 

N 

N 

N 

J 

N 

NTU 

NTU 

NTU 

NTU 

NTU 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

pCilL 

pCilL 

pCilL 

pCilL 

pCilL 

pCilL 

pCiL 

pCilL 

pCifL 

pCiL 

pCilL 

pCilL 

mglL 

mglL 

rnglL 

rnglL 

mg/L 

mglL 

mglL 

mglL 

mg/L 

mglL 

uglL 

uglL 

uglL 

uglL 

ug/L 

ug1L 

uglL 

uglL 

uglL 

mgk 

WlL 

mglL 

mglL 

mg1L 

mg5 

mg1L 

mglL 

mg/L 

mglL 

mglL 

mgk 

mglL 

mg/L 

uglL 

ugJL 

UdL 

uglL 

uglL 

uglL 

uglL 

ugk 

uglL 

ugk 

ugfl 

ugk 

uglL 

ugfl 

uglL




cis-l,3-Dichloropropene 10061-01-5 CH210224-DUP 03MAY1991 WG 5.00E+00 U ug/L 

PH 

SO296 

4097-92 31JAN1992 WG 

su 

PH 

SO296 

4686-92 3OMAR1992 

WG 

su 

PH 

SO296 

4821-94 14MARl994 WG 

su 

PH 

SO296 

4822-94 14MARl994 WG 

su 

PH 

SO296 

4823-94 14MAR1994 WG 

su 

PH 

SO296 

4824-94 14MAR1994 WG 

su 

PH 

SO296 

5569-93 23JUN1993 WG 

su 

PH 

SO296 

5570-93 23JUN1993 WG 

su 

PH 

SO296 

5571-93 23JUNl993 WG 

su 

PH 

SO296 

5572-93 23JUN1993 WG 

su 

PH 

SO296 

6028-92 190CT1992 WG 

Q 

su 

PH 

SO296 

6703-94 O6SEP1 994 WG 

su 

PH 

SO296 

6704-94 O6SEP1 994 WG 

su 

PH 

SO296 

6705-94 06SEP1994 WG 

su 

PH 

SO296 

6706-94 O6SEP1 994 WG 

su 

PH 

SO296 

6796-93 2lSEPl993 WG 

su 

PH 

SO296 

6797-93 21SEP1993 WG 

su 

PH 

SO296 

6798-93 21 SEPl993 w 

su 

PH 

SO296 

6799-93 2lSEP1993 w 

su 

PH 

SO296 

7756-93 08DEC1993 WG 

su 

PH 

SO296 

7757-93 08DECl993 WG 

su 

PH 

SO296 

7758-93 08DEC1993 WG 

su 

PH 

SO296 

7759-93 08DEC1993 WG 

su 

trans-l,3-Dichloropropene 10061-02-6 CH210144-WOOO 03APRl991 w 

U 

uglL 

trans-l,3-Dichloropropene 


10061-02-6 

10061 -02-6 

CH2I 0223-00000 

CH210224-DUP 

03MAYl991 

03MAY1991 

WG 

WG 

U 

U 

uglL 

uglL 

WAG 7, SVWU 8, MW24 

Alkalinity 

Alkalinity 

Alkalinity 

471-34-1 

471-34-1 

471-34-1 

1950-88 

3016-91 

4099-92 

14SEP1988 

29AUG1991 

01FEB1992 

WG 

WG 

WG 

T 

N 

N 

mglL 

mgfl 

mglL 

Alkalinity 

471-34-1 

5406-92 1 lAUGl992 WG 

N 

mglL 

Aluminum 

7429-90-5 

4099-92 OlFEB1992 w 

< 

N 

mg/L 

Aluminum, dissolved 

Americium 241 

Americium 241 

Americium 241 

Antimony 


Arsenic 


Barium 


Beryllium 


7429-90-5 

AM241 

AM241 

AM241 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

7440-41-7 

7440-41-7 

4099-92 

1950-88 

3016-91 

5406-92 

4099-92 

4099-92 

4099-92 

4099-92 

4099-92 

4099-92 

4099-92 

4099-92 

01 FEB1992 

14SEP1988 

29AUGl991 

11AUGI 992 

01 FEBI 992 

01 FEB1992 

OlFEB1992 

OlFEB1992 

01 FEB1992 

01 FEB1992 

01 FEBl992 

01FEBl992 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

e 

N 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

pCiL 

pCVL 

pCi 

mg/L 

mg/L 

mglL 

mglL 

mglL 

mg/L 

mglL 

mglL 

Bismuth 


Cadmium 

Cadmium 

Cadmium 

7440-69-9 

7440-69-9 

7440-43-9 

7440-43-9 

7440-43-9 

4099-92 

4099-92 

195088 

2295-89 

2979-90 

OlFEBl992 

01 FEB1992 

14SEPl988 

25AUGl989 

05SEP1990 

WG 

WG 

WG 

WG 

WG 

c 

< 

N 

N 

T 

T 

T 

mglL 

mglL 

mglL 

mg1L 

mglL 

Cadmium 

7440-43-9 

301691 29AUG 1991 WG 

< 

N 

mglL 

Cadmium 

7440-43-9 

4099-92 01 FEBl992 w 

N 

mglL 

Cadmium 

7440-43-9 

5406-92 llAUG1992 WG 

N 

mglL 


7440-43-9 

4099-92 OlFEBl992 w 

N 

mgn- 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 


Cesium137 

Cesium1 37 

Cesium-137 

Chloride 

Chloride 

Chloride 

Chloride 

Chromium 

Chromium 

Chromium 

Chromium 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

10045-97-3 

10045-97-3 

10045-97-3 

16887-00-6 

16887-00-6 

16887-00-6 

16887-00-6 

7440-47-3 

7440-47-3 

7440-473 

7440-47-3 

1950-88 

2295-89 

2979-90 

3016-91 

4099-92 

5406-92 

4099-92 

1950-88 

301691 

5406-92 

195088 

301691 

4099-92 

5406-92 

1950-88 

2295-89 

2979-90 

3016-91 

14SEP1988 

25AUG1989 

OSSEP1990 

29AUGl991 

OlFEBl992 

llAUG1992 

OlFEB1992 

14SEP1988 

29AUGI 991 

1 lAUGl992 

14SEPl988 

29AUG1991 

01 FEB1992 

llAUG1992 

14SEPl988 

25AUG1989 

O5SEP1990 

29AUG1991 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

v\IG 

WG 

HT 

HT 

HT 

N 

N 

N 

N 

NT 

N 

N 

HT 

N 

N 

N 

T 

T 

T 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

pciR 

pciR 

pciR 

mglL 

mg5 

mglL 

mglL 

mgk 

mg1L 

mglL 

mgfl 

Page 155 of 176




Chromium 7440-47-3 4099-92 01FEB1992 WG O.OOE+OO C N mglL 

Chromium 


Cobalt 

Cobalt 60 

Cobalt 60 

Cobalt 60 


Color 

Color 

Color 

Color 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 







Dissolved Alpha 





Dissolved Beta 









Fluoride 

Fluoride 

Fluoride 

Fluoride 

GCMS Scan 


Gross Alpha 

Gross Beta 




Iron 

Iron 

Iron 

Iron 

Iron 

Iron 


Lead 

Lead 

Lead 

Lead 

Lead 

Lead 


Lithium 

Lithium. Dissolved 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 


7440-47-3 

7440-47-3 

7440-48-4 

10198-40-0 

10198-40-0 

10198-40-0 

7440-48-4 

COLOR 

COLOR 

COLOR 

COLOR 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

DTW 

DTW 

DTW 

DTW 

DTW 

ALPHA DIS 

ALPHA DIS 

ALPHA DIS 

ALPHA DIS 

ALPHA DIS 

BETA DIS 

BETA DIS 

BETA DIS 

BETA DIS 

BETA DIS 

SO266 

SO266 

SO266 

SO266 

16984-48-8 

16984-48-8 

16984-48-8 

16984-48-8 

GCMS SCAN 

GAMMA 

1258746-1 

12587-47-2 

18540-29-9 

18540-29-9 

18540-29-9 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-93-2 

7439-93-2 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

5406-92 

4099-92 

4099-92 

1950-88 

3016-91 

5406-92 

4099-92 

1950-88 

3016-91 

4099-92 

5406-92 

195088 

2295-89 

2979-90 

3016-91 

4099-92 

5406-92 

4099-92 

1950-88 

2295-89 

2979-90 

3016-91 

5406-92 

1950-88 

2295-89 

2979-90 

3016-91 

5406-92 

1950-88 

2295-89 

2979-90 

3016-91 

5406-92 

1950-88 

3016-91 

4099-92 

5406-92 

1950-88 

3016-91 

4099-92 

5406-92 

4099-92 

4099-92 

4099-92 

4099-92 

1950-88 

3016-91 

5406-92 

1950-88 

2295-89 

2979-90 

3016-91 

4099-92 

5406-92 

4099-92 

1950-88 

2295-89 

2979-90 

3016-91 

4099-92 

5406-92 

4099-92 

4099-92 

4099-92 

1950-88 

2295-89 

2979-90 

3016-91 

4099-92 

5406-92 

4099-92 

llAUG1992 

01FEB1992 

01FEB1992 

14SEP1988 

29AUG1991 

11 AUGl992 

01 FEB1992 

14SEP1988 

29AUG1991 

01FEB1992 

11AUGl992 

14SEP1988 

25AUGl989 

05SEPl990 

29AUGl991 

OlFEB1992 

llAUGl992 

01FEB1992 

14SEP1988 

25AUG1989 

05SEP1990 

29AUG1991 

11 AUGl992 

14SEP1988 

25AUG1989 

05SEP1990 

29AUGl991 

11 AUGl992 

14SEP1988 

25AUG1989 

05SEP1990 

29AUG1991 

1 lAUGl992 

14SEP1988 

29AUG1991 

01FEB1992 

11 AUGl992 

14SEPl988 

29AUG1991 

01FEBl992 

1 lAUGl992 

OlFEB1992 

01 FEBl992 

OlFEBl992 

01FEB1992 

14SEP1988 

29AUGl991 

11AUG1992 

14SEP1988 

25AUG1989 

05SEPl990 

29AUG 1991 

01FEBl992 

llAUG1992 

OlFEB1992 

14SEP1988 

25AUGl989 

05SEP1990 

29AUG 1991 

01 FEE1 992 

1 lAUGl992 

OlFEBl992 

OlFEB1992 

OlFEBl992 

14SEP1988 

25AUGl989 

05SEP1990 

29AUGl991 

OlFEB1992 

llAUG1992 

01 FEBl992 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

w 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

c 

N 

< N 

< N 

NT 

N 

N 

C 

N 

HT 

N 

N 

N 

T 

T 

T 

N 

N 

N 

N 

N 

N 

N 

N 

Q 

c 

e 

NT 

NT 

NT 

N 

N 

NT 

NT 

NT 

N 

N 

HT 

N 

N 

N 

T 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

HT 

HT 

HT 

N 

N 

N 

N 

T 

T 

T 

N 

N 

N 

N 

N 

N 

HT 

HT 

HT 

N 

N 

N 

N 

Page 156 of 176




Manganese 

7439-96-5 1950-88 14SEP1988 WG O.OOE+OO HT mglL 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 


7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

2295-89 

2979-90 

3016-91 

4099-92 

5406-92 

4099-92 

25AUG1989 

05SEP1990 

29AUG1991 

01FEB1992 

llAUGl992 

01 FEE1992 

WG 

WG 

WG 

WG 

WG 

WG 

HT 

HT 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

Mercury 

7439-97-6 

4099-92 01 FEB1992 WG 

N 

mglL 


7439-97-6 

4099 - 92 

01 FEE1992 WG 

N 

mg1L 

Molybdenum 


Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 


Niobium 






PCB 

PCB 

PCB 

PCB 







Potassium 


Qual IR 

Radium-226 

Radium-226 

Radium226 

Ruthenium 

Ruthenium, Dissolved 

Selenium 

Selenium 

Selenium 

Selenium 

Selenium 

Selenium 


Silicon 


Silver 


Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 












Strontium 

Strontium. Dissolved 

7439-98-7 

7439-98-7 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-03-1 

7440-03-1 

NITRATEASNIT 




1336-36-3 

1336-36-3 

1336-36-3 

1336-36-3 

PHOSPHATEASP 

PHOSPHATEASP 

PHOSPHATEASP 

PHOSPHATEASP 

7723-14-0 

7723-14-0 

7440-09-7 

7440-09-7 

QUAL IR 

13982-63-3 

13982-63-3 

13982-63-3 

7440-18-8 

7440-18-8 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

7440-21-3 

7440-21-3 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

7440-24-6 

7440-24-6 

4099-92 

4099-92 

1950-88 

2295-89 

2979-90 

3016-91 

4099-92 

5406-92 

4099-92 

4099-92 

4099-92 

1950-88 

3016-91 

4099-92 

5406-92 

1950-88 

3016-91 

4099-92 

5406-92 

1950-88 

3016-91 

4099-92 

5406-92 

4099-92 

4099-92 

4099-92 

4099-92 

3098-91 

1950-88 

3016-91 

5406-92 

4099-92 

4099-92 

1950-88 

2295-89 

2979-90 

3016-91 

4099-92 

5406-92 

4099-92 

4099-92 

4099-92 

4099-92 

4099-92 

1950-88 

2295-89 

2979-90 

3016-91 

4099-92 

5406-92 

4099-92 

1950-88 

301691 

3038-91 

3039-91 

3040-91 

4099-92 

5406-92 

5407-92 

5408-92 

5409-92 

4099-92 

4099-92 

01 FEE1992 

OlFEB1992 

14SEP1988 

25AUG1989 

05SEP1990 

29AUG1991 

01FEB1992 

11 AUGl992 

01FEB1992 

01 FEE1992 

01 FEE1992 

14SEP1988 

29AUG1991 

01 FEB1992 

1 lAUGl992 

14SEP1988 

29AUG1991 

01 FEE1 992 

1 lAUGl992 

14SEP1988 

29AUGl991 

01FEB1992 

1 lAUGl992 

OlFEB1992 

01 FEBl992 

01FEB1992 

01FEB1992 

OSSEPl991 

14SEP1988 

29AUGl991 

11AUG1992 

01 FEE1 992 

01 FEE1992 

14SEP1988 

25AUGl989 

(HSEPl990 

29AUGl991 

01 FEBl992 

1 lAUGl992 

01FEB1992 

01 FEBl992 

01FEB1992 

OlFEBl992 

OlFEB1992 

14SEP1988 

25AUG1989 

05SEPl990 

29AUGl991 

01 FEB1992 

11AUG1992 

01FEB1992 

14SEP1988 

29AUG1991 

29AUG1991 

29AUG1991 

29AUG1991 

OlFEB1992 

llAUG1992 

llAUG1992 

llAUG1992 

11AUG1992 

OlFEBl992 

01 FEE1992 

WG 

WG 

WG 

WG 

WG 

WG 

v\IG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

N 

N 

T 

T 

T 

N 

N 

N 

N 

N 

N 

T 

N 

N 

N 

HT 

N 

N 

N 

T 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

N 

N 

T 

T 

T 

N 

N 

N 

N 

N 

N 

N 

N 

HT 

HT 

HT 

N 

N 

N 

N 

HT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

ug1L 

uglL 

uglL 

uglL 

mglL 

mgfl 

mglL 

mglL 

WlL 

mglL 

mglL 

mglL 

comment 

pCVL 

pCVL 

pCVL 

mgfl 

mglL 

mglL 

mglL 

mglL 

WlL 

mglL 

mglL 

mglL 

W/L 

mglL 

WlL 

mglL 

WlL 

mg1L 

mg/L 

mglL 

mglL 

mglL 

WlL 

umhoslcm 

umhodcm 

umhoslcm 

umhoslcm 

umhoslcm 

urnhodcm 

umhodcm 

umhodcm 

umhodcm 

umhodcm 

mglL 

mglL 

Page 157 of 176




Sulfate 12143-45-2 1950-88 14SEP1988 WG 5.00E+00 < HT mglL 

Sulfate 

Sulfate 

Sulfate 

Suspended Alpha 





Suspended Beta 





TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

Tantalum 

Tantalum.Dissolved 

Technetium-99 

Technetium99 

Technetium-99 

Technetiurn-99 

Technetium-99 

Technetium-99 

Temperature 

Temperature 

Thallium 


Thorium 

Thorium. Dissolved 

Tin 


Titanium 

Titanium, Dissolved 















Tungsten 


Turbidity 

Turbidity 

Turbidity 

Turbidity 

Uranium 

Uranium 

Uranium 

Uranium 


Vanadium 


Zinc 

Zinc 

Zinc 

Zinc 

12143-45-2 

12143-45-2 

12 143-452 

GA SUSP 

GA SUSP 

GA SUSP 

GA SUSP 

GA SUSP 

GB SUSP 

GB SUSP 

GB SUSP 

GB SUSP 

GB SUSP 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

7440-25-7 

7440-25-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

SO835 

SO835 

7440-28-0 

7440-28-0 

7440-29-1 

7440-29-1 

7440-31-5 

7440-31-5 

7440-32-6 

7440-34-6 

7440-44-0 

744044-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

744044-0 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

7440-33-7 

7440-33-7 

SO278 

SO278 

SO278 

SO278 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

DIS U 

7440-62-2 

7440-62-2 

7440-66-6 

7440-66-6 

7440-666 

7440-66-6 

3016-91 

4099-92 

5406-92 

1950-88 

2295-89 

2979-90 

3016-91 

5406-92 

1950-88 

2295-89 

2979-90 

3016-91 

5406-92 

1950-88 

3016-91 

3038-91 

3039-91 

3040-91 

5406-92 

5407-92 

5408-92 

5409-92 

4099-92 

4099-92 

1950-88 

2295-89 

2979-90 

3016-91 

4099-92 

5406-92 

3016-91 

5406-92 

4099-92 

4099-92 

4099-92 

4099-92 

4099-92 

4099-92 

4099-92 

4099 - 92 

1950-88 

3016-91 

302-91 

3039-91 

3040-91 

5406-92 

5407-92 

5408-92 

5409-92 

1950-88 

2295-89 

301691 

3098-91 

5406-92 

4099-92 

4099-92 

1950-88 

3016-91 

4099-92 

5406-92 

195088 

3016-91 

4099-92 

5406-92 

4099-9? 

4099-92 

4099-92 

1950-88 

2295-89 

2979-90 

3016-91 

29AUG1991 

01 FEB1992 

11 AUGI 992 

14SEP1988 

25AUG1989 

OSSEP1990 

29AUG 1991 

llAUG1992 

14SEP1988 

25AUG1989 

O5SEPl 990 

29AUG1991 

11 AUGl992 

14SEP1988 

29AUG1991 

29AUG1991 

29AUGl991 

29AUG1991 

11 AUGl992 

11AUG1992 

11 AUG 1992 

11 AUG 1992 

01 FEBI 992 

01FEBl992 

14SEPl988 

25AUG1989 

OSSEPl990 

29AUGl991 

OlFEB1992 

llAUG1992 

29AUG1991 

I AUG1992 

01 FEBI 992 

01FEBl992 

01FEBl992 

01FEBl992 

01FEB1992 

01 FEB 1992 

01 FEB1992 

01 FEBl992 

14SEPl988 

29AUGl991 

29AUGl991 

29AUG1991 

29AUG1991 

1 AUG 1992 

llAUGl992 

1 AUGl992 

11 AUGl992 

14SEP1988 

25AUGl989 

29AUGl991 

OSSEPI 991 

1 I AUGI 992 

01 FEE1992 

01 FEBI 992 

14SEPI 988 

29AUG1991 

OlFEB1992 

llAUG1992 

14SEP1988 

29AUG1991 

01FEB1992 

llAUG1992 

01 FEBI 992 

01 FEBI 992 

OlEB1992 

I ~SEP~ 9aa 

25AUG1989 

OSSEPI 990 

29AUG1991 

Page 158 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

m 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

5.00E+00 

l.OOE+OI 

8.00E+00 

O.OOE+OO 

1.00€+00 


-2.00E+00 0.00€+00 

-4.00€+00 3.00E+00 

3.00E+00 

l.OOE+Ol 

-1.30E+01 

-1.20E+01 O.OOE+OO 

-6.00E+00 2.00E+00 

9.00E+00 

l.lOE+Ol 

5.00E+00 

1.80E+01 

1.30E+01 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

O.OOE+OO 

O.OOE+OO 

2.50E+01 

2.50€+01 

O.OOE+OO 

7.00E+00 0.00€+00 

4.00E+00 O.OOE+OO 

1.60E+01 l.lOE+Ol 

7.10E+01 

6.90E+01 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

O.WE+OO 

1 .WE+W 

l.OOE+Ol 

5.00E+00 

6.00E+00 


I .WE+00 

1.00E+00 

1.00E+00 

l.OOE+OO 

I .00E+W 

1.00€+00 

I.WE+OO 

l.OOE+OO 

1 .WE+00 

l.OOE+OO 

O.OOE+OO 

9.00E+00 

8.00E+00 

I .40E+01 

2.30E+01 

O.OOE+OO 

O.OOE+W 

O.WE+OO 

O.OOE+W 

O.WE+W 

O.OOE+OO 

O.OOE+OO 

2.30E+01 

5.30E+Ol 

2.WE+01 

l.lOE+Ol 

< N 

N 

N 

NT 

NT 

NT 

N 

N 

NT 

NT 

NT 

N 

N 

J 

UJ 

J 

J 

< 

< 

< 

< 

< 

< 

< 

HT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

HT 

HT 

HT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

T 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

NT 

N 

N 

N 

N 

N 

HT 

N 

N 

N 

T 

N 

N 

N 

N 

N 

N 

T 

HT 

T 

N 

mglL 

mglL 

mglL 

PCYL 

pCiL 

pCiL 

pCVL 

PCYL 

pCYL 

pCYL 

pCVL 

pCiL 

pCYL 

ug1L 

uglL 

uglL 

ug1L 

uglL 

uglL 

uglL 

uglL 

uglL 

mglL 

mglL 

pCVL 

pCiL 

pCi 

PCiL 

pCiL 

pCYL 

F 

F 

mglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

mglL 

mglL 

mgn 

mglL 

mglL 

mglL 

mgk 

mg/L 

mg/L 

mglL 

mglL 

uglL 

ugk 

uglL 

ugk 

UglL 

mglL 

mg1L 

NTU 

NTU 

NTU 

N N 

mgk 

mgk 

mgk 

mgfl 

mgk 

mgn 

mgfl 

mgk 

mg/L 

W L 

mgk



ANALYE CAS NUMBER SAMPLE ID DATE lYPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Zinc 7440-66-6 4099-92 01FEB1992 WG 3.50E+01 N mq1L 

Zinc 


N 

N 

Zirconium 


< 

< 

N 

N 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

WAG 7, S WU 8, MW25 


Technetium-99 


WAG 7. SWvlU 8, MW26 

Alkalinity 

Alkalinity 

Alkalinity 

Aluminum 


Americium 241 

Americium 241 

Americium 241’ 

Americium 241 

Antimony 


Arsenic 


Barium 


Beryllium 


Bismuth 

Bismuth. Dissolved 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 

Cadmium 


Calcium 

Calcium 

Calcium 

Calcium 

Calcium 

Calcium 


Cesium1 37 

Cesium137 

Cesium-137 

Cesium-I 37 

Chloride 

Chloride 

Chloride 

Chloride 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 


Coball 

Coball 60 

Cobalt 60 

Cobalt 60 

Cobalt 60 

7440-66-6 

7440-66-6 

7440-67-7 

7440-67-7 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

DTW 

141 33-76-7 

79-01-6 

471-34-1 

471-34-1 

471-34-1 

7429-90-5 

7429-90-5 

AM241 

AM241 

AM241 

AM241 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

7440-41 -7 

7440-41-7 

7440-69-9 

7440-69-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

10045-97-3 

10045-97-3 

10045-97-3 

10045-97-3 

16887-00-6 

16887-00-6 

16887-00-6 

16887-00-6 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-484 

10198-40-0 

10198-40-0 

10198-40-0 

10198-40-0 

5406-92 

4099-92 

4099-92 

4099-92 

1950-88 

3016-91 

3038-91 

3039-91 

3040-91 

5406-92 

5407-92 

5408-92 

5409-92 

1952-88 

1952-88 

1952-88 

3017-91 

4101-92 

5410-92 

4101 -92 

4101-92 

2292-89 

2980-90 

3017-91 

5410-92 

4101 -92 

4101-92 

4101-92 

4101 -92 

4101-92 

4101-92 

4101-92 

4101-92 

4101-92 

4101-92 

1843-88 

2292-89 

2980-90 

3017-91 

4101-92 

5410-92 

4101-92 

1843-88 

2292-89 

2980-90 

3017-91 

4101-92 

5410-92 

4101-92 

2292-89 

2980-90 

3017-91 

5410-92 

1843-88 

3017-91 

4101-92 

5410-92 

1843-88 

2292-89 

2980-90 

3017-91 

4101-92 

5410-92 

4101 -92 

4101 -92 

2292-89 

2980-90 

3017-91 

5410-92 

11AUG1992 

01FEB1992 

01 FEB1992 

01 FEB1992 

14SEP1988 

29AUG1991 

29AUGl991 

29AUG1991 

29AUG1991 

11AUG1992 

11AUG1992 

llAUG1992 

1 1 AUGl992 

14SEP1988 

14SEP1988 

14SEP1988 

28AUGl991 

01 FEB1992 

llAUG1992 

01 FEB1992 

01FEB1992 

23AUG1989 

04SEP1990 

28AUGl991 

1 lAUG1992 

01 FEB1992 

01FEB1992 

01FEB1992 

01 FEBl992 

01 FEB1992 

01FEB1992 

01FEB1992 

OlFEBl992 

01FEB1992 

01FEB1992 

01SEP1988 

23AUG1989 

04SEP1990 

28AUG1991 

01 FEB1992 

llAUGl992 

01 FEBI 992 

01SEP1988 

23AUGl989 

04SEPI 990 

28AUG1991 

01FEBl992 

I 1 AUGl992 

01FEBl992 

23AUG1989 

04SEP1990 

28AUG1991 

11 AUGl992 

OlSEP1988 

28AUG1991 

01 FEB1992 

11 AUGl992 

OlSEPl988 

23AUG1989 

04SEPl990 

28AUGl991 

OlFEB1992 

I AUGI 992 

01FEBl992 

01FEB1992 

23AUG1989 

04SEP1990 

28AUGl991 

11AUG1992 

Page 159 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

w 

WG 

WG 

WG 

WG 

WG 

w 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

w 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

w 

w 

WG 

WG 

w 

WG 

WG 

WG 

w 

c 

< 

< 

< 

< 

< 

< 

< 

N 

N 

N 

N 

N 

NT 

NT 

N 

N 

N 

N 

N 

NT 

NT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

HT 

T 

T 

N 

N 

N 

N 

HT 

HT 

HT 

N 

N 

N 

N 

NT 

NT 

N 

N 

HT 

N 

N 

N 

T 

T 

T 

N 

N 

N 

N 

N 

NT 

NT 

N 

N 

mglL 

mglL 

mglL 

mglL 

su 

su 

su 

su 

su 

su 

su 

su 

su 

Feet 

pCiL 

uglL 

mglL 

mglL 

mglL 

mglL 

mglL 

pCiL 

pCVL 

pCiL 

pCilL 

mglL 

WlL 

mglL 

mglL 

mgfl 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

mgfl 

mglL 

mglL 

mglL 

pCilL 

pCiL 

pCVL 

pCVL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

Wfl 

mg/L 

mglL 

mgfl 

pCilL 

pcin 

pcin 

PCiR




Cobalt, Dissolved 7440-48-4 4101-92 01FEB1992 WG O.OOE+OO < N mglL 

Color 

Color 

Color 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 



Depth lo Water 

















Fluoride 

Fluoride 

Fluoride 

GCMS Scan 

Gross Alpha 

Gross Beta 




Iron 

Iron 

Iron 

Iron 

Iron 

Iron 


Lead 

Lead 

Lead 

Lead 

Lead 

Lead 


Lithium 

Lithium, Dissolved 

M Alkalinity 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 


Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 


Mercury 

Mercury. Dissolved 

Molybdenum 

COLOR 

COLOR 

COLOR 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

DTW 

DTW 

DTW 

DTW 

ALPHA DIS 

ALPHA DIS 

ALPHA DIS 

ALPHA DIS 

ALPHA DIS 

BETA DIS 

BETA DIS 

BETA DIS 

BETA DIS 

BETA DIS 

SO266 

SO266 

SO266 

SO266 

16984-48-8 

I 6984-48-8 

16984-48-8 

GCMS SCAN 

12587-46-1 

12587-47-2 

18540-29-9 

18540-29-9 

18540-29-9 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-93-2 

7439-93-2 

M ALKALINITY 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7439-98-7 

3017-91 

4101 -92 

5410-92 

1843-88 

2292-89 

2980-90 

3017-91 

4101-92 

5410-92 

4101-92 

2292-89 

2980-90 

3017-91 

5410-92 

1843-88 

2292-89 

2980-90 

3017-91 

5410-92 

1843-88 

2292-89 

2980-90 

3017-91 

5410-92 

1843-88 

3017-91 

4101-92 

5410-92 

3017-91 

4101-92 

5410-92 

4101-92 

4101-92 

4101-92 

1843-88 

3017-91 

5410-92 

1843-88 

2292-89 

2980-90 

3017-91 

4101-92 

5410-92 

4101-92 

1843-88 

2292-89 

2980-90 

3017-91 

4101-92 

5410-92 

4101-92 

4101-92 

4101-92 

1843-88 

1843-88 

2292-89 

2980-90 

3017-91 

4101-92 

5410-92 

4101 -92 

1843-88 

2292-89 

2980-90 

3017-91 

4101 -92 

5410-92 

4101-92 

4101 -92 

4101 -92 

4101-92 

28AUG 199 1 

OlFEB1992 

11AUG1992 

01SEPl988 

23AUGl989 

04SEP1990 

28AUG1991 

01 FEBl 992 

11AUG1992 

01 FEE1992 

23AUG1989 

04SEP1990 

28AUG1991 

11AUGl992 

01SEP1988 

23AUG1989 

04SEP1990 

28AUG1991 

1 1 AUGl992 

01SEP1988 

23AUGl989 

04SEP1990 

28AUG1991 

1 1 AUG 1992 

01SEP1988 

28AUG1991 

01 FEBI 992 

1 1AUG1992 

28AUG1991 

OlFEBl992 

1 1 AUGI 992 

01 FEBl992 

01FEBl992 

01 FEE1992 

01SEP1988 

28AUG1991 

1 1 AUG 1992 

OlSEPl988 

23AUGl989 

04SEPl990 

28AUG1991 

01FEB1992 

1 1 AUG 1992 

01 FEB1992 

01 SEP1988 

23AUG1989 

04SEP1990 

28AUG 1991 

01FEB1992 

1 1 AUG 1992 

01FEB1992 

01FEB1992 

01FEB1992 

OISEPI988 

OlSEPl988 

23AUGl989 

04SEP1990 

28AUGl99 1 

01 FEB1992 

1 1 AUG 1992 

01 FEB1992 

01SEP1988 

23AUG1989 

04SEP1990 

28AUGl991 

01FEB1992 

llAUGl992 

OlFEBl992 

OlFEB1992 

OlFEB1992 

OlFEBl992 

Page 160 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

2.80E+01 

6.50E+01 

I .80E+02 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

3.40E+01 

3.20E+01 

2.50E+01 

3.30E+01 

1.50E+01 

l.OOE+Ol 

1 .WE+00 

3.OOE+00 O.OOE+OO 

3.OOE+00 l.OOE+OO 

3.60E+01 

-4.00E+00 

l.OOE+OO 

2.20E+01 O.OOE+OO 

2.10E+01 5.00E+00 

2.44E+02 

I .73E+02 

2.30E+02 

2.24E+02 

O.WE+W 

3.95E+02 

O.WE+OO 

O.WE+OO 

2.00E+00 O.OOE+OO 


O.WE+OO 

O.OOE+OO 

O.OOE+OO 

1.80E+OI 

O.OOE+OO 

I .00E+00 

3.50E+01 



O.WE+OO 

1 .WE+00 

O.OOE+W 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+W 

O.WE+W 

2.32E+02 


3.WE+OI 

3.70E+01 

2.90E+01 

2.30E+01 

1.60E+01 

2.20E+01 

O.OOE+W 

O.WE+OO 

O.WE+OO 

O.OOE+W 

O.WE+W 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.WE+OO 

< 

a 

< 

< 

c 

< 

< 

< 

< 

< 

N 

N 

N 

HT 

HT 

HT 

N 

N 

N 

N 

N 

N 

N 

NT 

NT 

NT 

N 

N 

NT 

NT 

NT 

N 

N 

HT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

N 

N 

HT 

HT 

HT 

N 

N 

N 

N 

HT 

HT 

HT 

N 

N 

N 

N 

N 

N 

NT 

HT 

HT 

HT 

N 

N 

N 

N 

HT 

HT 

HT 

N 

N 

N 

N 

N 

N 

N




Molybdenum, Dissolved 7439-98-7 4101-92 01FEB1992 WG O.OOE+OO 

C 

N 

mglL 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 


Niobium 






PCB 

PCB 





7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-03-1 

7440-03-1 

NITRATEASNIT 

NITRATEASNIT 

NITRATEASNIT 

NITRATEASNIT 

1336-36-3 

1336-36-3 

PHOSPHATEASP 

PHOSPHATEASP 

PHOSPHATEASP 

PHOSPHATEASP 

1843-88 

2292-89 

2980-90 

3017-91 

4101-92 

5410-92 

4101 -92 

4101-92 

4101-92 

1843-88 

3017-91 

4101 -92 

5410-92 

3017-91 

5410-92 

1843-88 

3017-91 

4101-92 

5410-92 

01SEP1988 

23AUG1989 

04SEP1990 

28AUG1991 

01 FEB1992 

1 lAUG 1992 

01 FEB1992 

01FEB1992 

01FEB1992 

01SEP1988 

28AUGl991 

01 FEBl992 

1 lAUGl992 

28AUG1991 

llAUG1992 

01SEP1988 

28AUG 1991 

01 FEE1992 

11AUG1992 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

wr; 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

O.OOE+OO 

O.OOE+OO 

2.00E+00 

2.00E+00 

2.00E+00 

2.00E+00 

C 

C 

C 

C 

C 

C 

< 

C 

C 

C 

C 

C 

C 

C 

C 

< 

HT 

T 

T 

N 

N 

N 

N 

N 

N 

T 

N 

N 

N 

N 

N 

T 

N 

N 

N 

mglL 

mglL 

mglL 

mg1L 

mglL 

mg/L 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mglL 



Potassium 


Radium226 

Radium-226 

7723-14-0 

7723-14-0 

7440-09-7 

7440-09-7 

13982-63-3 

13982-63-3 

4101 -92 

4101 -92 

4101-92 

4101-92 

2292-89 

2980-90 

01 FEBl992 

01 FEE1992 

01 FEE1992 

01 FEE1992 

23AUG1989 

04SEP1990 

WG 

WG 

WG 

WG 

WG 

WG 

l.OOE+OO 

O.OOE+OO 

9.00E+00 

l.OOE+Ol 

O.OOE+OO 

O.OOE+OO 

N 

N 

N 

N 

NT 

NT 

mglL 

mglL 

mglL 

mg1L 

pCVL 

pciR 

Radium226 

13982-63-3 

3017-91 28AUGl991 WG l.OOE+OO O.OOE+OO 

N 

pCiL 

Radium-226 

13982-63-3 

5410-92 llAUG1992 WG O.OOE+OO O.OOE+OO 

N 

pCiL 

Ruthenium 


Selenium 

Selenium 

Selenium 

Selenium 

Selenium 


Silicon 


Silver 


Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 











Strontium 


Sulfate 

Sulfate 

Sulfate 

Sulfate 











7440-18-8 

7440-18-8 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

7440-21-3 

7440-21-3 

7440-22-4 

7440-22-4 

7440-235 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

7440-24-6 

7440-24-6 

12143-45-2 

12143-45-2 

12143-45-2 

12143-45-2 

GA SUSP 

GA SUSP 

GA SUSP 

GA SUSP 

GA SUSP 

GB SUSP 

GB SUSP 

GB SUSP 

GB SUSP 

GB SUSP 

4101-92 

4101-92 

1843-88 

2980-90 

3017-91 

4101-92 

5410-92 

4101 -92 

4101 -92 

4101 -92 

4101 -92 

4101-92 

1843-88 

2292-89 

2980-90 

3017-91 

4101-92 

5410-92 

4101-92 

3017-91 

3032-91 

3033-91 

3034-91 

4101-92 

5410-92 

5411-92 

5412-92 

5413-92 

4101 -92 

4101-92 

1843-88 

3017-91 

4101 -92 

5410-92 

1843-88 

2292-89 

2980-90 

3017-91 

5410-92 

1843-88 

2292-89 

2980-90 

3017-91 

5410-92 

OlFEB1992 

OlFEBl992 

01SEP1988 

MSEPl990 

28AUG1991 

01 FEE1 992 

11AUGl992 

01FEB1992 

01FEBl992 

01 FEE1992 

01FEB1992 

01 FEE1992 

01 SEP1988 

23AUG1989 

04s EP 1990 

28AUGl991 

01 FEE1992 

11 AUGl992 

01FEB1992 

28AUG1991 

28AUGl991 

28AUG1991 

28AUG1991 

01FEB1992 

1 AUGl992 

11AUG1992 

11AUGl992 

1 lAUGl992 

OlFEBl992 

01FEBl992 

01SEPl988 

28AUGl991 

01 FEE1992 

llAUG1992 

01SEPl988 

23AUGl989 

04SEP1990 

28AUG1991 

1 lAUG 1992 

01 SEPl988 

23AUG1989 

MSEPl990 

28AUGl991 

1 lAUG 1992 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

W E 

WG 

O.OOE+OO 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

0.00E+00 

8.00E+00 

6.00E+00 

0.00E+00 

O.OOE+OO 

l.OOE+OO 

1.60E+01 

l.OOE+OO 

l.OOE+OO 

l.OOE+OO 

2 .OOE+ 00 

2.00E+00 

2.73E+02 




0.00E+00 

2.75E+02 

7.00E+00 

0.00E+00 

0.00E+00 

l.OOE+OO 

0.00E+00 

l.lOE+Ol 

2.20E+01 

2.40E+01 

1.20E+Ol 

3.00E+00 

2.00E+00 

3.00E+00 

-2.00€+00 O.OOE+OO 

-2.00E+00 1.00E+00 

-3.00E+00 

-1.00E+00 

-9.00E+00 

-3.00E+00 O.OOE+OO 

1 .00E+00 O.OOE+OO 

C 

C 

< 

C 

C 

C 

C 

C 

C 

< 

N 

N 

T 

T 

N 

N 

N 

N 

N 

N 

N 

N 

T 

HT 

T 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

HT 

N 

N 

N 

NT 

NT 

NT 

N 

N 

NT 

NT 

NT 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

WlL 

mglL 

mglL 

mg1L 

mglL 

mglL 

WIL 

mgfl 

WlL 

mglL 

WIL 

mglL 

umhodcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhodcm 

umhodcm 

UMHOSICM 

UMHOSICM 

UMHOSICM 

mglL 

WlL 

mglL 

mglL 

mglL 

mglL 

pCVL 

pCiL 

pCilL 

pCiL 

pCiL 

pCiL 

pCiL 

pCVL 

pciR 

pCilL 

Page 161 of 176




TOX TOX 2292-89 23AUG1989 WG 6.90E+01 HT ug1L 

TOX 

TOX 

TOX 

TOX 

TOX 

Tantalum 

Tantalum,Dissolved 

Technetium-99 

Technetium-99 

Technetium-99 

Technetium-99 

Technetium-99 

Technetium-99 

Temperature 

Temperature 

Thallium 


Thorium 


Tin 


Titanium 

lidanium, Dissolved 













Tungsten 


Turbidity 

Turbidity 

Turbidity 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 


Vanadium 

Vanadium, Dksolved 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 


Zirconium 


PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

WAG 7, S WU 8. W 7 

1 ,l .l-Trichloroethane 


1.1.2.2-Tetrachloroethane 

1 ,1.2,2-Tetrachloroethane 

1 ,1,2-Trichloroethane 

TOX 

TOX 

TOX 

TOX 

TOX 

7440-25-7 

7440-25-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

SO835 

SO835 

7440-28-0 

7440-280 

7440-29-1 

7440-29-1 

7440-31-5 

7440-31-5 

7440-32-6 

7440-34-6 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-444 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

7440-33-7 

7440-33-7 

SO278 

SO278 

SO278 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

7440-61-1 

DIS U 

7440-62-2 

7440-62-2 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-67-7 

7440-67-7 

so296 

so296 

so296 

SO296 

so296 

SO296 

so296 

so296 

7 1-556 

71-55-6 

79-345 

79-34-5 

79-00-5 

2980-90 

3017-91 

3032-91 

3033-91 

3034-91 

4101-92 

4101-92 

1843-88 

2292-89 

2980-90 

3017-91 

4101-92 

5410-92 

3017-91 

5410-92 

4101-92 

4101-92 

4101-92 

4101-92 

4101 -92 

4101 -92 

4101-92 

4101 -92 

2292-89 

2980-90 

3017-91 

3032-91 

3033-91 

3034-91 

5410-92 

1843-88 

2292-89 

2980-90 

3017-91 

5410-92 

4101 -92 

4101-92 

3017-91 

4101 -92 

5410-92 

2292-89 

2980-90 

3017-91 

4101 -92 

5410-92 

4101 -92 

4101-92 

4101-92 

1843-88 

2292-89 

2980-90 

3017-91 

4101-92 

5410-92 

4101 -92 

4101-92 

4101-92 

3017-91 

3032-91 

3033-91 

3034-91 

5410-92 

5411-92 

5412-92 

5413-92 

04SEP1990 

28AUGl991 

28AUG1991 

28AUG1991 

28AUGl991 

01FEBl992 

01 FEBl992 

01SEP1988 

23AUG1989 

04SEP1990 

28AUG1991 

01FEBl992 

1 1AUGl992 

28AUG1991 

1 lAUGl992 

01 FEB1992 

OlFEB1992 

01FEBl992 

01FEBl992 

01FEB1992 

01 FEB1992 

01 FEBl992 

01 FEBl992 

23AUG1989 

04SEPl990 

28AUG1991 

28AUG1991 

28AUG1991 

28AUG1991 

llAUGl992 

01SEPl988 

23AUG1989 

04SEPl990 

28AUG1991 

11AUGl992 

01 FEBl992 

01FEB1992 

28AUG1991 

01FEB1992 

11AUG1992 

23AUG1989 

04SEPl990 

28AUG 1991 

OlFEBl992 

llAUG1992 

OlFEB1992 

01FEBl992 

OlFEB1992 

OlSEP1988 

23AUG1989 

04SEP1990 

28AUGl991 

OlFEB1992 

llAUG1992 

01FEB1992 

01FEBl992 

01FEBl992 

28AUG1991 

28AUG1991 

28AUG1991 

28AUG199 1 

llAUG1992 

llAUG1992 

11AUGl992 

llAUGl992 

CH200029-00000 190CT1989 

CH200631-00000 22AUG1990 

CH200029-00000 190CT1989 

CH200631-00000 22AUG1990 

CH200029-00000 190CTl989 

Page 162 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

w 

w 

WG 

WG 

w 

WG 

WG 

WG 

WG 

WG 

w 

WG 

WG 

WG 

WG 

WG 

w 

WG 

WG 

WG 

WG 

wc, 

WG 

wc, 

WG 

WG 

WG 

w 

HT 

J 

N 

J 

N 

J 

N 

Q 

N 

< N 

< N 

C 

HT 

T 

T 

N 

N 

N 

N 

< 

< 

N 

N 

N 

N 

N 

N 

N 

N 

HT 

T 

N 

N 

N 

N 

N 

NT 

NT 

NT 

N 

N 

N 

N 

N 

N 

N 

HT 

HT 

N 

N 

N 

N 

N 

N 

HT 

HT 

HT 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N




1.1.2-Trichloroethane 79-00-5 CH200631-00000 22AUG1990 WG 5.00E+00 U ug/L 





1.2.4-Trichlorobenzene 









1 ,4-Dichlorobenzene 



2 ,4-Dichlorophenol 





2-Butanone 

2-Butanone 



2-Hexanone 

2-Hexanone 




2-Nitrophenol 

3,3'-Dichlorobenzidine 



4,4'-DDE 

4,4-DDT 

4.6-Dinitro-2-methylphenol 









4-Nitrophenol 

Acenaphthene 


Acetone 

Acetone 

Aldrin 

Alkalinity 

Alkalinity 

Alkalinity 

Alkalinity 

Alkalinity 

Alkalinity 

Aluminum 

Aluminum 

Aluminum 


Americium 241 

Americium 241 

Americium 241 

Americium 241 

Americium 241 

Anthracene 

Antimony 

Antimony 

Antimony 


75-34-3 

75-34-3 

75-35-4 

75-35-4 

120-82-1 

95-50-1 

107-06-2 

107-06-2 

540-59-0 

540 - 59 - 0 

78-87-5 

78-87-5 

541 -73-1 

106-46-7 

95-95-4 

88-06-2 

120-83-2 

105-67-9 

51-28-5 

121 -14-2 

606-20-2 

78-93-3 

78-93-3 

91-58-7 

95-57-8 

591-78-6 

591-78-6 

91-57-6 

95-48-7 

88-74-4 

88-75-5 

91-94-1 

99 - 09 - 2 

72-54-8 

72-55-9 

50-29-3 

534-52-1 

101-55-3 

59-50-7 

106-47-8 

7005-72-3 

108-10-1 

108-10-1 

106-44-5 

100-01-6 

100-02-7 

83-32-9 

208-96-8 

67-64-1 

67-64-1 

309-00-2 

471 -34-1 

471-34-1 

471-34-1 

471-34-1 

471-34-1 

471-34-1 

7429-90-5 

7429-90-5 

7429-90-5 

7429-90-5 

AM241 

AM241 

AM241 

AM241 

AM241 

120-12-7 

7440-36-0 

7440-36-0 

7440-36-0 

7440-36-0 

CH200029-00000 

CH200631-00000 

CH200029-00000 

CH200631-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200631-00000 

CH200029-00000 

CH200631-00000 

CH200029-00000 

CH200631-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200631-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200631-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200631-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200631-00000 

CH200029-00000 

143888 

2293-89 

2981-90 

301891 

4102-92 

5414-92 

4102-92 

CH200029-00000 

CH200029-DIS 

4102-92 

143888 

2293-89 

2981-90 

3018-91 

5414-92 

CH200029-00000 

4102-92 

CH200029-00000 

CH200029-DIS 

4102-92 

190CT1989 

22AUG1990 

190CT1989 

22AUG1990 

190CT1989 

190CT1989 

190CT1989 

22AUGl990 

190CT1989 

22AUG 1990 

190CT1989 

22AUG1990 

190CT1989 

190CT1989 

19OCTl989 

190CT1989 

190CT1989 

190CT1989 

190CT1989 

190CT1989 

190CT1989 

190CT1989 

22AUG1990 

190CT1989 

lOOCTl989 

190CTl989 

22AUG1990 

190CT1989 

190CT1989 

190CT1989 

190CT1989 

190CT1989 

190CT1989 

190CT1989 

190CTl989 

190CT1989 

190CT1989 

190CT1989 

19OCTl989 

190CT1989 

190CT1989 

190CT1989 

22AUG1990 

190CTl989 

19OCTl989 

190CT1989 

190CTl989 

190CT1989 

190CT1989 

22AUG1990 

190CT1989 

1 OAUGl988 

23AUG1989 

05SEP1990 

O5SEP1991 

01 FEB1992 

1 1 AUGl992 

01 FEBl992 

190CT1989 

lSOCTl989 

01FEB1992 

1 OAUGl988 

23AUG1989 

05SEP1990 

05SEP1991 

llAUG1992 

190CT1989 

01FEB1992 

190CT1989 

190CTl989 

01FEB1992 

Page 163 of 176 

w 

WG 

WG 

WG 

WG 

w 

w 

WG 

WG 

WG 

w 

WG 

w 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

wc, 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

wc, 

WG 

WG 

w 

WG 

WG 

wc, 

WG 

WG 

WG 

w 

WG 

WG 

w 

WG 

WG 

wc, 

WG 

\I\EG 

wc, 

WG 

WG 

WG 

WG 

WG 

wc, 

wc, 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

w 

w 

WG 

WG 

WG 

w 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

l.OOE+Ol 

1.00Et01 

5.00E+00 

5.00Et00 

5.00E+00 

5.00E+00 

5.00Et00 

5.00E+00 

l.OOE+Ol 

l.OOE+Ol 

5.00Et01 

1.00Et01 

1.00Et01 

1.00Et01 

5.00E+01 

l.OOE+Ol 

l.OOE+Ol 

l.OOE+Ol 

6.00€+00 

1.00Et01 

l.OOE+Ol 

1.00E+01 

l.OOE+W 

l.OOE+Ol 

1.00E+01 

5.00E+01 

l.OOE+Ol 

2.00E+01 

5.00E+01 

0.00E+00 

O.OOE+OO 

O.OOE+OO 

5.00E+01 

1.00Et01 

1.00E+01 

1.00Et01 

l.OOE+Ol 

1.00Et01 

l.OOE+Ol 

1.00Et01 

5.00Et01 

5.00E+01 

1.00Et01 

1.00Et01 

l.OOE+Ol 


0.00E+00 

7.00E+01 

1.01 Et02 

1.01Et02 

6.6OE+Ol 

9.10Et01 

8.80E+01 

0.00E+00 

1.00E+00 

0.00E+00 

0.00€+00 

1 .00E+00 

1.00Et00 

-5.00€+00 

0.00E+00 O.OOE+OO 

-1.00E+00 0.00Et00 

1.00E+01 

O.OOE+OO 

O.OOE+OO 

0.00Et00 

O.OOE+OO 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

J 

U 

U 

U 

J 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

BE 

U 

U' 

< 

R 

J 

J 

R 

R 

R 

J 

HT 

HT 

HT 

N 

N 

N 

N 

N 

NT 

NT 

NT 

N 

N 

N 

N 

ug1L 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ugfl 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

pCVL 

pci5 

pci5 

pci5 

pCiL 

Wfl 

mgfl 

WlL 

WR 

Wfl




Arsenic 

7440-38-2 4102-92 01FEB1992 WG O.OOE+OO c 

N mg1L 

Arsenic 

Arsenic 

7440-38-2 

7440-38-2 

CH200029-00000 

CH200029-DIS 

190CTl989 

190CTl989 

WG 

WG 

O.OOE+OO 

O.OOE+OO 

U 

U 


7440-38-2 

4102-92 01 FEE1992 WG O.OOE+OO 

C 

Barium 

7440-39-3 

4102-92 OlFEB1992 w O.OOE+OO 

Barium 

Barium 


Benzene 

Benzene 





7440-39-3 

7440-39-3 

7440-39-3 

71 -43-2 

71-43-2 

56-55-3 

50-32-8 

205-99-2 

191-24-2 

CH200029-00000 

CH200029-DIS 

4102-92 

CH200029-00000 

CH200631-00000 

CH200029-00000 

CH200029-00000 

CH2 00029-00000 

CH200029-00000 

190CT1989 

190CT1989 

OlFEB1992 

190CT1989 

22AUG1990 

190CT1989 

190CT1989 

190CT1989 

190CT1989 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

5.00€+00 

5.00E+00 

l.OOE+Ol 

l.OOE+Ol 

l.OOE+Ol 

l.OOE+Ol 

B' 

B' 

U 

U 

U 

U 

U 

U 

Benzo(k)fluoranthene 207-08-9 

CH200029-00000 190CT1989 WG l.OOE+Ol 

U 

Benzoic Acid 

65-85-0 

CH200029-00000 190CT1989 WG 5.00E+01 

U 


100-51-6 

CH200029-00000 190CT1989 w I .00E+01 

U 


Beryllium 

85-68-7 

7440-41-7 

CH200029-00000 

4102-92 

190CT1989 

01 FEE1992 

WG 

WG 

1.00E+01 

O.OOE+OO 

U 

C 

Beryllium 

Beryllium 


Bismuth 


7440-41-7 

7440-41-7 

7440-41-7 

7440-69-9 

7440-69-9 

CH200029-00000 

CH200029-DIS 

4102-92 

4102-92 

4102-92 

190CT1989 

190CT1989 

01 FEBl 992 

01FEB1992 

01FEB1992 

WG 

WG 

WG 

WG 

WG 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

UN 

UN 

c 

C 

C 

Bromodichloromethane 75-27-4 

CH200029-00000 190CT1989 WG 5.00E+00 

U 


CH200631-00000 22AUG1990 w 5.00E+00 

U 

Bromoform 

75-25-2 

CH200029-00000 190CTl989 w 5.00E+00 

U 

Bromoform 

75-25-2 

CH200631-00000 22AUG1990 w 5.00E+00 

U 

Bromomethane 

74-83-9 

CH200029-00000 19OCTI 989 w 1.00E+01 

U 

Bromomethane 

Cadmium 

Cadmium 

Cadmium 

74-83-9 

7440-43-9 

7440-43-9 

7440-43-9 

CH200631-00000 

1438-88 

2293-89 

2981-90 

22AUG1990 

10AUG1988 

23AUG1989 

05SEP1990 

WG 

WG 

WG 

WG 

1.00E+01 

0.00€+00 

0.00€+00 

0.00E+00 

U 

C 

< 

c 

T 

T 

T 

Cadmium 

7440-43-9 

3oia91 05SEP1991 WG 0.00E+00 

C 

N 

Cadmium 

7440-43-9 

4102-92 01FEB1992 w 0.00E+00 

c 

N 

Cadmium 

7440-43-9 

5414-92 I AUG1992 w 0.00E+00 

< 

N 

Cadmium 

7440-43-9 

CH200029-00000 19OCTI 989 WG 0.00E+00 

N 

J 

Cadmium 

7440-43-9 

CH200029-DIS 190CT1989 w 0.00E+00 

N J 


Calcium 

Calcium 

Calcium 

Calcium 

Cakium 

Calcium 

Cakium 

Calcium 


7440-43-9 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

7440-70-2 

4102-92 

1438-88 

2293-89 

2981-90 

3018-91 

4102-92 

5414-92 

CH200029-00000 

CH200029-DIS 

4102-92 

OlFEB1992 

10AUGl988 

23AUGl989 

05SEPl990 

05SEPl991 

01 FEB1992 

1 lAUG1992 

190CT1989 

190CT1989 

01FEB1992 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

O.WE+OO 

1.00E+01 

1.40€+01 

I .50E+Ol 

1.60€+01 

1.60€+01 

1.40€+01 

1.40E+01 

1.40€+01 

1.60E+01 

C 

N 

HT 

HT 

T 

N 

N 

N 

J 

N 





Cesium1 37 

Cesium137 

Cesium-I37 

75-15-0 

75-15-0 

56-23-5 

56-23-5 

10045-97-3 

10045-97-3 

10045-97-3 

CH200029-00000 

CH200631-00000 

CH200029-00000 

CH200631-00000 

1438-88 

2293-89 

2981-90 

190CT1989 

22AUG1990 

190CT1989 

22AUG1990 

IOAUGI 988 

23AUG1989 

05SEPl990 

WG 

WG 

WG 

WG 

WG 

\IK; 

WG 

5.00E+00 

5.00€+00 

5.00E+00 

5.00E+00 

0.00E+00 

0.00E+00 

l.OOE+OO 

U 

U 

U 

U 

NT 

NT 

NT 

Cesium-137 

10045-97-3 

3oiagi O5SEPl 991 WG O.00E+OO 0.00E+00 

N 

Cesium-137 

10045-97-3 

541492 1 lAUGl992 WG 0.00€+00 O.OOE+OO 

N 

Chloride 

16887-00-6 

1438-88 10AUGl988 w 7.90€+01 

T 

Chloride 

Chloride 

Chloride 

Chloride 

Chloride 

Chloride 

16887-00-6 

16887-00-6 

16887-00-6 

16887- 

16887-00-6 

16887-00-6 

2293-89 

2981-90 

3oiagi 

4102-92 

5414-92 

CH200029-00000 

23AUGl989 

05SEP1990 

05SEP1991 

01FEB1992 

llAUG1992 

190CTl989 

WG 

WG 

WG 

WG 

WG 

WG 

8.00E+Ol 

7.90€+01 

7.70€+01 

7.80€+01 

8.6OE+Ol 

0.00€+00 

T 

T 

N 

N 

N 

N 

Chlorobenzene 

Chlorobenzene 

Chloroethane 

Chloroethane 

Chloroform 

Chloroform 

Chloromethane 

Chloromethane 

1 oa90-7 

108-90-7 

75-00-3 

75-00-3 

67-66-3 

67-66-3 

74-87-3 

74-87-3 

CH200029-00000 

CH200631-00000 

CH200029-00000 

CH200631-00000 

CH200029-00000 

CHZW631-00000 

CH200029-00000 

CH200631-00000 

190CT1989 

22AUG1990 

190CT1989 

22AUG1990 

19OCTl989 

22AUG1990 

190CT1989 

22AUG1990 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

5.WE+OO 

5.00E+00 

I .00E+01 

1.00€+01 

3.80E+01 

5.00E+00 

1.00E+01 

l.OOE+OI 

U 

U 

U 

U 

U 

U 

U 

Page 164 of 176




Chromium 7440-47-3 1438-88 10AUG1988 WG O.OOE+OO < T mglL 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 

Chromium 


Chrysene 

Cobalt 

Cobalt 

Coban 

Cobalt 60 

Cobalt 60 

Cobalt 60 

Cobalt 60 

Cobalt 60 


Color 

Color 

Color 

Color 

Color 

Color 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 

Copper 


Cyanide 






Di-n-butylphthalale 

Dkn-octylphthalate 


Dibenzofuran 



Dieldrin 



















Endosulfan I 

Endosulfan I1 


Endrin 

Endrin Ketone 

Ethylbenzene 

Et h y I be N e n e 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

7440-47-3 

218-01-9 

7440-48-4 

7440-48-4 

7440-48-4 

10198-40-0 

10198-40-0 

10198-40-0 

10198-40-0 

10198-40-0 

7440-48-4 

COLOR 

COLOR 

COLOR 

COLOR 

COLOR 

COLOR 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

7440-50-8 

57-12-5 

DTW 

DTW 

DTW 

DTW 

DTW 

84-74-2 

11744-0 

53-70-3 

132-64-9 

124-48-1 

124-481 

60-57-1 

84-66-2 

131-11-3 

ALPHA DIS 

ALPHA DIS 

ALPHA DIS 

ALPHA DIS 

ALPHA DIS 

BETA DIS 

BETA DIS 

BETA DIS 

BETA DIS 

BETA DIS 

SO266 

SO266 

SO266 

SO266 

SO266 

SO266 

959-98-8 

33213-65-9 

1031-07-8 

72-20-8 

53494-70-5 

10041-4 

100-41-4 

2293-89 

2981-90 

3018-91 

4102-92 

5414-92 

CH200029-00000 

CH200029-DIS 

4102-92 

CH200029-00000 

4102-92 

CH200029-00000 

CH200029-DIS 

1438-88 

2293-89 

2981-90 

3018-91 

5414-92 

4102-92 

1438-88 

2293-89 

2981-90 

3018-91 

4102-92 

5414-92 

1438-88 

2293-89 

2981-90 

3018-91 

4102-92 

5414-92 

CH200029-00000 

CH200029-DIS 

4102-92 

CH200029-00000 

1438-88 

2293-89 

2981-90 

3018-91 

5414-92 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200631-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

143888 

2293-89 

2981-90 

3018-91 

5414-92 

1438-88 

2293-89 

2981-90 

3018-91 

541 4-92 

1438-88 

2293-89 

2981-90 

30 18-91 

4102-92 

5414-92 

CH200029-00000 

CH200029-OooOO 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CHZ00029-00000 

CH200631-00000 

23AUG1989 

05SEP1990 

05SEPl991 

01 FEB1992 

llAUG1992 

190CT1989 

190CT1989 

01 FEB1992 

190CT1989 

01 FEB1992 

190CT1989 

190CT1989 

10AUG1988 

23AUG1989 

05SEP1990 

05SEP1991 

11 AUGI 992 

01FEB1992 

10AUG1988 

23AUG1989 

O5SEPl 990 

05SEP1991 

01 FEB1992 

11 AUGl992 

10AUG1988 

23AUGl989 

OSSEPI 990 

05SEPl991 

01FEBl992 

1 I AUGl992 

190CT1989 

190CTI 989 

01 FEBl992 

190CT1989 

10AUG1988 

23AUG1989 

05SEP1990 

05SEPl991 

11 AUGl992 

19OCTI 989 

I 9OCTl 989 

I 9OCTI 989 

190CT1989 

190CT1989 

22AUG1990 

190CT1989 

190CT1989 

190CT1989 

1 OAUG1988 

23AUGl989 

05SEP1990 

O5SEPl 991 

1 I AUGl992 

IOAUGI 988 

23AUGl989 

05SEPl990 

05SEP1991 

1 AUG 1992 

I OAUG 1988 

23AUGl989 

05SEPl990 

O5SEPl 991 

OlFEB1992 

llAUG1992 

190CT1989 

190CT1989 

190CT1989 

190CT1989 

190CT1989 

190CT1989 

22AUG1990 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

m 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WI; 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

< T 

< T 

4 N 

< N 

< N 

B 

B 

< N 

U 

< N 

U 

U 

NT 

NT 

NT 

N 

N 

c 

N 

HT 

HT 

HT 

N 

N 

N 

HT 

HT 

T 

N 

N 

N 

< 

U 

N 

N 

N 

N 

N 

R 

NT 

NT 

NT 

N 

N 

NT 

NT 

NT 

N 

N 

HT 

HT 

HT 

N 

N 

N 

R 

R 

R 

R 

R 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

uglL 

mglL 

mglL 

mglL 

pCilL 

pCilL 

pCilL 

pCilL 

pCilL 

mglL 

Units 

Units 

Units 

units 

Units 

units 

mglL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mgfl 

mg1L 

mglL 

Feet 

Feel 

Feet 

Feet 

Feet 

ug1L 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

pcia 

pci5 

pCilL 

pCilL 

pCilL 

pCilL 

pCiL 

pCiL 

pCilL 

pCiL 

mg1L 

mg1L 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

uglL 

uglL 

ugR 

ugR 

ug1L 

Page 165 of 176



ANALYE CAS NUMBER SAMPLE ID DATE WPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Fluoranthene 206-44-0 CH200029-00000 190CT1989 WG l.OOE+OI U uglL 

Fluorene 

Fluoride 

Fluoride 

Fluoride 

Fluoride 

Fluoride 

GCIMS Scan 


Gross Alpha 

Gross Beta 


Heptachlor 












Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 

Iron 


lsophorone 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 

Lead 


Llhium 

Lithium. Dissolved 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 

Magnesium 


Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 

Manganese 


Mercury 

Mercury 

Mercury 


Methoxychlor 



Molybdenum 


86-73-7 

16984-48-8 

16984-48-8 

16984-48-8 

16984-48-8 

16984-48-8 

GCIMS SCAN 

GAMMA 

12587-46-1 

12587-47-2 

CACOJHARDNES 

76-44-8 

1024-57-3 

118-74-1 

87-68-3 

77-47-4 

67-72-1 

18540-29-9 

18540-29-9 

18540-29-9 

18540-29-9 

18540-29-9 

193-39-5 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

7439-89-6 

78-59-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-92-1 

7439-93-2 

7439-93-2 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-95-4 

7439-954 

7439-95-4 

7439-954 

7439-95-4 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-96-5 

7439-97-6 

7439-976 

7439-97-6 

7439-97-6 

72-43-5 

75-09-2 

75-09-2 

7439-98-7 

7439-98-7 

CH200029-00000 

1438-88 

2293-89 

3018-91 

4102-92 

5414-92 

4102-92 

4102-92 

4102-92 

4102-92 

CH200029-00000 

CH200029-00000 

CH2 00029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

1438-88 

2293-89 

2981-90 

3018-91 

5414-92 

CH200029-00000 

1438-88 

2293-89 

2981-90 

3018-91 

4102-92 

5414-92 

CH200029-00000 

CH200029-DIS 

4102-92 

CH200029-00000 

1438-88 

2293-89 

2981 -90 

3018-91 

4102-92 

5414-92 

CH200029-00000 

CH200029-DIS 

4102-92 

4102-92 

4102-92 

1438-88 

2293-89 

2981-90 

3018-91 

4102-92 

5414-92 

CH200029-00000 

CH200029DIS 

4102-92 

1438-88 

2293-89 

2981-90 

3018-91 

4102-92 

5414-92 

CH200029-00000 

CH200029-DIS 

4102-92 

4102-92 

CH200029-00000 

CH200029-DIS 

4102-92 

CH200029-00000 

CH200029-00000 

CH20063100000 

4102-92 

4 102-92 

190CT1989 

lOAUG1988 

23AUG1989 

05SEP1991 

OlFEBl992 

llAUG1992 

01 FEB1992 

01FEBl992 

OlFEB1992 

01 FEBl992 

190CTl989 

190CT1989 

190CT1989 

190CT1989 

190CTl989 

190CT1989 

19OCTI 989 

lOAUGl988 

23AUGl989 

05SEP1990 

05SEP1991 

11 AUGl992 

190CT1989 

1 OAUGl988 

23AUG1989 

05SEP1990 

05SEP1991 

01 FEBl992 

I AUGI 992 

I 9OCTI 989 

190CTI989 

01FEB1992 

190CT1989 

I OAUG 1988 

23AUG1989 

05SEPI990 

05SEP1991 

01 FEBI 992 

11AUGl992 

190CT1989 

I 9OCTl 989 ' 

OlFEB1992 

OlFEBl992 

OIFEB1992 

I OAUGl988 

23AUG1989 

05SEP1990 

05SEPl991 

01 FEB1992 

1 lAUGl992 

190CT1989 

190CTl 989 

01FEB1992 

lOAUGl988 

23AUG1989 

05SEPl990 

05SEPl991 

01 FEBl992 

I lAUGl992 

I 9OCTI 989 

19OCT1989 

OIFEB1992 

01FEBl992 

19OCTI 989 

190CT1989 

01FEB1992 

190CT1989 

190CTl989 

22AUG1990 

OlFEBl992 

01EB1992 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

wc, 

wc, 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

wc, 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

wc, 

WG 

\M; 

wc, 

WG 

wc, 

WG 

WG 

wc, 

WG 

WG 

U 

Q 

U 

< 

< 

< 

< 

c 

N 

BNW 

< 

N' 

N. 

c 

U 

U 

c 

U 

U 

UB 

c 

< 

T 

T 

N 

N 

N 

N 

N 

N 

N 

N 

R 

NT 

NT 

NT 

N 

N 

HT 

HT 

HT 

N 

N 

N 

J 

J 

N 

HT 

T 

T 

N 

N 

N 

J 

J 

N 

N 

N 

HT 

HT 

HT 

N 

N 

N 

J 

N 

T 

HT 

HT 

N 

N 

N 

J 

N' 

N 

N 

N 

R 

UJ 

N 

N 

Page 166 of 176




N-Nitroso-di-n-propylamine 621-64-7 CH200029-00000 190CT1989 WG 1.00E+01 U ug1L 

N-Nitrosodiphen ylamine 

Naphthalene 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 

Nickel 


Niobium 


Nitrate 







Nitrobenzene 

PCB 

PCB 

PCB 

PCB 

PCB 

PCB 

PCB-1016 

PCB-1221 

PCB-1232 

PCB-1242 

PCB-1248 

PCB-1254 

PCB-1260 


Phenanthrene 

Phenol 









Potassium 

Potassium 

Potassium 


Pyrene 

RAD SCREEN 

Radium226 

Radium226 

Radium226 

Radium-226 

Radium-226 

Ruthenium 


Selenium 

Selenium 

Selenium 

Selenium 

Selenium 

Selenium 

Selenium 

Selenium 


Silicon 


Silver 

Silver 

86-30-6 

91-20-3 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-02-0 

7440-03-1 

7440-03-1 

14797-55-a 

NITRATEASNIT 

NITRATEASNIT 



NITRATEASNIT 

NITRATEASNIT 

98-95-3 

1336-36-3 

1336-36-3 

1336-36-3 

1336-36-3 

1336-36-3 

1336-36-3 

12674-11-2 

11104-28-2 

11141 -16-5 

53469-21-9 

12672-29-6 

11097-69-1 

11096-82-5 

87-86-5 

85-01-8 

108-95-2 

PHOSPHATEASP 

PHOSPHATEASP 

PHOSPHATEASP 

PHOS PHATEAS P 

PHOSPHATEASP 

PHOSPHATEASP 

7723-14-0 

7723-14-0 

7440-09-7 

7440-09-7 

7440-09-7 

7440-09-7 

129-00-0 

R SCREEN 

13982-63-3 

13982-63-3 

13982-63-3 

13982-63-3 

13982-63-3 

7440-18-8 

7440-18-8 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

7782-49-2 

7440-21-3 

7440-21-3 

7440-22-4 

7440-22-4 

CH200029-00000 

CH200029-00000 

1438-88 

2293-89 

2981-90 

3018-91 

4102-92 

5414-92 

CH200029-00000 

CH200029-DIS 

4102-92 

4102-92 

4102-92 

CH200029-00000 

1438-88 

2293-89 

2981-90 

3018-91 

4102-92 

5414-92 

CH200029-00000 

1438-88 

2293-89 

2981-90 

3018-91 

4102-92 

5414-92 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

1438-88 

2293-89 

2981-90 

3018-91 

4102-92 

5414-92 

4102-92 

4102-92 

4102-92 

CH200029-00000 

CH200029-DIS 

4102-92 

CH200029-00000 

2917-89 

1438-88 

2293-89 

2981-90 

3018-91 

5414-92 

4102-92 

4102-92 

1438-88 

2293-89 

2981-90 

3016-91 

4102-92 

5414-92 

CH200029-00000 

CH200029-DIS 

4102-92 

4102-92 

4102-92 

4102-92 


190CT1989 

190CT1989 

10AUG1988 

23AUG1989 

O5SEPl 990 

O5SEPl 991 

01 FEB1992 

11 AUGl992 

190CT1989 

190CT1989 

01 FEE1992 

01 FEBl 992 

01 FEE1992 

190CT1989 

10AUG1988 

23AUG1989 

O5SEPl 990 

05SEP1991 

OlFEB1992 

I 1 AUGI 992 

190CT1989 

10AUGl988 

23AUG1989 

05SEPl990 

05SEPl991 

01FEBl992 

11AUG1992 

190CT1989 

190CTl989 

19OCTI 989 

19OCTl 989 

190CTl989 

190CT1989 

190CTl989 

190CT1989 

1 SOCTI 989 

190CTl989 

1 OAUG 1988 

23AUG1989 

05SEPl990 

OLSEPI 991 

OlFEB1992 

llAUG1992 

01 FEB1992 

01 FEB1992 

01 FEE1992 

190CT1989 

190CT1989 

01 FEB1992 

190CT1989 

190CT1989 

10AUGl988 

23AUG1989 

05SEP1990 

05SEP1991 

11 AUGl992 

01FEB1992 

01FEBl992 

1 OAUG1988 

23AUG1989 

05SEP1990 

05SEPl991 

OlFEB1992 

I AUG1992 

190CT1989 

190CT1989 

01FEB1992 

01FEB1992 

OlFEB1992 

01FEB1992 

190CT1989 

Page 167 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

VbG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

U 

U 

< 

< 

c 

< 

< 

< 

< 

< 

c 

< 

< 

< 

< 

< 

< 

U 

< 

< 

< 

< 

< 

< 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

< 

< 

< 

< 

< 

< 

< 

< 

B 

B 

U 

< 

< 

c 

< 

< 

< 

< 

< 

< 

UN 

UNW 

< 

< 

UN 

T 

T 

T 

N 

N 

N 

N 

N 

N 

N 

T 

T 

T 

N 

N 

N 

HT 

HT 

HT 

N 

N 

N 

T 

T 

T 

N 

N 

N 

N 

N 

N 

B 

B 

N 

NT 

NT 

NT 

NT 

N 

N 

N 

N 

T 

T 

T 

N 

N 

N 

N 

NW 

N 

N 

N 

N 

R 

uglL 

uglL 

mglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg/L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mg1L 

uglL 

uglL 

ug1L 

ug/L 

uglL 

uglL 

uglL 

ug1L 

uglL 

uglL 

ug/L 

uglL 

uglL 

ugfl 

uglL 

uglL 

uglL 

mg/L 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

uglL 

pCilml 

pCiL 

pCilL 

pCilL 

pCiL 

pCVL 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mgfl 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mgfl




Silver 

7440-22-4 CH200029-DIS 190CT1989 WG O.OOE+OO UN R mg1L 


7440-22-4 

4102-92 01 FEBl 992 

c 

N 

mglL 

Sodium 

7440-23-5 

143858 lOAUG1988 

HT mglL 

Sodium 

7440-23-5 

2293 - 89 

23AUGl989 

HT mglL 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

Sodium 

















Strontium 


7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

7440-23-5 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

SO145 

7440-24-6 

7440-24-6 

2981-90 

3018-91 

4102-92 

5414-92 

CH200029-00000 

CH200029-DIS 

4102-92 

1438-88 

1439-88 

1440-88 

1441-88 

2293-89 

2981 -90 

3018-91 

3041-91 

3042-91 

3043-91 

4102-92 

5414-92 

5415-92 

5416-92 

5417-92 

4102-92 

4102-92 

05SEP1990 

05SEPl991 

OlFEB1992 

llAUGl992 

190CT1989 

190CT1989 

01FEB1992 

10AUG1988 

10AUG1988 

10AUG1988 

10AUG1988 

23AUG1989 

OSSEPl990 

05SEP1991 

05SEP1991 

O5SEPl991 

O5SEPl991 

01 FEE1992 

11 AUG 1992 

11 AUG 1992 

11AUG1992 

11 AUG 1992 

01 FEBl 992 

01 FEBl 992 

T 

N 

N 

N 

J 

N 

T 

T 

T 

T 

HT 

T 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

umhodcm 

umhodcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhodcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhoslcm 

umhodcm 

umhoslcm 

umhoslcm 

mglL 

mglL 

Styrene 

Styrene 

S u lfate 

Sulfate 

Sulfate 

Sulfate 

Sulfate 

Sulfate 

Sulfate 

Sulfide 











TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

Tantalum 

Tantaium.Dissolved 

Technetium99 

Technetium99 

Technetium-99 

Technetium99 

Technetium99 

Technetium99 

Temperature 

Temperature 

100-42-5 

100-42-5 

12143-45-2 

12143-45-2 

12143-45-2 

12143-45-2 

12143-45-2 

12143-45-2 

12143-45-2 

18496-25-8 

GA SUSP 

GA SUSP 

GA SUSP 

GA SUSP 

GA SUSP 

GB SUSP 

GB SUSP 

GB SUSP 

GB SUSP 

GB SUSP 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

TOX 

7440-25-7 

7440-25-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

14133-76-7 

SO835 

SO835 

CH200029-00000 

CH200631-00000 

1438-88 

229359 

2981-90 

3018-91 

4102-92 

5414-92 

CH200029-00000 

CH200029-00000 

143858 

229359 

2981-90 

3oiagi 

5414-92 

1438-88 

2293-89 

2981-90 

3018-91 

5414-92 

1438-88 

143988 

1440-88 

144188 

2293-89 

2981-90 

3018-91 

3041-91 

3042-91 

3043-91 

5414-92 

5415-92 

5416-92 

5417-92 

4102-92 

4102-92 

2293-89 

2981-90 

3018-91 

4102-92 

5414-92 

CH200631-00000 

2293-89 

2981-90 

190CT1989 

22AUG1990 

10AUG1988 

23AUG1989 

OSSEPl990 

05SEP1991 

01 FEBl992 

11AUG 1992 

190CT1989 

190CT1989 

10AUG1988 

23AUG1989 

OSSEP1990 

OSSEPl991 

1 lAUG1992 

10AUG1988 

23AUG1989 

05SEPl990 

OSSEP1991 

11AUGI 992 

1 OAUGl988 

10AUGl988 

1 OAUG 1988 

10AUG1988 

23AUG1989 

05SEP1990 

05SEPl991 

05SEPl991 

O5SEPl991 

05SEP1991 

I lAUGl992 

1 lAUGl992 

llAUGl992 

11 AUGl992 

01 FEE1 992 

01 FEBl 992 

23AUG1989 

05SEPl990 

05SEP1991 

01FEB1992 

1 lAUGl992 

22AUG1990 

23AUG 1989 

05SEP1990 

U 

U 

< 

UJ 

J 

J 

J 

c 

< 

UA 

HT 

HT 

T 

N 

N 

N 

N 

N 

NT 

NT 

NT 

N 

N 

NT 

NT 

NT 

N 

N 

T 

HT 

T 

T 

T 

T 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

T 

HT 

N 

N 

N 

H 

uglL 

uglL 

mglL 

mglL 

mglL 

mglL 

mgIL 

mg5 

mglL 

mglL 

pCilL 

pCilL 

pci5 

pCilL 

pCiL 

pCilL 

pCilL 

pCilL 

pCilL 

pci5 

uglL 

uglL 

ug5 

uglL 

ug5 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ug5 

uglL 

ugn 

mg/L 

mg/L 

pCi 

pCiL 

pci5 

pCiL 

pCi 

pci5 

F 

F 

Page 168 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

w 

w 

WG 

WG 

WG 

WG 

w 

w 

WG 

w 

w 

WG 

WG 

w 

w 

WG 

w 

WG 

WG 

w 

w 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

w 

WG 

WG 

WG 

WG 

w 

w 

WG 

WG 

WG 

w 

WG 

WG 

w 

w 

WG 

WG 

WG 

w




Temperature SO835 3018-91 O5SEP1991 WG 6.70E+01 N F 

Temperature 

Temperature 



Thallium 

Thallium 

Thallium 


Thorium 


Tin 


Titanium 

Titanium. Dissolved 

Toluene 

Toluene 













Toxaphene 








Tungsten 


Turbidity 

Turbidity 

Turbidity 

Turbidity 

Turbidity 

Turbidity 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 

Uranium 


Vanadium 

Vanadium 

Vanadium 


Vinyl Acetate 

Vinyl Acetate 



Xylene 

Xylene 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 

Zinc 


Zirconium 

SO835 

SO835 

127-18-4 

127-18-4 

7440-28-0 

7440-28-0 

7440-28-0 

7440-28-0 

7440-29-1 

7440-29-1 

7440-31-5 

7440-31-5 

7440-32-6 

7440-34-6 

108-88-3 

108-88-3 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

8001-35-2 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

79-01-6 

7440-33-7 

7440-33-7 

SO278 

SO278 

SO278 

SO278 

SO278 

SO278 

7440-61-1 

7440-61-1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

7440-61 -1 

DIS U 

7440-62-2 

7440-62-2 

7440-62-2 

7440-62-2 

108-05-4 

108-05-4 

75-01-4 

75-01-4 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-66-6 

7440-666 

7440-67-7 

4102-92 

5414-92 

CH200029-00000 

CH200631-00000 

4102-92 

CH200029-00000 

CH200029-DIS 

4102-92 

4102-92 

4102-92 

4102-92 

4102-92 

4102-92 

4102-92 

CH200029-00000 

CH200631-00000 

143848 

1440-88 

229349 

2981 -90 

3018-91 

3041-91 

3042-91 

3043-91 

5414-92 

5415-92 

5416-92 

5417-92 

CH200029-00000 

143888 

2293-89 

2981-90 

3018-91 

5414-92 

CH200029-00000 

CH200631-00000 

4102-92 

4102-92 

1438-88 

2293-89 

2981-90 

3018-91 

4102-92 

5414-92 

143888 

229399 

2981-90 

3oiagi 

4102-92 

5414-92 

4102-92 

4102-92 

CH200029-00000 

CH200029-DIS 

4102-92 

CH2W029-00000 

CH200631-00000 

CH200029-00000 

CH200631-00000 

CH200029-00000 

CH200631-00000 

143848 

229349 

2981-90 

3018-91 

4102-92 

5414-92 

CH200029-00000 

CH200029-DIS 

4102-92 

4102-92 

01 FEB1992 

11 AUGl992 

190CT1989 

22AUG1990 

01 FEB1992 

190CT1989 

190CT1989 

01FEB1992 

01FEB1992 

01 FEB1992 

01 FEB1992 

01 FEB1992 

01 FEBl992 

01 FEB1992 

190CT1989 

22AUG1990 

10AUG1988 

1 OAUG 1988 

23AUG1989 

05SEPl990 

05SEP1991 

05SEP1991 

05SEPl991 

05SEPl991 

11 AUGl992 

11 AUGl992 

llAUG1992 

llAUGl992 

19OCTl989 

1 OAUGl988 

23AUGl989 

05SEPl990 

OSSEP1991 

I lAUG1992 

190CT1989 

22AUGl990 

01FEB1992 

01FEB1992 

IOAUGI 988 

23AUG1989 

05SEP1990 

05SEP1991 

01 FEBl992 

llAUG1992 

lOAUG1988 

23AUG1989 

OSSEPl990 

05SEP1991 

01FEB1992 

1 lAUGl992 

01FEB1992 

01 FEB1992 

190CT1989 

1 SOCTI 989 

01 FEBl992 

19OCT1989 

22AUG1990 

190CT1989 

22AUG1990 

190CT1989 

22AUG1990 

lOAUGl988 

23AUGl989 

05SEPI 990 

05SEP1991 

OlFEB1992 

1 I AUGl992 

190CT1989 

19OCTl989 

01FEB1992 

OlFEB1992 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

wc. 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

wc. 

WG 

WG 

WG 

ws 

wc. 

WG 

WG 

wc. 

WG 

5.60E+01 

7.40E+01 

5.00E+00 

5.00E+00 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

5.00E+00 

5.00E+00 

6.00E+00 

7.00E+00 

l.OOE+OO 

1 .WE+00 

2.00E+00 

2.00E+00 

2.00E+00 

2.00E+00 

2.WE+00 

1.00E+00 

l.OOE+OO 

l.OOE+OO 

1 .00E+00 

l.OOE+OO 

1.00E+00 

1 .00E+00 

2.00E+01 

l.OOE+W 

5.00E+00 

5.00E+00 

1.00E+W 

1.00E+00 

2.70E+01 

l.lOE+Ol 

6.00E+01 

1 .5OE+O1 

1.50E+01 


O.WE+W 

0.00E+W 

O.OOE+OO 

O.OOE+OO 

O.WE+OO 

O.WE+OO 

O.WE+W 

O.WE+W 

0.00E+00 

O.WE+OO 

O.WE+OO 

I.WE+OI 

I.WE+Ol 

1.00E+01 

1 .00E+OI 

5.00E+00 

5.00E+00 

9.50E+01 

5.60E+01 

5.40E+Ol 

3.1OE+O1 

5.3OE+01 

5.30E+01 

1.20E+01 

3.70E+01 

3.90€+01 

O.OOE+W 

U 

U 

< 

UNW 

UN 

C 

< 

< 

< 

< 

< 

< 

U 

U 

U 

N 

NW 

N 

N 

N 

N 

N 

N 

N 

N 

HT 

HT 

T 

T 

N 

N 

N 

N 

N 

N 

N 

N 

NT 

NT 

NT 

N 

N 

N 

N 

T 

HT 

HT 

N 

N 

N 

HT 

T 

T 

N 

N 

N 

N 

N 

N 

HT 

HT 

HT 

N 

N 

N 

J 

J 

N 

N 

F 

F 

uglL 

uglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

WlL 

mglL 

Wk 

mgfl 

uglL 

uglL 

uglL 

ugfl 

uglL 

uglL 

uglL 

ugk 

mg/L 

mglL 

NTU 

NTU 

NTU 

NTU 

NTU 

NTU 

WlL 

mgk 

mglL 

mglL 

mglL 

mgk 

rnglL 

mglL 

mglL 

mglL 

mglL 

uglL 

uglL 

uglL 

uglL 

ug1L 

ugk 

mglL 

mgk 

mgk 

mglL 

mgk 

mglL 

mglL 

mglL 

mglL 

mg1L 

Page 169 of 176




Zirconium. Dissolved 7440-67-7 4102-92 OlFEB1992 WG O.OOE+OO < N mglL 

alpha-BHC 


beta-BHC 


bis(2-Chloroethybether 

bis(2-Chloroisopropybether 

bis(2-Ethy1hexyf)phthalate 

cis-1 ,3-Dichloropropene 

cis-1 .3-Dichloropropene 

delta-BHC 

garnma-BHC(Lindane) 


PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

PH 

trans-l,3-Dichloropropene 


WAG 7, SVWU 8, W O O 

1 ,I,l-Trichloroethane 










Alkalinity 

Antimony 


Arsenic 


Barium 


Benzene 

Benzene 

Beryllium 




Cadmium 


Calcium 



Chloride 

Chloroform 

Chloroform 

Chromium 


Cobalt 


Copper 





Ethylbenzene 

319-84-6 

5103-71-9 

319-85-7 

11 1-91-1 

111-44-4 

108-60-1 

117-81-7 

10061-01-5 

10061-01 -5 

319-86-8 

58-89-9 

5103-74-2 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

SO296 

so296 

SO296 

10061-02-6 

10061-02-6 

71-55-6 

71-55-6 

79-00-5 

79-00-5 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

107-06-2 

107-06-2 

47 1-34-1 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

71-43-2 

71-43-2 

7440-41 -7 

744041-7 

75-27-4 

75-27-4 

7440-43-9 

7440-43-9 

7440-70-2 

56-23-5 

56-23-5 

16887-00-6 

6766-3 

67-66-3 

744047-3 

744047-3 

7440-48-4 

744048-4 

7440-50-8 

7440-50-8 

DTW 

OXYGEN DIS 

SO266 

10041-4 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

CH200631-00000 

CH200029-00000 

CH200029-00000 

CH200029-00000 

1438-88 

1439-88 

1440-88 

1441-88 

2293-89 

2981-90 

3018-91 

3041-91 

3042-91 

3043-91 

4102-92 

5414-92 

5415-92 

5416-92 

5417-92 

CH200029-00000 

CH200631-00000 

5549-95 

7070-95 

5549-95 

7070-95 

5549-95 

7070-95 

5549-95 

7070-95 

5549-95 

7070-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

7070-95 

5549-95 

5549-95 

5549-95 

7070-95 

5549-95 

5549-95 

5549-95 

5549-95 

7070-95 

5549-95 

5549-95 

7070-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

190CT1989 

190CTl989 

19OCTl989 

19OCTl989 

19OCTl989 

lSOCTl989 

190CT1989 

19OCTl989 

22AUG1990 

190CT1989 

190CT1989 

190CT1989 

lOAUG1988 

1 OAUG 1988 

10AUG1988 

1 OAUG 1988 

23AUG1989 

OSSEP1990 

OSSEP1991 

05SEPl991 

OBSEPl991 

OSSEP1991 

OlFEB1992 

1 1 AUGl992 

1 1 AUGl992 

1 1 AUGl992 

1 1 AUGl992 

190CT1989 

22AUG1990 

21MAR1995 

12JUL1995 

21 MARl 995 

12JULl995 

21 MARl 995 

12JULl995 

21 MARl 995 

12JULl995 

21MAR1995 

12JUL1995 

21MAR1995 

21 MARl 995 

21MAR1995 

21MAR1995 

21MAR1995 

21MAR1995 

21MAR1995 

21MAR1995 

12JUL1995 

21MAR1995 

21MAR1995 

21MAR1995 

12JULl995 

21MAR1995 

21MAR1995 

21MAR1995 

21MAR1995 

12JULl995 

21 MARl 995 

21MAR1995 

12JULl995 

21MAR1995 

21MAR1995 

21MAR1995 

2 1MAR1995 

21MAR1995 

2lMAR1995 

21MAR1995 

21MAR1995 

21MAR1995 

21MAR1995 

Page 170 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

U 

ux 

ux 

U 

U 

< 

< 

Q 

c 

Q 

< 

U 

U 

U 

U 

c 

< 

U 

U 

U 

U 

< 

Q 

J 

< 

< 

U 

R 

UJ 

UJ 

R 

R 

H 

H 

H 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

su 

uglL 

ug5 

uglL 

uglL 

uglL 

45 

uglL 

ugfl 

uglL 

ugfl 

uglL 

45 

wlL 

mg5 

mglL 

w5 

mglL 

mglL 

W/L 

ugIL 

uglL 

w/L 

wfl 

uglL 

uglL 

WlL 

w5 

mglL 

uglL 

uglL 

mglL 

uglL 

ug1L 

mg5 

mglL 

WlL 

mgR 

mgk 

wfl 

Feet 

mglL 

w5 

ugfl




Ethylbenzene 100-41-4 7070-95 12JUL1995 WG 5.00E+01 U N uglL 

Fluoride 

Gross Alpha 

Gross Beta 

Iron 

Lead 


Magnesium 


Manganese 


Mercury 


Nickel 



Potassium 

Radon 222 

Selenium 


Silica 

Silver 


Sodium 






Sulfate 

Technetium99 

Temperature 



Toluene 

Toluene 









Turbidity 

Uranium 




Xylene 

Xylene 

Zinc 




PH 

PH 

PH 

PH 

WAG 7, SWU 0, MWOl 









1,2-DichloroeIhane 


Alkalinity 

Antimony 

16904-40-0 

12507-46-1 

12507-47-2 

7439-09-6 

7439-92-1 

7439-92-1 

7439 - 95 -4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7440-02-0 

7440-02-0 


7440-09-7 

RN222 

7702-49-2 

7702-49-2 

7631-06-9 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

SO145 

SO145 

SO145 

SO145 

12143-45-2 

14133-76-7 

SO035 

127-18-4 

127-10-4 

100-08-3 

100-00-3 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

156-60-5 

156-60-5 

79-01-6 

79-01-6 

SO270 

7440-61-1 

DIS U 

75-01-4 

75-01-4 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

156-59-2 

156-59-2 

SO296 

SO296 

SO296 

SO296 

71 -55-6 

71-55-6 

79-00-5 

79-00-5 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

107-06-2 

107-06-2 

471-34-1 

7440-36-0 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5 5 4 9 - 9 5 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5549-95 

5550-95 

5551-95 

5552-95 

5549-95 

5549-95 

5549-95 

5549-95 

7070-95 

5549-95 

7070-95 

5549-95 

5550-95 

5551 -95 

5552-95 

5549-95 

7070-95 

5549-95 

7070-95 

5549-95 

5549-95 

5549-95 

5549-95 

7070-95 

5549-95 

7070-95 

5549-95 

5549-95 

5549-95 

7070-95 

5549-95 

5550-95 

5551-95 

5552-95 

5553-95 

7074-95 

5553-95 

7074-95 

5553-95 

7074-95 

5553-95 

7074-95 

5553-95 

7074-95 

5553-95 

5553-95 

21MAR1995 

21MAR1995 

21 MARl 995 

21 MAR 1995 

21 MAR 1995 

21 MAR 1995 

21 MARl 995 

21MAR1995 

21MAR1995 

21MAR1995 

2lMARl995 

21 MAR 1995 

21 MARl 995 

2 lMARl995 

21MARl995 

21MAR1995 

21 MARl 995 

2lMARl995 

2 lMARl995 

21MAR1995 

21 MAR1 995 

21 MARl 995 

21MAR1995 

2lMARl995 

21MAR1995 

21 MAR1 995 

21 MAR1995 

21 MAR1995 

2lMAR1995 

2lMAR1995 

21MAR1995 

21 MARl 995 

12JUL1995 

21 MARl 995 

12JULl995 

2lMARl995 

2 1 MARl 995 

21 MARl 995 

21MAR1995 

21 MAR1995 

12JUL1995 

2lMARl995 

12JUL1995 

2lMARl995 

2 lMARl995 

2lMARl995 

21MAR1995 

12JUL1995 

21 MARl 995 

12JUL1995 

21 MARl 995 

21 MARl 995 

21 MARl 995 

12JUL1995 

21MAR1995 

2 1MAR1995 

2 lMARl995 

2lMARl995 

21MAR1995 

12JUL1995 

21MAR1995 

12JULl995 

21MAR1995 

12JULl995 

21MAR1995 

12JUL1995 

2lMARl995 

12 JULl995 

21MAR1995 

21MAR1995 

Page 171 of 176 

< N 

N 

N 

< 

< 

c 

Q 

c 




mglL 

Antimony, Dissolved 7440-36-0 5553-95 21MAR1995 WG O.OOE+OO 

- 

U 

Arsenic 

7440-38-2 

5553-95 2 lMARl995 WG 

C 

N 

mg/L 


7440-38-2 

5553-95 21 MARl 995 WG 

Q 

N 

mglL 

Barium 

7440-39-3 

5553 - 95 

21 MARl 995 WG 

c 

N 

mg1L 


7440-39-3 

5553-95 21MAR1995 WG 

C 

N 

mglL 

Benzene 

71-43-2 

5553-95 21 MAR 1995 

WG 

UJX 

N 

uglL 

Benzene 

71 -43-2 

7074-95 12JUL1995 WG 

U 

N 

uglL 

Beryllium 

7440-41-7 

5553 - 95 

21 MARl 995 WG 

c 

N 

mglL 


7440-41 -7 

5553-95 21 MARl 995 WG 

c 

N 

mglL 


5553-95 2lMARl995 WG 

UJX 

N 

uglL 


7074-95 12JUL1995 WG 

U 

N 

uglL 

Cadmium 

7440-43-9 

5553-95 2lMAR 1995 WG 

C 

N 

mglL 


Calcium 


7440-43-9 

7440-70-2 

7440-70-2 

5553-95 

5553-95 

5553-95 

21 MAR1 995 

21 MARl 995 

21 MARl 995 

WG 

WG 

WG 

c 

N 

N 

N 

mglL 

mg1L 

mglL 


5553-95 21MAR1995 

WG 

UJX N 

ug/L 


Chloride 

56-23-5 

16887-00-6 

7074-95 

5553-95 

12JULl995 

21MAR1995 

WG 

WG 

U 

N 

N 

uglL 

mglL 

Chloroform 

67-66-3 

5553-95 21 MARl 995 WG 

UJX 

N 

uglL 

C hloroform 

67-66-3 

7074-95 12JUL1995 WG 

U 

N 

uglL 

Chromium 

7440-47-3 

5553-95 21 MAR1 995 WG 

c 

N 

mglL 

Chromium, Dissolved 7440-47-3 

5553-95 21MAR1995 WG 

c 

N 

mglL 

Coban 

7440-48-4 

5553-95 21MAR1995 WG 

C 

N 

mglL 

Cobatl, Dissolved 

7440-48-4 

5553-95 21MAR1995 WG 

C 

N 

mglL 

Copper 

7440-50-8 

5553-95 2lMARl995 WG 

c 

N 

mglL 


7440-50-8 

5553-95 2lMARl995 WG 

c 

N 

mglL 




Ethylbenzene 

DTW 

OXYGEN DIS 

SO266 

10041-4 

5553-95 

5553-95 

5553-95 

5553-95 

21 MAR1 995 

21 MARl 995 

21 MAR1 995 

21 MAR1 995 

WG 

WG 

WG 

WG 

UJX 

N 

N 

N 

N 

Feet 

mglL 

mglL 

uglL 

Ethylbenzene 

100-41-4 

7074-95 12JULl995 WG 

U 

N 

uglL 

Fluoride 

16984-4a-a 

5553-95 21 MARl 995 w 

N 

mglL 

Gross Alpha 

Gross Beta 

Iron 

12587-46-1 

12587-47-2 

7439-89-6 

5553-95 

5553-95 

5553-95 

2IMARl995 

21MAR1995 

21MAR1995 

WG 

WG 

WG 

N 

N 

N 

pCilL 

pciA 

mglL 


Lead 


Magnesium 


Manganese 


Mercury 

7439-89-6 

7439-92-1 

7439-92-1 

7439-95-4 

7439-954 

7439-96-5 

7439-96-5 

7439-97-6 

5553-95 

5553-95 

5553-95 

5553-95 

5553-95 

5553-95 

5553-95 

5553-95 

21 MARl 995 

21 MAR1 995 

21 MARl 995 

21MAR1995 

21MAR1995 

21MARI 995 

21 MAR1 995 

21 MAR1 995 

WG 

WG 

WG 

WG 

\IKj 

WG 

WG 

WG 

c 

c 

C 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mg1L 

mglL 

mg/L 

mg1L 

mglL 

mglL 


7439-97-6 

5553-95 21MAR1995 WG 

Q 

N 

mg/L 

Nickel 

7440-02-0 

5553-95 21MAR1995 WG 

C 

N 

mglL 

Nickel. Dissolved 


7440-02-0 

NITRATEASNIT 

5553-95 

5553-95 

21MAR1995 

21MAR1995 

WG 

WG 

c 

c 

N 

N 

mglL 

mglL 

Potassium 

7440-09-7 

5553-95 21 MARl 995 WG 

N 

mgk 

Potassium, Dissolved 7440-09-7 

5553-95 21MAR1995 WG 

N 

mglL 

Radon 222 

RN222 

5553-95 21MAR1995 WG 

N 

pCilL 

Selenium 

7782-49-2 

5553-95 21MAR1995 w 

eN 

N 

mglL 

Selenium. Dissolved 

7782-49-2 

5553-95 21MAR1995 WG 

Q 

mglL 

Silica 

Silver 


7631-86-9 

7440-22-4 

7440-22-4 

5553-95 

5553-95 

5553-95 

21MAR1995 

21MAR1995 

21MARI 995 

WG 

WG 

WG 

c 

c 

N 

N 

N 

mglL 

mglL 

mg/L 

Sodium 

7440-23-5 

5553-95 21MAR1995 WG 

0 

N 

mglL 


7440-23-5 

5553-95 21MAR1995 w 

0 

N 

mglL 





Sulfate 

SO145 

SO145 

SO145 

SO145 

12143-45-2 

5553-95 

5554-95 

555595 

5556-95 

5553-95 

21MAR1995 

21MAR1995 

21 MAR1995 

21MAR1995 

21MAR1995 

WG 

WG 

WG 

WG 

WG 

N 

N 

N 

N 

N 

umhodcm 

umhodcm 

umhoslcm 

umhodcm 

mglL 

Technetium99 

14133-76-7 

5553-95 21MAR1995 WG 

N 

pCiL 

Temperature 

SO835 

5553-95 21MAR1995 WG 

N 

F 


127-18-4 

5553-95 21MAR1995 WG 

UJX N 

uglL 


127-18-4 

7074-95 I 2JULl 995 WG 

U 

N 

uglL 

Toluene 

108-86-3 

5553-95 21MAR1995 w 

U JX 

N 

uglL 

Toluene 

108-88-3 

7074-95 12JULl995 WG 

U 

N 

uglL 

Total Organic Carbon 7440-44-0 

5553-95 21MAR1995 w 

N mgR 




7440-44-0 

7440-44-0 

7440-44-0 

5554-95 

555595 

5556-95 

21MAR1995 

21MAR1995 

21MAR1995 

WG 

WG 

WG 

N 

N 

N 

mglL 

mglL 

mgfl 

Page 172 of 176




Trans-I .2-Dichloroethene 156-60-5 5553-95 21MAR1995 WG 5.00€+00 UJX N ug1L 




Turbidity 

Uranium 




Xylene 

Xylene 

Zinc 




PH 

PH 

PH 

PH 

WAG 7, SVUvlU 8. MW302 

1 .I,I-Trichloroethane 

I ,I,I-Trichloroethane 

1 .I,2-Trichbroethane 








Alkalinity 

Antimony 

Antimony, Dissotved 

Arsenic 


Barium 


Benzene 

Benzene 

Beryllium 




Cadmium 


Calcium 




Chloride 

Chloroform 

Chloroform 

Chromium 


Coban 


Copper 





Ethylbenzene 

Ethylbenzene 

Fluoride 

Gross Alpha 

Gross Beta 

Iron 


Lead 


Magnesium 


156-60-5 

79-01 -6 

79-01 -6 

SO278 

7440-61-1 

DIS U 

75-01-4 

75-01-4 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

156-59-2 

156-59-2 

SO296 

SO296 

SO296 

SO296 

71-55-6 

71 -55-6 

79-00-5 

79-00-5 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

107-06-2 

107-06-2 

471-34-1 

7440-36-0 

7440-36-0 

7440-38-2 

7440-38-2 

7440-39-3 

7440-39-3 

71-43-2 

71-43-2 

7440-41-7 

7440-41-7 

75-27-4 

75-27-4 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

56-23-5 

56-23-5 

16887-00-6 

67-66-3 

67-66-3 

7440-47-3 

7440-47-3 

7440-48-4 

7440-48-4 

7440-50-8 

7440-50-8 

DTW 

OXYGEN DIS 

SO266 

100-41-4 

100-41-4 

16984-48-8 

12587-46-1 

12587-47-2 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-95-4 

7439-95-4 

7074-95 

5553-95 

7074-95 

5553-95 

5553-95 

5553-95 

5553-95 

7074-95 

5 5 5 3 - 9 5 

7074-95 

5553-95 

5553-95 

5553-95 

7074-95 

5553-95 

5554-95 

5555-95 

5556-95 

5557-95 

7078-95 

5557-95 

7078-95 

5557-95 

7078-95 

5557-95 

7078-95 

5557-95 

7078-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

7078-95 

5557-95 

5557-95 

5557-95 

7078-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

7078-95 

5557-95 

5557-95 

7078-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

7078-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

12JUL1995 

2 lMARl995 

12JUL1995 

21 MAR1 995 

21 MAR 1995 

21 MAR1 995 

21MAR1995 

12JULl995 

21MAR1995 

12JUL1995 

21 MARl 995 

21 MAR1 995 

2lMARl995 

12JUL1995 

21 MARl 995 

2lMAR 1995 

21 MARl 995 

21MAR1995 

2 IMARI 995 

12JULl995 

21MAR1995 

12JUL1995 

21 MAR1995 

12JULl995 

21 MAR1995 

12JUL1995 

21 MAR1 995 

12JULl995 

21 MAR1 995 

21 MARl 995 

2IMAR1995 

21MARl995 

21MAR1995 

21MARI 995 

2lMARl995 

21 MAR1 995 

12JUL1995 

21MAR1995 

21 MAR1995 

21 MAR1 995 

12JULl995 

21 MAR1 995 

2IMAR1995 

2lMARl995 

21 MARl 995 

2lMARl995 

12JUL1995 

21MAR1995 

2lMARl995 

12JULl995 

21MAR1995 

21MAR1995 

21 MARl 995 

2lMARl995 

2lMARl995 

21 MARl 995 

21 MAR1 995 

21MAR1995 

2lMARl995 

21 MARl 995 

12JULl995 

21 MAR1 995 

21MAR1995 

21MAR1995 

21MAR1995 

21MAR1995 

21MAR1995 

21 MARl 995 

21MAR1995 

21MAR1995 

Page 173 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

w 

WG 

w 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

w 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

w 

WG 

WG 

WG 

WG 

WG 

WG 

5.00E+00 

1.00€+00 

1.00E+00 

2.80€+01 

0.00E+00 

0.00E+00 

1.00E+01 

l.OOE+Ol 

1.00E+01 

1 .OOE+Ol 

O.OOE+OO 

0.00E+00 

2.50E+01 

2.50€+01 

6.00€+00 

6.00E+00 

6.00E+00 

6.00E+00 

U 

U JX 

ux 

UJX 

ux 

UJX 

U 

< 

< 

JX 

UJX 

U 

U JX 

U 

UJX 

U 

U JX 

U 

UJX 

U 

< 

Q 

< 

Q 

UJX 

U 

< 

< 

UJX 

U 

< 

c 

U JX 

U 

UJX 

U 

c 

< 

< 

< 

< 

< 

UJX 

U 

< 

< 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

uglL 

uglL 

ug1L 

N N 

mglL 

mglL 

uglL 

uglL 

uglL 

uglL 

mglL 

mglL 

uglL 

uglL 

su 

su 

su 

su 

uglL 

uglL 

ug/L 

uglL 

uglL 

ug/L 

uglL 

uglL 

ug1L 

uglL 

mglL 

mg/L 

rnglL 

mglL 

mglL 

mglL 

rn@ 

uglL 

uglL 

mglL 

rnglL 

uglL 

ug/L 

mglL 

mglL 

mglL 

rngk 

uglL 

UglL 

mgfl 

uglL 

uglL 

mglL 

mglL 

mglL 

mglL 

mglL 

mglL 

Feet 

mglL 

mglL 

uglL 

uglL 

mglL 

pci/L 

pCiL 

mgk 

mgk 

W L 

mglL 

mgfl 

mgfl




Manganese 


Mercury 


Nickel 



Potassium 


7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7440-02-0 

7440-02-0 

NITRATEASNIT 

7440-09-7 

7440-09-7 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

5557-95 

21MAR1995 

2lMARl995 

21 MARl 995 

21 MARl 995 

21MARl995 

21MAR1995 

2 lMARl995 

21 MARl 995 

21 MARl 995 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

O.OOE+OO 

l.OOE+OO 

l.lOE+Ol 

O.OOE+OO 

c 

Q 

< 

c 

c 

c 

Q 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

mglL 

mg1L 

mglL 

mglL 

mglL 

mglL 

mglL 

Radon 222 

Selenium 


Silica 

RN222 

7782-49-2 

7782-49-2 

7631-86-9 

5557-95 

5557-95 

5557-95 

5557-95 

21MAR1995 

21MAR1995 

21 MARl 995 

21 MARl 995 

WG 

WG 

WG 

WG 

1.05E+02 1.20E+01 

O.OOE+OO 

O.OOE+OO 


CN 

Q 

N 

N 

N 

pCVL 

mg1L 

mglL 

mglL 

Silver 

7440-22-4 

5557-95 21MAR1995 WG O.OOE+OO 

c 

N 

WlL 


7440-22-4 

5557-95 21MAR1995 

WG O.OOE+OO 

< N 

mglL 

Sodium 






Sulfate 

Technetium-99 

Temperature 



Toluene 

Toluene 









Turbidity 

Uranium 




Xylene 

Xylene 

Zinc 



7440-23-5 

7440-23-5 

SO145 

SO145 

SO145 

SO145 

12143-45-2 

14133-76-7 

SO835 

127-10-4 

127-18-4 

108-80-3 

108-88-3 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

156-60-5 

156-60-5 

79-01-6 

79-01-6 

SO278 

7440-61-1 

DIS U 

75-014 

75-01-4 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

156-59-2 

5557-95 

5557-95 

5557-95 

5558-95 

5559-95 

5560 - 95 

5557-95 

5557-95 

5557-95 

5557-95 

7078-95 

5557-95 

7078-95 

5557-95 

5558-95 

5559-95 

5560-95 

5557-95 

7078-95 

5557-95 

7078-95 

5557-95 

5557-95 

5557-95 

5557-95 

7078-95 

5557-95 

7078-95 

5557-95 

5557-95 

5557-95 

21 MARl 995 

21 MAR1 995 

21 MARl 995 

21 MARl 995 

21 MAR1 995 

21MAR1995 

21 MAR1995 

21 MAR1995 

21 MARl 995 

21MAR1995 

12 JULl995 

2lMARl995 

12JUL1995 

21 MAR1 995 

21MAR1995 

21 MARl 995 

21MAR1995 

21MAR1995 

12JUL1995 

21MAR1995 

12JULl995 

21MAR1995 

21MAR1995 

21MAR1995 

21 MARl 995 

12JULl995 

21 MAR1 995 

12JUL1995 

21MAR1995 

21MAR1995 

21MAR1995 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

ViG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

7.50E+01 

8.10E+01 

7.54E+02 

7.61E+02 

7.60€+02 

7.58E+02 

1.31E+02 

8.00E+W 2.40E+01 

5.50E+Ol 

5.00E+00 

5.00E+00 

5.00E+00 

5.00E+00 

2.00E+00 

2.00E+W 

2.00E+00 

2.WE+00 

S.WE+W 

S.WE+OO 

1 .WE+00 

l.WE+W 

2.20E+OI 

O.WE+W 

O.WE+OO 

l.OOE+OI 

l.OOE+OI 

l.OOE+OI 

1.00E+01 

O.OOE+W 

O.OOE+OO 

S.WE+W 

B 

B 

UJX 

U 

UJX 

U 

UJX 

U 

UJX 

U 

UJX 

U 

UJX 

U 

< 

< 

UJX 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

mglL 

mglL 

umhoslcm 

umhoslcm 

umhoslcm 

umhosfcm 

mglL 

pCVL 

F 

uglL 

uglL 

uglL 

ugk 

mgk 

mil5 

mgk 

mglL 

uglL 

uglL 

uglL 

uglL 

NTU 

W/L 

mglL 

uglL 

uglL 

uglL 

ug1L 

mgk 

WlL 

uglL 

cis-I ,2-dichloroethene 156-59-2 

7078-95 12JUL1995 WG S.WE+W 

U 

N 

uglL 

PH 

SO296 

5557-95 2lMARl995 WG 6.00E+W 

N su 

PH 

SO296 

5558-95 21MAR1995 WG 6.WE+00 

N su 

PH 

SO296 

5559-95 2lMAR1995 WG 6.00E+00 

N su 

PH 

SO296 

5560-95 21MAR1995 WG 6.00E+00 

N su 

WAG 7. SWU 8. MW303 

1 .I,I-Trichloroethane 


1, I .2-Trichloroethane 

1,1,2-TrichIoroethane 



1 .I-Diihloroethene 




Alkalinity 

Antimony 


Arsenic 

Anenic, Dissolved 

Barium 


Benzene 

Benzene 

Beryllium 

71 -55-6 

7 1-55-6 

79-00-5 

79-00-5 

75-34-3 

75-34-3 

75-35-4 

75-35-4 

107-06-2 

107-06-2 

471-34-1 

7440-36-0 

7440-36-0 

7440-30-2 

7440-38-2 

7440-39-3 

7440-39-3 

71-43-2 

71-43-2 

7440-41 -7 

5561 -95 

7082-95 

5561-95 

7082-95 

5561 -95 

7082-95 

5561-95 

7082-95 

5561-95 

7082-95 

5561-95 

5561 -95 

5561-95 

5561 -95 

5561 -95 

5561 -95 

5561-95 

5561-95 

7082-95 

5561 -95 

21 MAR1 995 

12JULl995 

2lMAR 1995 

1 PJULl995 

2lMARl995 

12JULl995 

21MAR1995 

lZJULl995 

2 lMARl995 

lZJULl995 

21MAR1995 

21MAR1995 

21MAR1995 

21MAR1995 

2 1 MAR 1995 

2lMARl995 

21MAR1995 

21 MARl 995 

12JULl995 

21MAR1995 

Page 174 of 176 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

\IK; 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

WG 

S.WE+OO 

5.00E+00 

5.00E+W 

5.00E+W 

S.WE+OO 

5.00E+00 

S.WE+W 

5.WE+W 

5.00E+W 

S.WE+OO 

5.07E+02 

O.WEt00 

O.WE+W 

O.OOE+W 

O.WE+W 

O.OOE+OO 

O.WE+OO 

5.00E+W 

5.WE+00 

O.WE+OO 

UJX 

U 

UJX 

U 

UJX 

U 

U JX 

U 

UJX 

U 

< 

Q 

< 

Q 

< 

c 

UJX 

U 

< 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

N 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

uglL 

ugk 

uglL 

ugk 

mgk 

Wk 

mgk 

mgk 

mgk 

mglL 

mglL 

ugfL 

uglL 

mglL



ANALYTE CAS NUMBER SAMPLE ID DATE MPE RESULT ERROR QUALIFIER QUALIFIER UNITS 

Beryllium. Dissolved 7440-41 -7 5561-95 21MAR1995 WG O.OOE+OO < N mg1L 



Cadmium 


Calcium 




Chloride 

Chloroform 

Chloroform 

Chromium 


Cobalt 


Copper 





Ethylbenzene 

Ethylbenzene 

Fluoride 

Gross Alpha 

Gross Beta 

Iron 


Lead 


Magnesium 


Manganese 


Mercury 


Nickel 



Potassium 


Radon 222 

Selenium 


Silica 

Silver 


Sodium 






Sulfate 

Technetium99 

Temperature 



Toluene 

Toluene 






Trans-I .2-Dchloroethene 



Turbidity 

Uranium 



75-27-4 

75-27-4 

7440-43-9 

7440-43-9 

7440-70-2 

7440-70-2 

56-23-5 

56-23-5 

16887-00-6 

67-66-3 

67-66-3 

7440-47-3 

7440-47-3 

7440-48-4 

7440-48-4 

7 4 4 o - 5 o - a 

7440-50-8 

DTW 

OXYGEN DIS 

SO266 

100-41-4 

100-41 -4 

i69a4-48-a 

12587-46-1 

ma7-47-2 

7439-89-6 

7439-89-6 

7439-92-1 

7439-92-1 

7439-95-4 

7439-95-4 

7439-96-5 

7439-96-5 

7439-97-6 

7439-97-6 

7440-02-0 

7440-02-0 


7440-09-7 

7440-09-7 

RN222 

7782-49-2 

7782-49-2 

7631-86-9 

7440-22-4 

7440-22-4 

7440-23-5 

7440-23-5 

SO145 

SO145 

SO145 

SO145 

12143-45-2 

14133-76-7 

so835 

127-18-4 

in-18-4 

108-88-3 

ioa-88-3 

7440-44-0 

7440-44-0 

7440-44-0 

7440-44-0 

156-60-5 

156-60-5 

79-01-6 

79-01-6 

so278 

7440-61-1 

DIS U 

75-01-4 

5561 -95 

7082-95 

5561 -95 

5561-95 

5561-95 

5561-95 

5561 -95 

7082-95 

5561 -95 

5561-95 

7082-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561 -95 

5561 -95 

5561 -95 

5561-95 

7082-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561-95 

5561 -95 

5561 -95 

5561 -95 

5561 -95 

5561-95 

5561-95 

5561 -95 

5561 -95 

5561-95 

5561 -95 

5562-95 

5563-95 

5564-95 

5561 -95 

5561 -95 

5561 -95 

5561-95 

7082-95 

5561 -95 

7082-95 

5561-95 

5562-95 

5563-95 

5564-95 

5561-95 

7082-95 

5561-95 

7082-95 

5561-95 

5561-95 

5561-95 

5561-95 

21 MARl 995 

I 2JUL 1995 

21MAR1995 

21MAR1995 

21 MARl 995 

21MAR1995 

21 MAR1 995 

12JUL1995 

2 lMARl995 

21MAR1995 

12JUL1995 

21MAR1995 

21 MAR1995 

21 MARl 995 

21 MAR 1995 

21 MARl 995 

21 MARl 995 

2lMAR 1995 

21MAR1995 

21MAR1995 

2 IMARI 995 

12JULl995 

2 lMARl995 

2 IMARI 995 

2 IMARI 995 

2 IMARI 995 

2 lMAR1995 

2 lMARl995 

21MARl995 

2IMAR1995 

2lMARl995 

2lMARl995 

21MARI 995 

2 I MAR 1995 

21 MARl 995 

21MAR1995 

2lMAR1995 

21 MAR1 995 

21MAR1995 

21 MAR1995 

21 MAR1 995 

21 MARl 995 

21MAR1995 

21 MAR1 995 

21MARl995 

2 IMARI 995 

21MARI 995 

2 IMARI 995 

21 MAR1995 

21MAR1995 

21 MARl 995 

21 MAR1 995 

2 IMARI 995 

21 MAR 1995 

21 MAR1 995 

2lMARl995 

12JUL1995 

21 MARl 995 

12JUL1995 

21 MARl 995 

21MARl995 

21 MAR1 995 

21 MARl 995 

21MAR1995 

12 JULl995 

21 MAR1 995 

12JULl995 

2 IMARI 995 

2lMAR 1995 

21 MAR1 995 

21 MARl 995 

Page 175 of 176 

UJX 

N 

U 

N 

c 

N 

< N 

N 

N 

U JX 

N 

U 

N 

N 

UJX 

N 

U 

N 

C 

N 

< N 

< N 

Q 

C 

N 

< N 

N 

N 

N 

U JX 

N 

U 

N 

N 

N 

N 

N 

N 

< 

N 

< 

N 

N 

N 

N 

N 

< 

N 

Q 

N 

c 

N 

< 

N 

< 

N 

N 

N 

N 


ANALYTE 


Xylene 

Xylene 

Zinc 


cis-I .Z-dichloroethene 


PH 

PH 

PH 

PH 

CAS NUMBER 

75-01-4 

1330-20-7 

1330-20-7 

7440-66-6 

7440-66-6 

156-59-2 

156-59-2 

SO296 

SO296 

SO296 

SO296 

SAMPLE ID 

7082-95 

5561-95 

7082-95 

5561-95 

5561 -95 

5561 -95 

7082-95 

5561 -95 

5562-95 

5563-95 

5564-95 

DATE 

12JUL1995 

21MAR1995 

1 2JULl995 

21MAR1 995 

21 MAR1 995 

21 MARl 995 

12JUL1995 

21 MARl 995 

2 1 MARl 995 

ZlMAR1995 

2lMARl995 


TYPE RESULT ERROR QUALIFIER QUALIFIER 

WG I.OOE+OI 

U 

N 

WG I.OOE+OI 

UJX N 

WG 1.00E+01 

U 

N 

WG 0.00E+00 

< N 

WG 0.00E+00 

< N 

WG 5.00E+00 

U JX 

N 

WG 5.00E+00 

U 

N 

WG 6.00E+00 

N 

WG 6.00E+00 

N 

WG 6.00E+00 

N 

WG 6.00€+00 

N 

UNITS 

uglL 

uglL 

uglL 

mglL 

mglL 

uglL 

uglL 

su 

su 

su 

su 

Page 176 of 176

Appendix L. 10 

Results of Integrated Exposure Uptake Biokinetic Model for Lead

Internal Correspondence 

MARTIN MARIEITA ENERGY SYSTEMS, INC. 

Date: September 6, 1995 

To: 

From: 

Subject: 

Fred Dolislager 

Kowetha Davidson (1060 COM, Rm. 103, MS6480) 

Integrated Exposure Uptake Biokinetic (IEUBK) Model for Lead 

I have included the printouts for the lead model. The model was run for ages of 0 to 5 years; 1 

used 5 years because that is the age group used for the other runs 1 did for you. The lead 

concentrations in soil and vegetables were all run. When the concentration in vegetables was 

below 0.001 kg lead/g, the vegetable concentrations were not input into the model, because the 

program rounds off to three decimals. The program was run assuming that consumption of 

homegrown vegetables was 25% of all vegetable consumption (the average value according to 

EPA). I also ran a duplicate set of values setting the soil concentration to 200 ,ug lead/g just in case 

your model did not account for background levels of lead in soil. This value is the default 

established by the U.S. Environmental Protection Agency. The concentration for house dust was 

calculated using the multiple source analysis in which the values for dust were based on a 70% 

conversion of soil to dust and a air-todust conversion of 100 pg Pb in dustlpg Pb/m3 of air. Default 

values were used for air (0.1 pg Pb/m3) and drinking water (4 pg/L). 

The current directive from EPAs Office of Solid Waste and Emergency Response (OSWER) 

(directive # 9344.4-12) for soil lead recommends a screening level of 400 ppm (mg/kg or 1919) for 

residential land use. A screening level is not a cleanup level, but is defined as the level of 

contamination above which there may be sufficient concern to warrant site-specific study of risk. 

The directive also states that OSWER would attempt to limit exposure of children to soil lead such 

that the estimated risk of blood lead exceeding 10 pg/dL would be 5% or less and that OSWER 

would apply EPA's IEUBK model on a site-specific basis. I have not included printouts of the lead 

model output for soil lead concentrations at the screening level of 400 ppm. I will give these to you 

if you want them. 

When the values for both soil and vegetables from Wag 1 , 7, and KOW were input into the model, 

the results showed that, in each case, the probability that blood lead levels in children 0-5 years

old would exceed 10 pg/dL is estimated to be 0.97% or less when consumption of homegrown 

vegetables approximated 25% of the vegetable intake. If the soil lead concentrations is set to the 

default level (200 pg/g) and homegrown vegetables are consumed, the probability of blood lead 

levels in children 0-5 years old exceeding 10 pg/dL is estimated to be 2.70% or less. These results 

indicate that the concentration of lead in the soil and vegetables would not present a health concern 

for children.

Table J.l. Concentrations and Chronic Daily Intakes of Lead 

-. 

ANALYTE UNITS COW (VEGETABLES] 

Residential ,WAG1 , S W 38,soil 

Lead 

mg/kg 1.38EM1 1.lOE-02 9. Dl I 9 

Kesidentlal , w ~ti i , SwhlvtOO, soil - 13.8 - - - ..- 

Lead mg/kg 1.30EM1 4.58E-03 0. bo5 d 

W J I?iLD 

Keslm , , SWMUfX,-soiT- 

V' 

Residential , WAG 7 , SWMU 8, soil 

- 

,/ 

Lead m& 9.96EM0 7.97E-03 3. ocf 

Residential , WAG T , SWMU 130, soil 

."& J 

kKl __ m& 1.13EM1 6.01E-05 .. jrn 

1 /, 

Residential , WAG 7 , SWMU 131, soil 

3 

- Lead mgkg 8.49EM0 1.2OE-04-2k- - 

Lead mg/kg 1.99EM1 1.15E-05 * rr? &-J 

Resident&-- , WAG 7 , SWMU 132, soil if.+ 

Lead mgkg 1.17EM2 9.39E-04 '.M 'A& V' 

ResiGtid , WAG 7 , SWMU 133, soil / 19 

Lead mg/kg 1.62E+02 1.09E-03 0 ' ' 

a 

-7GesidentiaI , WAG 7 , SWMU 134, soil I @ > 2 

Lead m& 2.60EMl 1.75E-04 1- 'I@' 

-.- 

Residential 

a-(r ~ 

, WAG KOW, SWMU 95, soil 

Lead m& 3.59E+01 2.88E-02 '7 

- KisidGtial , WAG KOW, SWMU 157, soil 33-1 a 

Lead 

Residential , WAG KOW, SWMU 944 soil 

mg/kg 1.47EM1 

I Ylq 

1.18E-02 reo' 

Lead 

mg/kg 1.44EM1 1.192-02 3 r O l v 

lq#Y 

Y 

._3 

J 

-2 

Page 1 of 1

AIR CONCENTRATION: 0.100 ug Pb/m3 DEFAULT 

Indoor AIR Pb Conc: 30.0 percent of outdoor. 

Other AIR Parameters: 

Age Time Outdoors (hr) Vent. Rate (m3/day) 

0-1 1.0 2.0 

1-2 2.0 3.0 

2-3 3.0 5.0 

3-4 4.0 5.0 




Lung Abs. (%) 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 

DIET: 

DEFAULT 

DRINKING WATER Conc: 4.00 ug Pb/L 

WATER Consumption: DEFAULT 

DEFAULT 

SOIL & DUST: 

Soil: constant conc. 

Dust: Multiple Source Analysis 

Age 

0-1 

1-2 

2-3 

3-4 

4-5 

5-6 

6-7 

Soil (ug Pb/g) 

200.0 

200.0 

200.0 

200.0 

200.0 

200.0 

200.0 

House Dust (ug Pb/g) 

150.0 

150.0 

150.0 

150.0 

150.0 

150.0 

150.0 

Additional Dust Sources: None DEFAULT 

Soil contribution conversion factor: 0.70 

Air contribution conversion factor: 100.0 

PAINT Intake: 0.00 ug Pb/day 

DEFAULT 

MATERNAL CONTRIBUTION: Infant Model 

Maternal Blood Conc: 2.50 ug Pb/dL 

CALCULATED BLOOD Pb and Pb UPTAKES: 

YEAR 

------ 

0.5-1: 

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

Blood Level 

(ug/dL) 

----------- 

3.8 


3.9 

3.7 

3.1 

2.7 

2.5 

Total Uptake 

( ug/day 1 

____-------- 

7.00 

10.00 

10.49 

10.51 

0.91 

8.71 

a.83 

Soil+Dust Uptake 

( ug/day 1 

_______----- 


6.40 

6.46 

6.54 



4.23

1-2: 

2-3: 

3-4: 

4-5: 

'-6: 

a-7: 

2.65 

3.00 

2.92 

2.86 

3.04 

3.37 

0.92 

0.96 

0.99 

1.05 

1.11 

1.13 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

0.03 

0.06 

0.07 

0.07 

0.09 

0.09

I 

t 

Cutoff: 10.0 ug/dL 

Z above: 1.66 

Z Below: 98.34 

C. Mean: 3.7 

LEaD 0.99d 

e 2 4 6 8 10 12 14 16 18 20 

BLOOD LEAD CONCENTRATION 

0 to 60 Months

LEAD MODEL Version 0.99d bl Q6 L, SW NU 'i5 @,so \\ 


idoor AIR Pb Conc: 30.0 percent of outdoor. 

Lher AIR Parameters: 


0-1 1.0 2.0 

1-2 2.0 3.0 

2-3 3.0 5.0 





Lung Abs. (%) 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 

Diet: alternate diet selected by user as follows: 

Home-grown Fruit: 0.000 ug Pb/g 0.0 % 

Home-grown Vegetables: 0.011 ug Pb/g 25.0 % 

Recreational Fish: 0.000 ug Pb/g 0.0 % 

Wild Game: 0.000 ug Pb/g 0.0 % 



DEFAULT 

SOIL & DUST: 



Age 

0-1 

1-2 

2-3 

3-4 

4-5 

5-6 

6-7 


13.8 

13.8 

13: 8 

13.8 

13.8 

13.8 

13.8 


19.7 

19.7 

19.7 

19.7 

19.7 

19.7 

19.7 





DEFAULT 




YEAR 

------ 

0.5-1: 

1-2: 

-3: 

-4 : 

4-5: 

5-6: 

6-7: 

Blood Level 

(ug/dL) 

----------- 

2.0 

2.0 

1.9 

1.8 

1.6 

1.6 

1.5 

Total Uptake 

(ug/day) 

____-------- 

3.69 


5.11 

5.06 


5.10 

5.49 


(ug/day) 

------------ 

0.42 

0.66 

0.66 

0.67 

0.50 

0.45 

0.42

YEAR 

------ 

0.5-1: 

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

Diet Uptake 

( ug/day) 

_---------- 

Water Uptake 

( ug /day) 

---_-------_ 

2.87 0.38 

2.92 0.96 

3.39 1-00 

3.30 1.03 

3.22 1.07 

3.43 1.13 

3.82 1.15 

Paint Uptake 

( ug/day) 

-----------_ 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

Air Uptake 

(ug /day) 

-------- 

0.02 

0.03 

0.06 

0.07 

0.07 

0.09 

0.09

? 

rp 

rp 

L 

Probabi 1 i ty Densi 

Function fcblood 

? 

f

LEAD MODEL Version 0.99d wbk(Ci,SwMY 3 8, 50; \ 





0-1 1.0 2.0 

1-2 2.0 3.0 

2-3 3.0 5.0 










Lung Ats. (%) 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 



SOIL & DUST: 


Dust: constant conc. 

Age 

0-1 

1-2 

2-3 

3-4 

4-5 

5-6 

6-7 


200.0 

200.0 

200.0 

200.0 

200.0 

200.0 

200.0 

Additional Dust Sources: None 


DEFAULT 


200.0 

200.0 

200.0 

200.0 

200.0 

200.0 

200.0 

DEFAULT 

DEFAULT 

MATERNAL, CONTRIBUTION: Infant Model 



YEAR 

0.5-1: 

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

Blood Level 

( ug/ dL 1 

----------- 





3.5 

3.1 

2.8 

Total Uptake 

( ug/day 1 

--__-------- 

7.79 

11.05 

11.66 

11.73 

9.92 

9.71 

9.85 


( ug /day 1 

-----_-_____ 


7.35 

7.43 

7.52 

5.68 

5.15 


Diet Uptake Water Uptake Paint Uptake Air Uptake

YEAR 

------ 

0.5-1: 

1-2: 

-3: 

2-4: 

4-5: 

5-6: 

6-7: 

(ug/day) ( ug/day 1 

----------- ------_-____ 

2.73 0.37 

2.76 0.91 

3.22 0.95 

3.16 0.98 

3.13 1.04 

3.35 1.11 

3.74 1.13 

(ug/day) 

---___-_____ 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

(ug/day) 

- - - - - - - - 

0.02 

0.03 

0.06 

0.07 

0.07 

0.09 

0.09

Cutoff: 10.0 ug/dL Z Above: 2.70 - 


C. Mean: 4.1 

- 

- 

- 

- 

- 

- 

- 

LEAD 0.99d 

BLOOD LEAD CONCENTRATION

- 

LEAD MODEL Version 0.99d 'W &61, /,-O,bd 


'ndoor AIR Pb Conc: 30.0 percent of outdoor. 

ther AIR Parameters: 


0-1 1.0 2.0 

1-2 2.0 3.0 

2-3 3.0 5.0 





Lung Abs. (%) 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 








DEFAULT 

SOIL & DUST: 



Age 

0-1 

1-2 

2-3 

3-4 

4-5 

5-6 

6-7 

Soil (ug Pb/g) House Dust (ug Pb/g) 

13.0 19.1 

13.0 19.1 

13.. 0 19.1 

13.0 19.1 

13.0 19.1 

13.0 19.1 

13.0 19.1 





DEFAULT 




YEAR 

------ 

0.5-1: 

1-2: 

'-3: 

-4 : 

4-5: 

5-6: 

6-7: 

Blood Level 

( ug/ dL ) 

----------- 

2.0 

1.9 

1.8 

1.7 

1.6 

1.5 

1.5 

Total Uptake 

( ug/day 1 

___--------- 

3.63 






5.33 


(ug/day) 

____-------- 

0.40 

0.64 

0.64 

0.64 

0.48 

0.43 

0.41

YEAR 

------ 

0.5-1: 

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

Diet Uptake 

(&day 1 

____------- 

2.83 

2.85 

3.28 

3.19 

3.10 

3.30 

3.67 

Water Uptake 

(ug /day) 

--------_-__ 

0.38 

0.96 

1.00 

1.03 

1.07 

1.13 

1.15 

Paint Uptake 

(ug/day) 

------------ 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

Air Uptake 

( ug / day) 

--_----- 

0.02 

0.03 

0.06 

0.07 

0.07 

0.09 

0.09

1 ~ 1 ) , ) , 1 1 1 1 1 1 1 , I , , 


Z Above: 0.01 


C. Mean: 1.9 

- 

- 

- 

- 

- 

1 # 1 , 1 , 

0 1 2 3 4 5 6 7 8 9 18

LEAD MODEL Version 0.99d 

V A 6 1, SWFCL 100, So ;\ 




Age Time Outdoors (hr) Vent. Rate (m3/day) Lung Abs. (%) 

0-1 1.0 

2.0 32.0 

1-2 2.0 

3.0 32.0 

2-3 3.0 

5.0 32.0 

3-4 4.0 

5.0 32.0 


5.0 32.0 


7.0 32.0 


7.0 32.0 








SOIL & DUST: 



DEFAULT 

Age 

0-1 

1-2 

2-3 

3-4 

4-5 

5-6 

6-7 


200.0 150.0 

200.0 150.0 

200.0 150.0 

200.0 150.0 

200.0 150.0 

200.0 150.0 

200.0 150.0 






DEFAULT 




YEAR 

------ 

3.5-1: 

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

Blood Level 

(ug/dL) 

----------- 

3.9 


3.9 

3.7 

3.2 

2.8 

2.6 

Total Uptake 

( ug/ day 1 

---___---___ 

7.16 

10.06 

10.62 

10.66 

9.07 

8.91 

9.07 


( ug/day) 

------------ 


6.40 

6.46 

6.53 




YEAR 

------ 

'1: 

-2 : 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

Diet Uptake 

(ug/day) 

---_-______ 

2.71 

2.71 

3.14 

3.07 

3.03 

3.24 

3.61 

Water Uptake 

( ug / day ) 

------------ 

0.37 

0.92 

0.96 

0.99 

1.05 

1.11 

1.13 

Paint Uptake 

(ug/day) 

----__--____ 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

Air Uptake 

( ug/day) 

- - - - - - - - 

0.02 

0.03 

0.06 

0.07 

0.07 

0.09 

0.09


Z Rbouc: 1.76 


C. Mean: 3.8 

LERD 8.99d 

- ' , I , 1 

0 2 4 6 8 10 12 14 16 18 20 

BLOOD LERD CONCENTRlIION 

0 to 60 Months

LEAD MODEL Version 0.99d W f4 6 1, S k wu 13 b, Sa; I 

ATR CONCENTRATION: 0.100 ug Pb/m3 DEFAULT 

?door AIR Pb Conc: 30.0 percent of outdoor. 

>ther AIR Parameters: 


0-1 1.0 2.0 

1-2 2.0 3.0 

2-3 3.0 5.0 





DIET: 

DEFAULT 

Lung Abs. (%) 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 



DEFAULT 

SOIL & DUST: 



Age 

0-1 

1-2 

2-3 

3-4 

4-5 

5-6 

6-7 


8.5 15.9 

8.5 15.9 

8.5 15.9 

8.5 15.9 

8.5 15.9 

8.5 15.9 

8.5 15.9 





DEFAULT 




YEAR 

-----_ 

0.5-1: 

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

Blood Level 

(ug/dL) 

---------_- 

1.9 

1.8 

1.7 

1.6 

1.5 

1.4 

1.4 

Total Uptake 

( ug /day) 

-----_------ 

3.38 








( ug/day 1 

-----------_ 

0.31 

0.49 

0.49 

0.50 

0.37 

0.33 

0.31

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

2.79 

3.14 

3.03 

2.93 

3.10 

3.42 

0.96 

1.00 

1.03 

1.07 

1.13 

1.15 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

0.03 

0.06 

0.07 

0.07 

0.09 

0.09

I I ' 1 1 ' 

A 

I , I I I I I 


z Above: 0.00 

z Below: 100.00 

G. Mean: 1.7 

LEnD 0.99d 

J 

J 

e 1 2 3 4 5 6 7 8 


LEAD MODEL Version 0.99d vAAG 3, SwWk 3 ; Ss:/ 





0-1 1.0 2.0 

1-2 2.0 3.0 

2-3 3.0 5.0 





Lung Abs. (%I 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 








SOIL & DUST: 



Age 

0-1 

1-2 

2-3 

3-4 

4-5 

5-6 

6-7 


10.0 

10.0 

10,. 0 

10.0 

10.0 

10.0 

10.0 

DEFAULT 


17.0 

17.0 

17.0 

17.0 

17.0 

17.0 

17.0 





DEFAULT 




YEAR 

------ 

0.5-1: 

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

Blood Level 

(ug/dL) 

----------- 

2.0 

1.9 

1.8 

1.7 

1.6 

1.5 

1.5 

Total Uptake 

( ug /day 1 

_----------- 

3.59 






5.34 


( ug/day ) 

------------ 

0.34 

0.54 

0.54 

0.54 

0.41 

0.37 

0.35

YEAR 

_____- 

-1: 

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

Diet Uptake 

(ug/day) 

----------- 

2.85 

2.89 

3.33 

3.25 

3.16 

3.37 

3.75 

Water Uptake 

(ug/day) 

__-----_--__ 

0.38 

0.96 

1.00 

1.03 

1.07 

1.13 

1.15 

Paint Uptake 

( ug /day ) 

---_-------- 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

Air Uptake 

(ug/day) 

------- - 

0.02 

0.03 

0.06 

0.07 

0.07 

0.09 

0.09

Cutoff: 10.0 us/dL 

X Above: 0.01 

z Below: 99.99 

C. Mean: 1.8 

LEAD 0.99d 

e 2 3 4 5 6 7 8 9 


LEAD MODEL Version 0.99d \MAG?, SWmk 8,Sa;l 


?door AIR Pb Conc: 30.0 percent of outdoor. 

cher AIR Parameters: 


0-1 1.0 2.0 

1-2 2.0 3.0 

2-3 3.0 5.0 










Lung Abs. (%) 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 



DEFAULT 

SOIL & DUST: 



Age 

0-1 

1-2 

, 2-3 

3-4 

4-5 

5-6 

6-7 


200.0 150.0 

200.0 150.0 

200.0 150.0 

200.0 150.0 

200.0 150.0 

200.0 150.0 

200.0 150.0 






DEFAULT 




YEAR 

------ 

0.5-1: 

1-2: 

-3 : 

-4 : 

4-5: 

5-6: 

6-7: 

Blood Level 

(ug/dL 1 

----------- 

3.9 



3.8 

3.2 

2.8 

2.6 

Total Uptake 

( ug/day 1 

------------ 

7.18 

10.09 

10.67 

10.71 

9.12 

8.97 

9.14 


( ug/ day 1 

------------ 


6.39 

6.45 

6.53 




YEAR 

------ 

0.5-1: 

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

Diet Uptake 

( ug/day 1 

--------__- 

2.73 

2.75 

3.19 

3.13 

3.09 

3.30 

3.68 

Water Uptake 

(ug/day) 

___-_-______ 

0.37 

0.92 

0.96 

0.99 

1.05 

1.11 

1.13 

Paint Uptake 

( ug/ day) 

----__----__ 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

Air Uptake 

(ug/day) 

-------- 

0.02 

0.03 

0.06 

0.07 

0.07 

0.09 

0.09

1 ' 1 ' 1 ' 1 1 ~ , , , 1 , 1 , I 


Z Iboue: 1.76 


C. Mean: 3.8 

LEIID 0.99d 

2 4 6 8 10 12 14 16 18 20 

BLOOD LElD CONCENIRATION

LEAD MODEL Version 0.99d 





0-1 1.0 2.0 

1-2 2.0 3.0 

2-3 3.0 5.0 





Lung Abs. (%) 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 

DIET: 

DEFAULT 



SOIL & DUST: 



Age 

0-1 

1-2 

2-3 

3-4 

4-5 

5-6 

6-7 


11.3 

11.3 

11.3 

11.3 

11.3 

11.3 

11.3 

DEFAULT 


17.9 

17.9 

17.9 

17.9 

17.9 

17.9 

17.9 





DEFAULT 




YEAR 

Blood Level Total Uptake 

( ug/dL 1 ( ug /day 1 

----------- ______------ 

1.9 3.43 

1.9 4.36 





1.4 5.04 

------ 

0.5-1: 

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 


( ug/day) 

------------ 

0.37 

0.58 

0.58 

0.59 

0.44 

0.39 

0.37

1-2: 

2-3: 

3-4: 

4-5: 

.6 : 

a-7: 

2.78 

3.13 

3.03 

2.93 

3.10 

3.42 

0.96 

1-00 

1.03 

1.07 

1.13 

1.15 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

0.03 

0.06 

0.07 

0.07 

0.09 

0.09

I I 1 I 1 I I I I I I I I I I I 


Z Aboue: 0.01 


C. Mean: 1.8 

- 

- 

- 

- 

- 

LEAD 0.99d 

I I I I I 

1 2 3 4 5 6 7 8 9

LEAD MODEL Version 0.99d Wh6 ?,5mb* 131, 56; \ 


:door AIR Pb Conc: 30.0 percent - of outdoor. 

-her AIR Parameters: 


0-1 

1.0 

2.0 32.0 

1-2 

2.0 

3.0 32.0 

2-3 

3.0 

5.0 32.0 

3-4 


5.0 32.0 

4-5 


5.0 32.0 

5-6 

6-7 



7.0 

7.0 

32.0 

32.0 

DIET: 

DEFAULT 



SOIL & DUST: 



Age 

0-1 

1-2 

2-3 

3-4 

4-5 

5-6 

6-7 


19.9 

19.9 

19.9 

19.9 

19.9 

19.9 

19.9 

DEFAULT 


23.9 

23.9 

23.9 

23.9 

23.9 

23.9 

23.9 





DEFAULT 




YEAR 

------ 

0.5-1: 

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

Blood Level 

(ug/dL) 

----------- 

2.0 

2.0 

1.9 

1.8 

1.6 

1.5 

1.5 

Total Uptake 

(ug/day) 

------------ 

3.60 


5.05 




5.22 


(ug/day) 

------------ 

0.54 

0.86 

0.86 

0.87 

0.65 

0.58 

0.55 

Diet Uptake Water Uptake Paint Uptake Air Uptake 

YEAR 

----e- 

(ug/day 1 

----------- 

(ug/day) 

------------ 

( ug /day 1 

------------ 

(ug/day) 

-------- 

0.5-1: 2.66 0.38 0.00 o. 02

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

2.78 

3.13 

3.02 

2.93 

3.10 

3.42 

0.96 

1.00 

1.03 

1.07 

1.13 

1.15 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

0.03 

0.06 

0.07 

0.07 

0.09 

0.09


z lboue: 0.01 


C. Mean: 1.9 

LElD 0.99d 

1 2 3 4 5 6 7 8 9 10 

BLOOD LElD CONCENIRlI I ON < ug/dL> 

0 to 60 Months





0-1 1.0 2.0 32.0 

1-2 2.0 

3.0 

32.0 

2-3 3.0 

5.0 

32.0 


5.0 

32.0 


5.0 

32.0 


7.0 

32.0 


7.0 

32.0 

DIET: 

DEFAULT 



SOIL & DUST: 



Age 

0-1 

1-2 

2-3 

3-4 

4-5 

5-6 

6-7 


117.0 

117.0 

117.0 

117.0 

117.0 

117.0 

117.0 

DEFAULT 


91.9 

91.9 

91.9 

91.9 

91.9 

91.9 

91.9 





DEFAULT 

MATERNAL, CONTRIBUTION: Infant Model 



YEAR 

------ 

0.5-1: 

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

Blood Level 

( ug /dL ) 

----------- 

3.0 

3.2 

3.0 

2.8 

2.4 

2.2 

2.0 

Total Uptake 

( ug /day 

------------ 

5.47 

7.59 

8.04 

8.01 

7.00 

6.98 

7.18 


( ug/day 

------------ 

2.47 

3.91 

3.94 

3.97 

2.98 

2.69 

2.55

1-2: 

2-3: 

3-4: 

4-5: 

-6 : 

*-7: 

2.70 

3.06 

2.97 

2.89 

3.07 

3.39 

0.94 

0.98 

1.01 

1.06 

1.12 

1.14 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

0.03 

0.06 

0.07 

0.07 

0.09 

0.09

I I I I I I I I I 

1 


z above: 0.39 


C. Mean: 2.9 

LEdD 0.99d 

2 4 6 8 10 12 14 16 

BLOOD LEaD CONCENTRLTION

LEAD MODEL Version 0.99d M 4~ 6 7 I sv mk 133, 6 

\ 

ATR CONCENTRATION: 0.100 ug Pb/m3 DEFAULT 

ndoor AIR Pb Conc: 30.0 percent of outdoor. 

,ther AIR Parameters: 


0-1 1.0 2.0 32.0 

1-2 2.0 3.0 32.0 

2-3 3.0 5.0 32.0 

3-4 4.0 5.0 32.0 

4-5 4.0 5.0 32.0 

5-6 4.0 7.0 32.0 

6-7 4.0 7.0 32.0 








SOIL & DUST: 



DEFAULT 

Age 

0-1 

1-2 

2-3 

3-4 

4-5 

5-6 

6-7 


162.0 

162.0 

162.0 

162.0 

162.0 

162.0 

162.0 


123.4 

123.4 

123.4 

123.4 

123.4 

123.4 

123.4 





DEFAULT 




YEAR 

------ 

0.5-1: 

1-2: 

-3 : 

-4 : 

4-5: 

5-6: 

6-7: 

Blood Level 

(ug/dL) 

-------____ 

3.5 

3.7 

3.5 

3.3 

2.8 

2.5 

2.3 

Total Uptake 

(ug/day) 

------------ 

6.44 

8.92 

9.44 

9.46 

8.13 

8.04 

8.22 


( ug/day 1 

------------ 

3.34 

5.27 

5.32 

5.37 


3.66 

3.46

YEAR 

------ 

0.5-1: 

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

Diet Uptake 

(ug/day) 

___------__ 

2.71 

2.69 

3.10 

3.02 

2.97 

3.17 

3.53 

Water Uptake 

(ug/day 1 

_______-____ 

0.37 

0.92 

0.97 

1.00 

1.05 

1.12 

1.14 

Paint Uptake 

Air Uptake 

( ug/day ) 

------------ 

(ug/day) 

-------- 

0.00 0.02 

0.00 0.03 

0.00 0.06 

0.00 0.07 

0.00 0.07 

0.00 0.09 

0.00 0.09

I I I I I I I I I I 


z Above: 0.97 


C. Mean: 3.4 

L 

LEAD 0.99d 

0 2 

- 

I I I 

4 6 8 10 12 14 16 18 


0 to 60 Months




Age Time Outdoors (hr) 

0-1 

1.0 

1-2 

2.0 

2-3 

3.0 

3-4 


4-5 


5-6 


6-7 


Vent. Rate (m3/day) 

2.0 

3.0 

5.0 

5.0 

5.0 

7.0 

7.0 

Lung a s . (%) 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 

3iet: al-ernate diet selec-ed by user as follows: 





3RINKING WATER Conc: 4.00 ug Pb/L 


DEFAULT 

SOIL & DUST: 



Age 

0-1 

1-2 

2-3 

3-4 

4-5 

5-6 

6-7 


200.0 150.0 

200.0 150.0 

200.0 150.0 

200.0 150.0 

200.0 150.0 

200.0 150.0 

200.0 150.0 





DEFAULT 

.YATERNAL CONTRIBUTION: Infant Model 


ZALCULATED BLOOD Pb and Pb UPTAKES: 

YEAR 

------ 

3.5-1: 

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

Blood Level 

(ug/dL 1 

----------- 

3.9 


3.9 

3.7 

3.2 

2.8 

2.6 

Total Uptake 

(ug/day) 

------------ 

7.13 

10.01 

10.55 

10.59 

9.00 

8.83 

8.97 


( ug/ day 1 

------------ 


6.40 

6.46 

6.53 




YEAR 

- ___- 

-1: 

--2 : 

2-3: 

3-4; 

4-5: 

5-6: 

6-7: 

Diet Uptake 

(ug/day) 

__----_-___ 

2.69 

2.66 

3.07 

3.00 

2.96 

3.16 

3.52 

Water Uptake 

( ug /day 1 

_-_-_------- 

0.37 

0.92 

0.96 

0.99 

1.05 

1.11 

1.13 

Paint Uptake 

(ug/day 1 

------------ 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

Air Uptake 

(ug/day 1 

------- - 

0.02 

0.03 

0.06 

0.07 

0.07 

0.09 

0.09


x Above: 1.76 


C. Mean: 3.7 

LEAD 0.99d 


0 to 60 Honthr

'LEAD MODEL Version 0.99d 

vk(93, 5wwU 13'4,s0'1\ 


idoor AIR Pb Conc: 30.0 percent of outdoor. 

,cher AIR Parameters: 


0-1 1.0 2.0 

1-2 2.0 3.0 

2-3 3.0 5.0 





DIET: 

DEFAULT 

Lung Abs. (%) 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 

32.0 



SOIL & DUST: 



DEFAULT 

Age 

0-1 

1-2 

2-3 

3-4 

4-5 

5-6 

6-7 

soil (ug Pb/g) 

26.0 

26.0 

26.0 

26.0 

26.0 

26.0 

26.0 


28.2 

28.2 

28.2 

28.2 

28.2 

28.2 

28.2 





DEFAULT 




YEAR 

__--__ 

0.5-1: 

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

Blood Level 

(ug/dL) 

----------- 

2.0 

2.0 

1.9 

1.8 

1.7 

1.6 

1.5 

Total Uptake 

(ug/day) 

-----_______ 

3.72 


5.25 

5.18 


5.04 

5.34 


( ug/day 1 

___--------- 

0.67 

1.06 

1.06 

1.07 

0.80 

0.72 

0.68

1-2: 

2-3: 

3-4: 

4-5: 

5-6: 

6-7: 

2.77 

3.12 

3.02 

2.93 

3.10 

3.42 

0.96 

1.00 

1.03 

1.07 

1.13 

1.15 

0.00 

0.00 

0.00 

0.00 

0.00 

0.00 

0.03 

0.06 

0.07 

0.07 

0.09 

0.09

I I , , , , , 

I I ( I I I I I I I I , 

Cutoff: 18.8 ug/dL - 

x Above: 0.82 

x Below: 99.98 - 

C. Hean: 1.9 

- 

- 

- 

- 

- 

- 

- 

- 

LEAD 8.99d 

3 ' W I ' - 

0 1 2 3 4 5 6 7 8 9 18

Appendix L. 11 

Superfund’s Standard Default Exposure Factors for the Central 

Tendency and Reasonable maximum exposure


DEC- 13-93 MON 645 h B W / E M P - 02 

DEC 1 6 1993 

FOR TBE CENTRAL TENDENCY AND 

REASONABLE MAXIMUM EXPDSVRE

DEC-13-93 W O N 

8:58 645 A B W A E M 

P, 

TABLE OF COtJTENTS 

1.0 iNTRODUCTfON 

L.l Cebtral Tendency 

1.2 Reasonable Maximum Exposure (EWE) 

1.3 Residential Exposure 

1.4 Occupational. Exposure 

(8 

2.0 CONCENTRATION 

- 

Page 

3 

5 

5 

6 

6 

c 

3.0 EXPOSURE FREQUENCY 

3.1 Central Tendency 

3.1.1 Residential 

3.. 1.2 Occupational 

3.2 Reasonable Maximum Exposure 

3.2.1 Residential 

3.2.2 Occupational 

4.0 EXPOSURE DURATION 

4.1 Central Tendency 

4.1.1 Residential 

4.1.2 Occupational c 

4.2 Reasonable Maximum Exposure 

4.2'.1 Residential 

4.2.2 Occupational 

5.0 BODY WEIGHT 

5.1 Child 

5.2 Adult 

6.0 INGESTION OF POTABLE WATER 


6.1. I Residential Ingestion Rate 

6.1.2 Occupational Ingestion Rate 

5.2 ReaSonable Maximum Exposure 

6.2.1 Residential Ingestion Rate 


7.0 INGESTTON OF SOIL AND DUSTS 

7.1 Central Tendency Exposure 

7.1,1 Chfld's Ingestion Rate 

7.1.2 Adult Ingestion Rate: Non-Contact Intensive 

7.1.3 Adult Ingestion Rate: contact Intensive 

7.1.4 Residential Exposure Scenario: Child + Adult 

7.1.5 Exposure Frequency and Duration: Central 

Tendency 


7.2.1 Child's Ingestion Rate 

7.2-2 Adult Ingestion Rate: Non-Contact Intensive 

7.2.3 Adult Ingestion Rate: Contact Intensive 

7.2.4 Residential Exposure Scenario: Child + Adult 

8 

6 

9 

9 

9 

9 

9 

9 

10 

10 

10 

10 

11 

11 

11 

1

l3EC-13-93 W O N s:59 6 5 4 5 A B W J E M 

P- 84 

7.Zr5 Exposure Frequency and Duration: FHE 

7.3 General Exposure Frequency and Duration 

Considerations 

7.4 Frabticn Ingested from the Contaminated Source 

7.5 Matkix Effect 

8.0 INHA1,ATION OF CONTAMINANTS 

9.0 IN,GGSTION OF LOCALLY CAUGHT FISH 

10 .o INGESTS& OF PRODUCE 

10.1 Total Produce Consumption Rates 

10.2 Crdp Specific Ingestion Rates 

.- 

11 

12 

12 

12 

13 

13 

14 

15 

16 

TABLE OF DEF@LT 

- KEFERENCES 

EXF’OSURE FACTORS 

17 

18 

2

1.0 INTRODUCTZON 

Last spring, EPA's Risk Assessment Council released a memorandum 

entitled "Guidance on Ri6k Characterization for Risk Managers and 

Risk AssessorsU (U.S. EPA 1992) in which the council advocated 

greater interface between risk assessment and risk management, 

greater discussion of confidence and uncertainty in the risk 

assessment, and presentation of the range of possible exposures 

including the use of multiple risk descriptors. Focusin-g 

specifically on this last point regarding the exposure 

assessment, the Risk Assessment Councfl (RAC) clearly indicated 

that it expects all risk assessments "to address or provide 

descriptions of (I) individual risk to include the central 

tendency and high end portions of the risk distribution, (2) 

important subgroups of the population such as highly exposed or 

highly susceptible groups or individuals, if known, and (3) 

population risk". 

. For several years now, the Superfund program ha6 considered 

exposure to sensitive subgroups or populations a8 applicable and 

has been estimating individual risk corresponding to the 

reasonable maximum exposure (RME). The Rtsk Assessment Guidance 

for SyDerfund: Human Health Evaluation Ma (Part A) (U.S. EPA 

1989) also known as RAGS, defines the -%the highest exposure 

that is reasonably expected to occur at a site and in practice is 

estimated by,combining 90 - 95th percentile values for some but 

not all exposure parameters. Shortly after RAGS was released, 

the Superfund Program developed the "Standard Default Exposure 

Factors" Supplemental Guidance (U.S. €PA 1991) t0 Promate 

consistency in the evaluation of the RME exposure in baseline 

risk assessments when site-specific data was lacking. It is the 

position of the Superfund Program that RACS and the standard 

default values for the RME are consistent with the Risk 

Assessment Council's expectation to provide a description of the 

high-end portion of the risk distribution. 

.. 

Until the guidance contained herein was developed, existing 

Superfund guidance did not provide a framework in which to 

estimate risk corresponding to the central tendency portion of 

the risk disttibution as called for by the Risk Assessment 

Council. Perceiving a need to fill this void, a workgroup was 

organized by the Superfund Program in October of 19928 comprised 

mainly of EPA Regional Superfund risk assessors, with the PurpQse 

of defining the central tendency for use in Superfund baseline 

risk assessments. Over the course of the following SfX months8 

the workgroup,convened periodically to discuss an approach and 

identify standard default exposure factors for the central 

tendency. In'doing so, the workgroup also felt it beneficial to 

review the current default exposure factors for the RME and 

identify whether any changes were warranted at this time. 

Consequently, this guidance builds on the concepts identified in 

RAGS Part A and the Risk Assessment Council's recommendations 

regarding risk descriptors for the central tendency. It 

supersedes the standard default exposure factors for the RME 

3

contained in the guidance of the same name (U.S. EPA 1991). 

Reliance on the point estimate approach vs. the use of monte 

carlo techniques to characterize the range of possible exposure 

estimates was initially discussed by the workgroup as both 

approaches have merit in addressing the Risk Assessment Council's 

call to present the range of possible exposures and risk 

outcomes. In the end, the workg_roup concluded that to0 many 

issues regarding the practical application of monte Carlo 

technique8 remained unresolved and would require a significant 

investment of time and resources to address such that the 

traditional point estimate approach to exposure assessments was 

favored at this time. Additionally, the point estimate approach 

to exposure vas deemed fully consistent with the intent of tho 

Risk Assessment Council in their memo. . 

As there pr6Bently is an agency-wide effort underway to address 

all Of the Risk Assessment Council8 s recommendations (including 

the use of mbnte carlo techniques and revisions to EPA's Exposure 

Factors Handbook iacorporating distributions for the Various 

exposure parheters), the guidance contained herein for the 

Superfund Prdgram is subject to change and consequently should be 

viewed as interim in status. When such agency-wide guidance is 

available, if is expected that it may supersede this guidance. 

The guidance'contsined herein has been developed to encourage a 

ConsiSt@nt approach to assessing exposures when there is a lack 

of site-specific data or consensus on which parameter value to 

choose, given a range of possibilities. Accordingly, the 

exposure factors presented in this document are generally 

considered mast appropriate and should be used in baseline risk 

assessments unless alternate or site-specific values can be 

clearly justified by supporting data. 

Supporting data for many of the exposure factors presented in 

this guidance can be found in the Exposure Factors Handbook (EFH; 

U.S. €PA, 1990). Additionally, in some instances, peer reviewed 

studies were utilized to identify suitable default values as well 

as group consensus techniques when a faced with a great deal of 

uncertainty. In these instances, either the study or a clearly 

documented logical approach used to identify default factors is 

referenced. 

The general exposure equation into which these standard factors 

are to be utilized is as follows: 

- Intake C x IR x EF x ED 

BW x AT 

C = 

uhere 

Concentration of the contaminant in a given medium 

IR = Intake/Contact Rate; the amount.of contaminated 

medium contacted per unit time or event 

EF = Exposure Frequency 

4

DEC-13-93 MON 0 1 8 1 645 F5BW/EM 

P. fa7 

ED * Exposure Duration 

BW t Body Weight 

AT PL Averaging Time (equal to exposure duration for 

non-carcinogens and 70 years for carcinogens) 

1.1 Cehtral Tendency (a) 

The Risk Assessment Council defined the central 

tendency risk descriptor as either the arithmetic mean 

risk or the median risk and continues to say that the 

arithmetic mean risk can be derived by using average 

va$ues for all the exposure factors though cautions 

that when dealing with skewed data, the median or 50th 

pekcentfle may better approximate the midpoint of a 

distribution (U.S. EPA 1992). As a result, any 

approach to the identification-of default factors for 

the central tendency should seek to identify average or 

50th percentile values whenever possible. In keeping 

with this approach, default exposure factors 

approximating the average or 50th percentile value have 

beCn identified whenever possible for use in central 

tehdency exposure evaluations. 

1.2 Rebaonablr Harthunt Exposure (RME) 

The Risk Use-ssment Council defined a high end risk 

descriptor as one which characterizes risk to an 

individual at the upper end of the risk distrabutlm. 

Conceptually, it can be equated to about the 90th 

pekcentile of the population distribution (U.S. EPA 

1992). As previously indicated, the reasonable maximum 

e+osure (RME) terminology used by the Superfund 

Prdgram is believed consistent with this description. 

Thd Risk Assessment Guidance for Suuqrfund : Human 

mlth E valuation Manual (Part A) (RAGS) defines the 

RME as the highest exposure that is reasonably expected 

to occur at a site and in practice is estimated by 

combining upper bound (90 - 95th percentile) values for 

sode but not all exposure parameters. Consequenrly, 

the Superfund Program will continue to use the current 

terminology of reasonable maximum exposure (-1 in 

fulfilling the Risk Assessment Council's mandate to 

evaluate a high end risk descriptor. 

In keeping with the previous default factor guidance 

(U-S. EPA 1991), 90 to 95th percentile values were 

targeted in this guidance document when identifying 

default factors for intake/contacc- rate, exposure 

frequency, and exposure duration. An average value or 

conservative estimate of the media average contacted 

over the exposuze period was targeted for 

identification of default values for body weight and 

exposure concentration respectively, 

5

DEC-13-93 W O N 9 l C a l 645 A B W / E M 

Within the context of this guidance, standard default 

exeosure factors have been identified for various 

exposure pathways and receptor populations owing to the 

differsnt nature and magnitude of the assumed 

exbosure. Generally speaking, default values for 

reeidentlal and occupational receptors have been 

identified and serve as the general basis for 

organization of this guidance. 

-- 

1.3 Reaideatirl Erpoauro 

Redidential default exposure factors are generally 

relevant whenever there are OE reasonably may be 

eaected to be residences on or adjacent to the site. 

The contadnation may be on the site itself or may have 

midrated from it. With the exception of exposure to 

contaminated soils, distinctions are not Usually made 

id the default parameters for exposures to different 

aged receptors. Because of the higher intake to body 

weight ratio presumed to occur during the early years 

(ages 1-6) for this exposure pathway, special attention 

should be given to evaluating exposure for this pathway 

and is discussed in sections 7.4. and 7.5. 

1.4 occbpationsi Exporruca 

Occupational default exposure factors are generally 

relevant whenever the site serves or may reasonably be 

cected to serve aa a place of temporary or permanent 

employment. Examples of employment in which one may be 

prebumed to come in contact with contaminated media 

dght include employment at the facility itself or 

nearby facilities (commercial/ industrial), servicing 

of fhe facility (grounds keeper/utility maintenance), 

or construction of new facilities oz the demolition of 

old facilities on or adjacent to the site. 

2.0 CONCENTRATION 

Central Tandedcy and RME 

The concentration term in the intake equation is the arithmetic 

average of the concentration that is contacted over the exposure 

period. _mmzua_the uncertainty associated with any estimate. 

0-Fexposure cdncentration, the 95% percent upper confidence limit 

an-the arithmetic average concentration will be used for this 

variable in both the central tendency and reasonable maximum 

e_aposure estidates. - Consideration should be given to the data 

set upon which the 954 upper confidence limit of the mean value 

is generated so as to represent as closely as possible the nature 

(acute vs. chronic) of potential exposures. 

In some instances, there may be great variability in measured or 

modeled concentration values such as when Qjp::few samples are 

taken or when model inputs are uncertain. I these cases the 

*-mu---!-* 

u p p e i ~ t * a ~ t haverage e concen +FE? a ion-zay- even 

exceed the x dm d u e observed or predicted. Should this 

6

DEC-13-93 W O N 9 : ~ 2645 A B W A E M 

P, la9 

scenario arise, then the simple arithmetic mean and maximum 

concentratioas's%%%ld-be'~used 'for the central tendency and 

reasonable maximum exposure concentrations respectively. 

3.0 EXPOSURE FREQWENCY 

The following default exposure frequencies may be utilized unless 

otherwise indicated or site-specific data is available. 

3.1 Cenhal Tendency 

3,k.l Residential 

The central tendency residential default exposure 

frequency of 234 days/year corresponds to the fraction 

of time estimated that is actually spent at home (64 

percent) for both men and women based on a study of 

time use patterns summarized in,the EFH W.S. EPA 

1990). Because the study included both personal and 

work related travel, a 365 day year was used from which 

to compute the 64 percent. 

3.1.2 Occupational ? 


3.2,.1 Residential 

The RME residential default exposure frequency of 350 

mystyear is based on the previously identified default 

value which assumes a two week vacation each year. 

This i s viewed as a reasonably conservative estimate of 

exposure frequency absent site-specific data. 

3.2.2 Occupational 

The RME occupational default exposure frequency of 250, 

dZy$/year Is consistent with the previously identified 

default value and is based on a 5 day work week with 

two weeks of vacation each year. This is viewed as a 

reasonably-conservative estimate of exposure frequency 

absent site-specific data. 

4.0 EXPOSURE DURATION 

The following default exposure durations may be utilized unless 

otherwise indicated or site-specific data is available. 

4.1 Central Tendency 


The residentfal central tendency default exposure 

duration of S'ycars is based on data summarized in the 

EFH (U.S. EPA 1990) in which the average length Of 

residence in the same house of people who own their own 

home was estimated to be 9 years. 

4.1.2zC-mpational ? 

7

nEC-13-9J W O N 9 r e 3 e 3 4 5 A B W / E M 

P- 1 8 

4.2 Rearonable Maximum Exposure 


The RME residential default exposure duration of 3.0 

%-ears is based on data summarized in the EFR (U.S. EPA 

1940) In which the 90th percentile for the length of 

residence in the same house of people who own their own 

home was estimated to be 30 years. 

4.2.2 Occupational 

The,.RME occupational default exposure duration of 25 

p,ears*is based upon the 95th percentile for the number 

of years worked at the same location as reported by the 

U.S. Bureau of Labor Statistics, 1990. 

5.0 BODY wEIGET 

The average body weight is to be utilized'for both the central 

tendency and pMe exposure evaluations in keeping with the 

- respective definitions. 

5.1 Child 

The approximate average body weight of young children (boys 

'ad girls combined) under the age of 6 years is 

approximately 15 kg (U.S. EPA 1990). Distributions of body 

weights hnd average body weights and for other age groups 

can be found in the EFH (U.S. EPA 19901. 

5.2 Adult 

The average body weight of XI--g corresponds to.the average 

weight of men and women age 18-75 as reported in EFH (U.S. 

EPA 1990). Distributions of body weights and average body 

weights for other age groups can be found in the EFH (U.S. 

EPA 19901. 

6.0 ZNGCSTXON OF POTABU WATER 


6-1.1. Residential Ingestion Rate 

The central tendency potable water ingestion rate for 

an adult-of 114 llday is based on the average intake 

observed from five studies as summarized in the EFH 

(U.S. €PA 1990). The observed range reported across 

the five studies was from 0.26 - 2.8 llday. 


Nosdata upon which to base a default value. 

6.2 Reasonable Maxhwa Exposure 

6.2.1 Residential Ingestion Rate 

The RME potable water ingestion rate of-FUday is 

close to the 90th percentile of values measured and 

estimated by researchers as summarized in EFH (U.S. €PA 

1990). It is also the value currently used by EPA's 

Office of Water in establishing drinking water 

standards. 

8

DEC-13-93 MON 

9 r e 3 645 A B W / E M 

P, 11 

.. 

* . 

c 

6.2.2. Occupational Ingestion Rate 

Nn data upon which to base a default value. 

7.0 INGESrXbN OF SOIL AND DUST 

Due to the importance of the receptor's age and behavioral 

characteristics, default ingestion rates for this exposure 

pathway have been established based on the characteristics of the 

receptor rather than on the location of the exposure (residential 

vs. occupatidnal). Default ingestion rates for this pathway are 

as described Qelow in Sections 7.1 and 7.2- 


7 .l.l. 

child's Ingestion Rate 

Nunierous studies have documented that the propensity to 

ingest non-food items is greatest in the early years of 

development, As a result, children between the ages of 

l'and 6 years are of greatest concern as they are 

expected to have the greatest exposure to contaminated 

soils and dusts via ingestion. Numerous studies 

(tracer studies and estimates of deposationfexposed 

,surface area) have resulted in wide ranging estimates 

of the amount of sail and dusts ingested by young 

children'making it difficult to identify a single value 

for' use as the central tendency. Additionally, owing 

to the nature of the experimental studies, it is 

extremely difficult to separate the contribution to 

exposure resulting from exterior soils vs. interior 

dusts. As d result-the ingestion rate is reported as 

the combined rate for soils and dusts. 

It vas believed by-a consensus of workgroup members 

that the iestian rate of 100 mg/day as a Central 

tendency ingestion rate for a child between the ages of 

r6yyears was within reason based on results using 

traeer elements (Davis et al. 1990 and Calabrese 19891. 

Furthermore, 100 mg/day is nearly identical to the 

ingestion rate for this age group based on age specific 

values utilized in support of the NAAQS for lead (U.S. 

EPA 1989b) and the lead biokinetic uptake model. 

7.1r2 Adtflt'!.s Ingestion Rate: Non-Contact Intensive 

For the adult who does Rot engage in soil or dust 

contact intensive activities on a regular basis 

(apartment dweller, typical homeowner, office worksf, 

teacher, professional, etc.) the soil and dust default 

inge]stion rate for the central tendency of SB,aq/daybased 

on a study of Calabrese 1990 (with supporting 

estimates from Hawley 1985). 

7.1.3 Adult's Ingestion Rate: Contact Intensive 

For adults who routinely engage in heavy contact with 

soils and dusts on a regular basis (including seasonal 

work), the workgroup was unable to identify a default 

9

DEC-13-93 MON 

.. 

9 1 m 4 645 raBW/EM 

P- 1 2 

-. 

soil ingestion rate corresponding to the central 

tendency given the data available. Tt is suggested 

that an evaluation of the RME scenario for this 

receptor be conducted. 

l.i.4. W3;iiential: Child + Adult Combined 

In evaluating a residential exposure scenario for this 

pathway, a weighted average of the child's and adult's 

exposure is to be utilized. The duration of exposure 

fog.the central tendency ha6 been defined as consisting 

of'riihe-years (average number for years at the same 

dwelling). It is the default position to assume that 

fat 2-of the nine years, intake will be at the child's 

rate and'xor-the rernaining-Tyears, intake will be at 

thq-adult rate, This is consistent with the proportion 

of time one is assumed to be a young child that is 

utilized for Fua residential calculations. Thus 

residential exposure for the central tendency should 

generally be evaluated as follows: 

4- ,$*35 9 7 

2 Years x 100 ma/dav t 7 Years x 50 ma/dav 

q3 

15 kg 70 kg 

-- 

--, 

7,1,.5 Exposure Frequency and Duration: Central Tendency 

The default value for the duration of exposure for the 

central tendency scenario is 9 years for a residential 

ex&sure based on the average length of stay in a home 

as keported in the EFK (U.S-EPA 1990). It should be 

noted that generally the intake over the 9 year 

exposure period is to be computed as described in 

section 7.1.4. The default 

+ 

expasura..freaue ncy- €or the 7 

central tendency is 350 da s/ ea-rrdue to the nature in 

which the soil ingest on rates have been computed 

(avkrage daily exposure). 

A default exposure frequency and duration has not been 

specified for the central tendency occupational 

scenario at this time as St ha8 not been discussed by 

the workgroup. 


7.2.133@3-ci!.$;rirgestion Rate 

The'default RME ingestion rate for a young child age 1- 

6 years of age of .-28b~~g~day_represents the consensus 

opinion of the workgroup based on review of available 

data and is believed to correspond to a conservative 

estimate of an average ingestion rate for this age 

group over a chronic period of exposure. 

Unfortunately, the available data did not support 

identification of the 90 or 95 percentile value, 

was the consensus among workgroup participants that 

over the 6 year period of concern for this receptor 

category, the value of 200 mg/day waa reasonable to 

It 

10

DEC-13-93 MON -:e4 64s A B W / E M P- 13 

t ~ 

assume. It should be noted that this value was nPt 

F,cessarily deemed relevant for acute exposures when a 

child may-engage in intensive contact with Soils and 

dusts for a brief period of time. In these situations, 

ingestion rates greater than this value may be 

warranted. 

7.2.2 Adult's rngestion Rate: Non-Contact Intensive 

The M default soil and dust ingestion rate of 100 

mi#day is based a study of Sedman (1989). This value 

is presumed suitable for non-contact intensive 

scenarios (apartment dweller, typical homeowner, off ice 

worker, teacher, professional, etc. 1 

7.2.3'Adult's IngestiQn,Rate: Contact Intensive 

The RME default soil and dust hgestion rate of 480 

%>/day is deemed appropriate for acute exposures (those 

le6s than a year in duration). This value is based on 

estimates made by Hanley (19651 in which he estimated 

deposition rates, exposed surface areas of the hands, 

and the fraction inadvertently consumed. 

7.2.4 RG'T*&ntial: Child + Adult 

In evaluating a residential RME exposure scenario, the 

exposure duration for the RME has been defined as 

consisting of 30 years (90 percentile for years at the 

same dwelling U.S. EPA 1990). It shall generally 

assumed when evaluating the RME residential exposure 

for the ingestion of soil and dusts that fxts6'of the 

Wy-ears, intake will be at the child's rate and for 

.the remaining 24 years, intake will be at the adult 

w e . Thus residential RME exposure for this pathway 

should generally be evaluated as follows: 

a 

4 vears x 200 mq/dav + 24 v ears x 100 mu/dav 

15 kg 70 kg 

-T 

7.2.5 Exposure Frequency and Duration: RME 

The default value for the duration of exposure for the 

RME scenario is 30 years for a residential exposure 

based on the 90th percentile for the length of stay in 

a home as reported in the EFH (U.S.EPA 1990). It 

should be noted that generally the intake over the 30 

year exposure period is to be computed as described in 

section 7.2.4. The default exposure frequency for the 

RME is 350 daysjyear due to the nature in which the 

sail ingestion rates have been computed (average daily 

exposure) and assuming a two week period away from home 

each year. 

The default value for the 

RME occupational scenario 

percentile for the number 

11 

-. 

c 

y& 

H4.3 1(, 

duration of exposure for the 

is 25 years based on the 95th 

of years worked at the same

DEC-13-93 W O N 

-. 

9:e5 645 A B W / E M 

- 

P, 14 

location (Bureau of Labor Statistics 1990). The 

exposure frequency of 250 days/year corresponds to a 

. five day work week, 

7.3 

7.4 

General Exposure Fzequency and Duration Considerations 

Owing to the strong age and behavioral dependent nature 

of'this exposure, exposure durations and frequencies 

other than the default values may be warranted for this 

exposure pathway. For example, a situation may arise 

in'which a child-care facility is of concern and the 

residential default values for exposure frequency and 

durtation may not be appropriate. Similarly, certain 

occupations may lead to intensive exposure but for 

brief periods of time (i.e. construction workers, field 

laborers, seasonal workers, etc.) rendering use of the 

occupational default values for' exposure frequency and 

dJration Inappropriate. 

Additionally, there may be situations in which a Region 

believes it necessary to adjust the exposure frequency 

to account for meteorological conditions which may be 

presumed to drastically reduce or eliminate exposure to 

potential contaminants via soil ingestion. In these 

situations, any adjustments to tho exposure freWenCy 

to reflect local weather patterns should first be 

approved by the Regional Office- 

For these reasons, the default exposure durations and 

exposure frequencies may not always be relevant for the 

expesurt at hand. Elctra care should be taken when 

idehtifying suitable exposure frequencies and durations 

far this exposure pathway. 

Frahtioa Ingested From the Contaminated Source 

The fraction ingested from the contaminated source is 

an important variable that often gets overlooked when 

evaluating scenarios that are largely dependent on the 

receptor coming to the source of contamination rather 

than the contamination migrating to the receptor. Dub 

Eo variations in the proximity of the receptor to the 

contaminated source, size of the contaminated source, 

recaptors of concern, mobility of receptors, and the 

nat\ire of exposure, default values for the fraction 

ingested from the contaminated source are not possible. 

Howdver, *it-advocated that this factor be given, 

e a - catef ul cansid~r~t~on-w~e~-'e~iuating this 

eiiposuKpTEiiay. 

7.5 Matrix Effect 

A parameter unique to all combinations of compounds and 

soil types- the matrix effect - accounts for the 

tendency of a compound to bind to soils. The more 

"soil loving" a compound is, the less likely it is to 

12

DEC-13-93 W O N 

645 A B W / E M P, 1s 

l- 

de$orb and become bioavailable in the gastrointestinal 

tr+ct once ingested. Chemical and physical properties 

of contaminants and tho soil. can thus have a profound 

effect on the bioavailability of a compound. 

Unfortunately che data do not exist to support default 

desorption values for all compounds at this time though 

work i s currently underway to develop some guidance in 

this area. At present, any adjustments for this 

phenomenon are left open to the discretion of the 

Regional Office. 

8.0 INBALATl!ON OF COHTAXINANk8 

It is antiddated that at some time in the future, inhalation 

exposures w i l l be evaluated using inhalation reference 

concentrations. However, at this xime, tbe methodology is not 

yet avcilabJe and consequently, inhalatian rates and resulting 

dose (mg/kg/day) are the approach that is advocated for this 

- exposure pathway. Inhalation rates are dependent on age, sex, 

and activity level to name just a few factors and can be fbwd in 

the-Exposure Factors Handbook (U.S. EPA 1990). 

The same defajalt inhalation raEa,h@$,Been Adentified for both the 

central tendehcy and-the-!posure sceparios. Thfs is in 

keeping with the assumption regarding inhalation rate used in the 

derivation of, cancer potency estimates and inhalation reference 

concentrations. . The default value of m-m'!jday COrreSpOndS to a 

reference man's inhalation rate who is at rest 8 hourstday and at 

a light activity level (i.e. domestic work, personal care, 

hobbies, minor indoor home improvements) for the remaining 16 

hours/day. 

9.0 INGESTIO~ OF LOCALLY -GET FISK 

The evaluation of this exposure pathway will not always be 

relevant to ebery site. The receptor of concern for this pathway 

is apt to include both the recreational fisherman and a 

subsistence fisherman and thear family. The preferred approach 

to the evaluation of this errpasure pathway is to obtain site? 

specific-dqregarding consumption rates and fishing habits. 

This is due tb the strong influence of local habits, populations, 

and condition9 on the resulting exposure. 

when site-specific data are not feasible to obtain, tEKdefatalt 

app-r3-deF-SUgg88ted for thls exposure pathway is based on an 

cst&g~tk or-the avara&e- sizeof a fish meal and merely varies the 

e%posure freqiency,-duxation, and fraction ingested from the - 

Sontaainated Source between the central tendency and the RME 

estimates. With this approach, recreational and subsistence 

fishermen can be assumed to consume the same amount of fish per 

eating occasidn yet differ in the frequency or number of fish 

meals actual13 consumed and the fraction of fish meals consumed 

that originated from the contaminated source. This change in 

approach was adopted because it was believed to better 

characterize exposure resulting from an intermittent and often 

13

D€C-13-9= W O N 

.- 

- 

9:@6 6.45 A B W / E M 

.. 

P, 16 

infrequent dxposure pathway than the default approach previously 

advocated which relied on an intake rate averaged over a year of 

exposure. 

he average :amount of fish consumed per eating,Bccaaion was 

observed to be ldS.g/6eal- or about 5 ounces as reported in the 

study of Pad et al. (1982). The range reported far the size of 

the fish mea?. was from 43 g/meal (5th percentile!_tO 565 g/meal 

(99th percentile). The study vas based on the results Of a selfadministere+USDA 

nationwide consumption survey from 1977-78 of 

individuals in 48 states. The amount of fish corresponds to 

consumption habits for fin-fish as reported on-.a:uet weight 

basis. It' daes not include shellfish. Although fish consumption 

habits have ,likely increased over the past 15 years, the Pa0 

study was believed to be the best study available upon which to 

base a default value. 

Owing to the very site-specific nature of the frequency of this 

exposure, no:defaults are given at this time for exposure 

frequency (fish meals/year) . However, estimates of the average 

and 90th - 95th percentile for the frequency of exposure should 

be used for the central tendency and RME respectively, Default 

values for *sure duration are those which are consistent with 

residential default values previously identified of-9'yearsmar 

qqntral tendency and 30.years €or the RHE. Additionally, it 

was believed that a site-specific value far tho fraction of fish 

consumed iroh tho contaminated source was appropriate rather than 

establishing'a default value for this factor. The average and 

the 90th - 45th percentile values are suggested far the central 

tendency and RME for this parameter respectively. 

10.0 INGESTiQN OF PRODUCE 

The fOllowin approach has been suggested for this exposure 

pathway prov I! ded it is relevant to the risk evaluation: 

a. Strongly consider evaluating consumption of homegrown 

produce if it constitutes a current exposure pathway and if 

produce,ia available for analysis. If produce is not 

available for analysis, evaluation of this exposure pathway 

is open to the discretion of the Regional Office 

(recognizing that this decision is apt to depend on,the 

level of confidence in available plant uptake models). 

b. If the decision is made to employ an uptake model, the 

Region is strongly encouraged to seek the assistance and/or 

review of the proposed approach by ECAO-Cincinnati. 

c. e?n*evaluating this exposure-pathuayr preference should-, 

be given for site specific-consumption rates (obtainable vfa 

door tO :door surveys) if feasible., When site specific 

consmptfon rates are not feasible, either generic defaults 

regarding total consumption rates for all fruits combined or 

all vegetables combined (uSDA 1960) or defaults based on the 

14

mEC- 13--9= MON -3rla-r 645 A B W / E M 

average amount of a fruit or vegetable consumed on a given 

eating occasion (Pao et al- 19821 together with site 

specific exposure frequencies is suggested. 

d. The fraction ingested assumed to originate from a 

contaminated source will always be a site specific 

determihation. 

The choice of which of the approaches described belzw should be 

utilized for'the identification of default ingestion rate values 

1s left up to the risk assessor based on their understanding of 

the site. T)ze USDA (1980) results are based on the average 

consumption rate as self-reported over a three day period and 

included non-consumers as well as consumers in the calculation. 

In contrast,nthe data of interest from Pa0 et a1.(1982) focused 

on the amount consumed of various food crops far a given eating 

occasion. m2irk"d3men def sult values .are used,,Lhe same 

ingestion rake utilize%"far-the-'central tendency is advocated far 

use in evaluking the RME scenario.yXf'- lib euggested that in 

these 

- 

instances, merely-the exposure frequency, duration, and the 

fraction ingbsted from the contaminated source vary between.the 

central tendency and the RME evaluations- 

10.2 Total produce Consumption Rate8 (USDA 1980, U.S. EPA 

1990) 

A8:summarized fn the EFH (U.S. EPA 19901, the USDA 

estimated the average intake on any one day of.dClfsits 

combined-AsaUkgt rson and 

oximatcly -11s of t h i s ~ ~ ~ ! ~ be 6 dssumed & ~ d 

8- much"~3f10 of this 

C92'glday) could be assumed to be homegrown as a 

reaqonable m maximum exposure case. 

Thb average intake on any one day for ai&&--vegstables 

w n e d was- estimated as 201 g/dawg-ZJrt_hermore, 

approximately 1/4 (50 g/day) of this amount could be 

assumed ta-be homegrown-on average and astlnuch as 215. 

(864 gtaay c a u F ~ ~ ~ ~ 

reasonable maximum exposure case. 

Due to the nature of the study, (a daily average intake 

over a three day exposure period), it can be assumed 

that the contact rates represent a chronic value. If 

this approach is selected, then the exposure frequency 

.e. 

for the- central" tendency and-WE-should be 356- 

diy'styear. The defaq t-ex -duration-raf lects the 

reddential- central -$,,tr,'p ten ency value of -mrs-or 30: 

ysars-fdr-the-RME scenario- Assumptions regarding the 

fraction ingested from the contaminated source are not 

specified though national averages for the fraction 

that can be assumed to be homegrown have been suggested 

as a described above. 

15

P- 18 

10.2 

- 

Crop Specific coasumption Habits (Peo et al. 1992) 

As, sumrnerized in the attached table, average values for 

the amount of a particular fruit or vegetable consumed 

on a given eating occasion can be identified based on 

the results of a nationwide survey conducted by the 

USDA as summarized in Pa0 et al. (1982). Additionally, 

the authors' reported the distribution of consumption 

vahes observed for each fruit or vegetable included in 

the survey. The Pao at al. data was based on the USDA 

nationwide food consumption survey conducted In 1977- 

78 Y 

Default values for the frequency of exposure have not 

been identified and are subject to site-specific 

determinations reflecting local consumption habits. 

The default exposure duration reflects the residential 

cgdtral tendency value of 9 years or 30 years for the 

W E scenario. The fraction ingested originating from 

the contaminated source has not been specified but is 

open to consideration of site-specific factors. 

16

P. 19 

C. . 

.I 

14Sghnd -fK 30 years 

wslh % 

70 kg

. 

m 

2 

Attachment 2 . 

Quantity Consumed Per ellno OCCaSlOn of Various Frultr and Ve@abltm (gram) 

Paa et. al. 1982 

Percontlte 

std. 

I 

food category WQ. dw. 5th 25th 60th 75th BOW 95th 99th Max. 

fresh grapefruit 159 58 106 134 134 165 268 268 330 660 

fresh oranges 146 57 73 14s 145 145. iao 228 360 1160 

appk3 141 49 69 138 138 138 212 212 276 636- 

bananas 106 37 SO 95 119 119 136 238 476 

canteloup 

171 91 61 136 136 272 212 272 529 896 

,raw pears 163 68 82 164 164 164 164 320 , 328 2132, 

raw peaches 160 75 76 152 I52 152 304 364 ' 456 760 

raisins 39 28 3 14 28 43 73 ' 73 145 290 

white potatoes 125 90 29 03 105 170 236 280 426 1260 

cabbage /cole slaw . 68 45 15 40 60 90 120 120 240 1020 

Q - 

faw carrots 43 40 4 13 31 55 100 122 183 500. 

raw celery 

33 24 8 17 28 40 60 80 120 204 

g raw cucumbers 80 78 8 24 10 110 158 220 316 840 

lefluce/tossed salads 65 59 10 20 5s 93 140 186 270 1080, 

B raw onions 

31 33 3 17 18 36 57 72 180 350 

Et 1 raw tomoatoes 81 55 30 45 62 119 123 182 246 72E! 

cooked bromli 112 68 30 78 90 165 185 190 360 680 

cooked cabbage 128 83 28 75 145 150 225 300 450 610 

- cooked cartots 79 50 19 46 75 92 150 155 276 736 

m 

,r mrn onloff cab 

95 56 21 65 83 123 170 170 330 050 

$ lima beans 110 75 21 67 88 I70 1?5 219 350 075 

01 cow peas, fleld peas and 

p blackeve peas 131 aa 22 88 88 175 196 350 350 ?OO. 

u aaokedgreenpeas 90 57 20 43 85 05 170 170 330 080 

3 cooked spinach 121 70 24 ?0 103 185 205 205 380 454 

o strlng beans 86 54 18 67 16 135 140 140 280 840 

cooked summer squash 145 98 27 105 108 215 215 352 430 860 

cooked sweet potatoes 136 87 38 a6 114 is5 225 230 450 1020 

cucumber pickles 45 45 7 30 65 30 130 222 455 

i 

Cooked vegetables Includes canned.

DEC-13-9Z MON 

9te9 645 ABW0-EM 

P.21 

c- . 

WFERENCES 

Calabrese, E.J., Barnes, R., Stanek, E.J., Pastides, H., Gilbert, 

C.E., Veneman, P., wang, X., Lasztity, A., and P.T. Kosteck. 

1989. 3ow Much soil Do Young Children Ingest: an EpldemioLogic 

Study. Reg. (rax. and Phamac. 10:123-137. 

Davis, S., Wallerr P1, Buschbom, R., Ballou, J. and P. White. 

1990. Quantitative Estimates of Soil Ingestion in Normal 

Children between the Ages of 2 and 7 Years: Population-based 

Estimates Using Aluminum, Silicon, and Titanium as Soil Tracer 

Elements. Are. Environ. Health. 45(21 :112-122. 

Hawley, J.K. 1985. Assessment of health risk from exposure to 

contaminated soil. Risk Analysis 5 (4) : 289-302- 

.. 

- Pao, E.M, Flehing, K.H., Guenther, P..M. et al. 1982. Foods 

commonly eateh by individuals: amount per day and per eating 

occasion- W.$. Department of Agriculture. Home Economics Report 

No. 44. 

Sedman, R. 1989. Development of Applied Action Levels for Soil 

Contact: A Scenario for the Exposure of Humans to Soils in a 

Residential Setting. Environmental Health Perspectives. VOl 79, 

pg 291-313. 

W.S. Bureau of Labor Statistics. 1990. Statistical summary: 

tenure with current employer as of January 1987. (transmitted 

via facsimile, Sept. 7, 1990). 

USDA., 1380. W.S. Department of Agriculture. Food and nutrient 

intakes of individuals in one day in the United States, Spring 

1977. Nationwide Food Consumption Survey 1977-19778. Preliminary 

Report No. 2 . 

U.S. EPA 1989.n Risk Assessment Guidance for SuPerfund: Human 

Health Evaluation Manual (Part A) , EPA/540/1-89-002. December 

1989. 

U.S. EPA 1989b. Review of the National Ambient Air Quality 

Standards for 'Lead: Exposure Analysis Methodology and Validation. 

USEPA Office of Air Quality Planning and Standards. EPA 450/2- 

es/oii. 

U.S. EPA 1990. Exposure Factors Handbook. EPA/600/8-89-043. 

March 1990. 

U.S. €PA 1991. "Human Health Evaluation Manual, Supplemental 

Guidance: Standard Default Exposure Factors". OSWER Directive 

9285.6-03. March 25, 1991. 

U.S. €PA 1992. "Guidance on Risk Characterization for Risk 

Managers and Risk Assessors. Memorandum from Henry Habicht to 

Assistant Administrators. Feb. 26, 1992

APPENDIX M 

SCREENING ECOLOGICAL RISK ASSESSMENT 

TABLES

Table 6.1. Toxicological benchmarla for screening contaminants of potential concern for efkctr on aquatic biota 

Estimated Estimated Estimated LCV I* Scnsitive 

LO"* uNSL EC,- Aquatic Lev'* Lev'* LCV'* EC,'* Species Test Population Secondary Secondary NAWQC'* NAWQC" 

Chemical CAS Number Daphnidt Fish Fish Masts Dapbnidi Fitb Invertebrata Daphnids EC,- EC,- Acute Values' Chronic Values Acute Chronic 

Aluminum 7429905 460 lpoo 1288 540 75 750 87 

Antimony 7440160 610 5400 IM)o 1900 79 985 104 

Arsenic 74403112 

Barium 7440391 5800 69 I 18 

Cadmium 7440439 2 0 I3 17 0 75 0013 41 1.9 I I 

Calcium 7440702 I IM)o 

Chloride 161187006 

Chmmium I8540299 2 6 132 73.18 05 0 266 I16 16 II 

Cobalt 7440484 5. I 290 44 3 98 195 106 

coppa 7440508 I 0.21 38 6.066 0 205 0 26 8.6 18 12 

Imn 743911% I58 1300 16 loo0 

Lud 7439921 500 12 26 I8 118 25 46 0 35 71 82 32 

Magnesium 7439954 82000 

Mang~!W 743996s I loo I 770 I 100 I12 1470 80 1 

Nickel 7440020 5 5 35 128 4 45 II 213 1400 I60 

Potassium 7440097 53000 

Selenium 7782492 100 91.65 118.32 23 260 260 15 

Siliean 7440213 

Silva 7440224 10 2.6 0 12 0 56 0 14 0 12 0 36 4 10 

Sodium 7440235 moo00 

Stmntium 7440246 42000 6100 620 

Thallium 7440280 100 130 57 64 67 164 180 

Vandium 7440622 940 80 410 12 284 19 I 

Zinc 7440666 10 46.71 36.41 5243 21 80 I20 I IO 

Chlomfonn 67661 4481 I240 ' $62 3360 I88 

Methylene Chloride 75092 

Toluene 108883 25229 1269 245000 200 1150 I76 

bii(2-Ethylhoyl)phLalate I17817 3 8.4 3 50 286 12 2 

cis4 . 2-Dichle 

I36592 

Ethylbenzene 100414 12922 438000 440 198 6970 189 

I - LCV - Lowest Chronic Value 

2 - EC" . Effective Conccnlrltion that a reduction of 20% of the gowrh prOhKtion m n 

3 - NAWQC -National Ambient Water Quality Criteria 

a - All toxicity value were cxtnaed fmm 'PC-Dam Buc: Screening Bmchmuiu fm Emlogical Risk Assessment (revised Dccanba 1994)' 

Environmental Sciences Division. Hulth Scienca Raurch Division, ORNL 

- - m toxicolagiul benchmark wu unavailable

Table 6.2. Toxicological benchmarks for screening contaminants of potential concern for effects on sediment-associated biota 

Effects Effects EPA I,' 

Chemical CAS Number Range Low ange Mcdiu OMOE '*' EPA *' Region V H&S '.' WIDNR "' 

Aluminum 7429905 

Arsenic 

7440382 

Barium 

7440393 

Beryllium 

7440417 

Calcium 

7440702 

Chromium 

I8540299 

Cobalt 

7440484 

Copper 

7440508 

Iron 

7439896 

Lead 

743992 I 

Magnesium 

7439954 

Manganese 

7439965 

Mercury 

7439976 

Nickel 

7440020 

Potassium 

7440097 

Selenium 

7782492 

Sodium 

7440235 

Vanadium 

7440622 

Zinc 

7440666 

Acetone 

6764 I 

Benzene 

71432 


1 I7817 


84742 

Fluoranthene 

206440 

Phenanthrene 

85018 

Pyrcne 129000 

1 = OMOE - Ontario Ministry of the Environment 

2 = EPA - United States Environmental Protection Agency 

3 = H&S - Hull and Suter 

4 = WINDR - Wisconsin Division of Natural Resources 

8.20E+00 

8. I OE+O 1 

3.40E+OI 

4.678+01 

1.50E-01 

2.1 OE+01 

1.50E+02 

7.00E+OI 

3.708+02 

2.708+02 

2.18E+02 

7.10E-01 

5. I6E+OI 



I. 70E+04 

6.408-02 

5.208-02 

8.908+05 

4.2 I E+OI 

a =All toxicity values wen extracted from "PC-Data Base: Screening Benchmarks for Ecological Risk Assessment (revised December 1994)" 

Environmental Sciences Division, Health Sciences Research Division, ORNL 

- = no toxicological benchmark was unavailable 

5.00E+02

Table 63 Toxicological benchmarlo for screening contpmhwb of potential concern for 

effects on soil and Utter invertebmtes and hetertrophie proceaaca' 

Contaminant CAS ID Plants SoWerobes Enrthwom 

(mg/kg) (dG3) (mg/kg) 

91576 

99092 

50293 

83329 

208968 

67641 

120127 

11096825 

71432 

56553 

50328 

205992 

191242 

207089 

117817 

86748 

218019 

84742 

53703 

132649 

206440 

86737 

193395 

91203 

85018 

129000 

108883 

79016 

1330207 

7429905 

76644 17 

7440360 

7440382 

7440393 

7440417 

7440439 

7440702 

18540299 

7440484 

7440508 

57125 

7439896 

743992 1 

7439954 

7439965 

7439976 

7440020 

7440097 

7782492 

7440224 

7440235 

7440280 

#N/A 

#N/A 

MIA 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

MIA 

MIA 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

200 

#N/A 

#NIA 

#N/A 

#N/A 

#N/A 

#N/A 

#NIA 

#N/A 

200 

#N/A 

0 

50 

#N/A 

5 

10 

500 

10 

3 

#NIA 

1 

20 

100 

#N/A 

0 

50 

#N/A 

500 

0.3 

30 

#NIA 

1 

2 

#N/A 

1 

#N/A 

#N/A 

#NIA 

#NIA 

#N/A 

#NIA 

#N/A 

#NlA 

MIA 

#N/A 

#N/A 

#NlA 

#N/A 

#N/A 

#N/A 

#NIA 

#N/A 

#NlA 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

MIA 

#N/A 

#N/A 

#NIA 

MIA 

6.00E+02 

MIA 

#N/A 

1 .OOE+02 

3.00E+03 

#N/A 

2.00E+01 

MIA 

1.00E+01 

1.00E+03 

1.00E+02 

#N/A 

2.OOEM2 

9.00E+02 

#NIA 

1.00E+02 

3. WE4 1 

9.00EMl 

#N/A 

1.00E+02 

5.0OEM1 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

MIA 

#NlA 

#N/A 

#N/A 

#N/A 

#N/A 

#NlA 

#N/A 

#N/A 

#N/A 

#NIA 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

3.00E+0 1 

#N/A 

#N/A 

#N/A 

MIA 

#NlA 

#N/A 

#NIA 

#N/A 

#N/A 

#NIA 

6.00EM 1 

#N/A 

#NIA 

2.00EN 1 

#N/A 

4.00E-o 1 

#NIA 

5.00E+01 

#N/A 

#N/A 

5.00Ei-02 

#NIA 

#N/A 

1 .OOM1 

2.00E+02 

#N/A 

7.00E+01 

#NIA 

#N/A 

MIA

Table 6.3 (continued) Toxicologial benchmarks for screming contaminants of potential concern for 

efferts on roil and litter invertebmtea and hetertmphic prac-' 

Contaminant CAS ID Phts SoilMicroba Jhrthworms 

(mg/kP) (mg/kg) (mg/kg) 

V d U m 7440622 2 2.00E+01 #N/A 

Zinc 7440666 50 1 .OOE+O2 2.00E+02 

a - All benchmarks extract4 hm PC-Data Base: Screening benchmarks for ecolo@d risk ass*ismcnt 

Revised December 1994. Environmental Sciences Division & Health Scicnces Research Division, 

Oak Ridge National Labomtory. 

#NA = Benchmark not available.

Table 6.4 Todcologial bmchmnrlo for r c contaminants ~ of potential concern 

for effects on nildliTe' 

91576 

99092 

#NIA 

#N/A 

#N/A 

#N/A 

#NfA 

#N/A 

50293 

83329 

208968 

1.586 

#N/A 

#NfA 

1.994 

#N/A 

#NfA 

2.262 

#N/A 

#N/A 

67641 

19.825 

24.92 

#N/A 

120127 

MIA. 

#N/A 

#NfA 

11096825 

#N/A 

#NIA 

#N/A 

71432 

23.23 

29.201 

33.135 

56553 

50328 

#N/A 

0.88 I 

MIA 

1.108 

#NIA 

1.257 

205992 

191242 

207089 

117817 

#N/A 

#N/A 

#N/A 

16.154 

#N/A 

#N/A 

#N/A 

20.305 

#NIA 

#N/A 

#N/A 

23.041 

86748 

218019 

84742 

53703 

132649 

206440 

#N/A 

#N/A 

484.699 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

609.274 

#N/A 

W A 

#NlA 

#N/A 

#NlA 

691.356 

#N/A 

#NIA 

#N/A 

86737 

193395 

91203 

85018 

#N/A 

#N/A 

UNIA 

#NIA 

MIA 

#NIA 

#N/A 

#N/A 

#NlA 

#N/A 

#N/A 

#N/A 

129000 

108883 

79016 

#N/A 

22.895 

0.617 

#N/A 

28.78 

0.175 

#N/A 

32.6J7 

0.88 

1330207 

7429905 

7664417 

7440360 

1.815 

1.701 

#NIA 

0.11 

2.282 

2.138 

W A 

0.138 

2.589 

2.426 

#N/A 

0.157 

7440382 

7440393 

7440417 

0.111 

10.777 

1.308 

0.14 

13.547 

1.645 

0.158 

15372 

1.866 

7440439 

7440702 

18540299 

7440484 

0.169 

MIA 

6.502 

#N/A 

0.212 

#NIA 

8.174 

MIA 

0.24 

#N/A 

9.275 

#N/A 

7440508 

32.826 

41.263 

46.822 

57125 

74398% 

12.547 

MIA 

15.772 

MIA 

17.897 

#N/A 

743992 1 

15.86 

19.936 

22.622 

7439954 

#N/A 

MIA 

#N/A

Table 6.4 (continued) Toxicological benchmnrh for screening conemirunts of potential concern 

for effects on nildlife' 

Madm White-footed Short-tailed 

Contaminant CAS ID vole^ Mouae' shrrn' 

Q 

(mgkz-d) 

Mang8tlCSC 7439965 174.456 219.293 248.837 

Macury 7439976 0.013 0.016 0.018 

Nickel 7440020 79.298 99.679 113.108 

Potassium 7440097 MIA MIA MIA 

Selenium 7782492 0.066 0.083 0.094 

Silver 7440224 MIA #NlA #NIA 

SOdiUm 7440235 MIA MIA #NIA 

Thallium 7440280 0.015 . 0.019 0.021 

VaMdium 7440622 0.377 0.474 0.538 

Zinc 7440666 317.192 398.715 452.43 

1 = All benchrmuks e- from PC-Data Bsse: Smening benchnuuks for ecological risk .ssessnnd 

Revised Decemba 1994. Environmental Scimces Division & Health Sciences Rarearch Division, 

Oak Ridge National Laborrtory. 

2 = Value rrprcsad No Observed Advaac Effects Levels (NOAELP). 

#NA = Benchmark not available.

Table 6.5. Bioaccumulation factors 

Soil to Plant 

Plant-to-Meat 

Earthworm to 

BTF (wet wt.) BTF (wet wt.) Predator BTF (wet wt.) for Aquatic 

COPC CASNumbcr Kor [m] (daydig) Soum (days&) Source (day%)' Orgnnisnis' 

Aluminum 7429905 6.00E-04 [fl I.5OE-03 [i] 5.44842 I 4 na 

Antimony 

Arsenic 

Barium 

Beryllium 

CdTlium 

Calcium 

chromium VI 

Cobalt 

I4 

I 4 

I 4 

Id 

na 

COP 

If on 

Lead 

Magnesium 

Mangange 

Maw 

Nickel 

Potsssium 

Selenium 

Silver 

Sodium 

Thallium 

Tin 

Vanadium 

Zinc 

AcenaphthmC 


Acetone 

Anlhrscene 

Aroclor 1260 

Bm(a)anthracene 

Benzene 

Bcluo(a)pyrmc. 3,4- 

Bcmo(b)flmthene 

Bmo(g,h,i)pcrylcnc 

Benzo(k)flomanthme 

Bis(2-cthylh~l)atc 

chloroform 

7440360 

7440382 

7440393 

7440417 

7440439 

7440702 

18540299 

7440484 

7440508 

74398% 

7439921 

7786303 

7439965 

7439976 

7440020 

7447407 

7782492 

7440224 

7440235 

7440280 

74403 1 5 

7440622 

7440666 

208968 

208968 

67641 

120127 

11096825 

56553 

71432 

50328 

205992 

191242 

207089 

117817 

67663 

* 

* 

1.00E+04 

5 .O 1 E+03 

5.80E-0 I 

2.82E+04 

1.41E+07 

3.98E+05 

1.328+02 

l.l5E+06 

l.l5E+06 


1.15E+06 


9.33E+01 

fi] 

5.04E-05 

6.00E-03 

1 .OOE-02 

1.5OE-03 

8.25E-02 

5.25E-02 

3.75E-05 

5.408-03 

1.80E-02 


2.09E-04 

8.25842 

6.80E-02 

3.00E-01 

1.80E-02 

3.00E-01 

I .00E-01 

2.25E-02 

7.50E-03 

6.00E-05 

3.00E-01 

8.25E-04 

9.90E-02 

2.83E-02 


7.%E+OO 

1.56E-02 


3.37E-03 

3.45E-01 

1.82E-03 

1.82E-03 

8.87E-04 

1.82E-03 

2.57E4-00 



2.00E-03 

1.30E-05 

1.00E-03 


2.00E-03 

9.00E-03 

1.00E-04 

9.00E-03 

2.00E-02 


2.OOE-02 

5.00E-04 

1.00E-02 

5.208-03 

1.80E-02 

1.00E-01 

3.00E-03 

8.00E-02 


1 .OOE-02 

2.50E-03 

l.OOE-01 

2.51E-04 

I .26E-04 

1.46E-08 

7.08E-04 

3.5 4E-0 1 

I .OOE-02 

3.32E-06 

2.89E-02 

2.89E-02 

1.00E-01 

2.89842 

1.03E-07 

2.34E-06 

na 

1.46E-0 1 

3.768-02 

na 

7.36E-0 1 

na 

7.84E-02 

na 

8.32E-02 

6.OSE-02 

7.208-02 

8.48E-02 

6.40E-02 

1.54E-01 

6.568-02 

NI 

na 

na 

na 

na 

na 

na 

na 




5.12E-02 




5.44842 

3.36E-02 

2.40E-02 

3.36E-02 



BAF 

1.00E+00 

2.80E+02 


2.00E+00 

5.00E+01 

2.00E+02 

3.00E+02 

I 4 2.10E+02 

I 4 1 .OOE+O2 

14 3.00E+02 

I 4 

na 

I 4 4.00E+02 

I4 6.30E+04 

I 4 I .00E+02 

na 

8.00E+00 

2.00E+00 

1.00E+02 

1.00E+04 

na 

1.00E-02 

1.00E+03 

14 3.90E+02 

IYI na 

IYl 2.00E-01 

Izl na 

IYl 

na 

I 4 

na 

IYI 

na 

I 4 3.00E+01 

I 4 

na 

14 na 

I4 

na 

IYI 3. I OE+O2 

IY 1 6.00E+00

Table 6.5. Bioaccumulation factors (continued) 

Soil to Plant Plant-to-Meat Earthworm to BAF 

BTF (wet wt.) BTF (wet wt.) Predator BTF (wet wt.) for Aquatic 

COPC CASNumber Kow [ml (days&) Source (daydig) Source (day%)* Organisnisi 

chrysenc 218019 4.07E+05 3.32E-03 [a] 1.02E-02 [a] 7.04E-02 I4 na 

Dibcnzo(a, h)anhccne 53703 4.07E+05 3.328-03 [a] 1.02E-02 [a] 7.848-02 I4 na 

Dibenzofinnn I32649 1.30E+04 ti] 2.438-02 [a] 3.278-04 [a] 4.85E-02 [Y I na 

Dibutylphthalate 84742 4.00E+05 3.36843 [a] l.OOE-02 [a] 4.85E-02 [YI na 

Dichlmthanc, 1,l- 75343 6.17E+OI 5.36E-01 [a] 1.55E-06 [a] 4.85E-02 [YI na 

Dichloroethylene. 1.1- 75354 6.92EMl 5.02E-01 [a] 1.748-06 [a] 4.85E-02 [YI 7.00E+00 

Dichloroethylmc. I.2.C- 540590 7.90E+01 4.65E-01 [a] 1.988-06 [a1 4.85E-02 [YI 7.00E+00 

Dichlmthylmc. 1.2,T- 156605 3.02E+OO 3.07EMO [a] 7.598-08 lal 4.85E-02 IYI 7.00E+00 

Fluoranthcne 206440 7.94E+04 8.55E-03 [a] 1.99E-03 Ial 5.928-02 [zl na 

Fluorene 86737 1.58E+04 2.17E-02 [a] 

3.97E-04 [a] 3.20E-02 [Zl na 

Indcno(l,2,3-CD)pyrene 193395 3.16E+06 1.02E-03 [a] 7.94E-02 lal 6.56842 I4 na 

Methylnaphthalene 91576 7.24E+03 3.418-02 [a] 1.82844 [a) 3.20E-02 14 na 

Naphthalene 91203 1.70E+03 7.89E-02 [a] 4.27E-05 1.1 3.36E-02 I4 4.30E+02 

Phenanthrene 85018 2.888+04 1.54E-02 [a] 7.238-04 Ial 4.48842 14 na 

129000 2.098+05 4.89E-03 [a] 5.25E-03 la1 6.24E-02 14 na 

Toluene 108883 5.37EM2 1.54E-01 [a] 1.35E-05 1.1 4.858-02 IYl 8.30E+01 

Trichlmthylcnc 79016 2.40Ei-02 2.45E-01 [a] 6.03E-06 [a] 4.858-02 lYl 1.70E+01 

Xylcna (mixcd) 108383 1.82E+03 7.58E-02 [a] 4.57E-05 Ial 2.88E-01 I4 3.208+02 

[a) Trnvia and Arms (1988). Plant BTF dcrivcd 6m regrauion quation: log(BTF) = 1.588-0.578 log(Kow) and 

Converted to a wet weight bash .Mrming planta arc 85% water (USEPA 1993). Plant-to-meat BTF dcrivcd h 

regression equation: log(BTF) = log(Kow) - 7.6. 

[b] IAEA (1993). Original dish BTF converted to a wet weight basis assuming radish WM 91% water (IAEA 1993). 

[c] IAEA (1993). Plant type WM unspecified in IAEA (1993). Convcded BTF to wet weight basir assming plantr arc 

85% water (USEPA 1993). 

[dl IAEA (1993). Original grass BTF converted to a wet weight basis assuming gram is 90% walcr (IAEA 1993). 

[el NCRP (1989). 

[fl Baa et a!. (1984). Plant type wat unspecified in Baa et al.. Converted BTF to wet weight batis assuming plants. 

arc 85% wata (USEPA 1993). 

[g] IAEA (1993) value reported for plant-to-goat. 

[h] IAEA (1993) value reported for Pl~t-to-bC~f. 

[i] Baa et al. (1984) value rcportcd for plant-to-bccf. 

ti] Kow obtained 6om SupCmnd Chcmicd Data Uatrix (1993). 

[k] Kow obtained h Montgomery and Welkom (1990).

Table 6.5. Bioaccumulation factors (continued) 

[I] IAEA (1993). Original fodder BTF convetted to a wet weight basis assuming fodder WM 81% water (IAEA 1993). 

[m] Kow - Chemical specific octanol-water patition cocfiicimt obtained from chcmlib.dat, MEPAS 1/26/95. 

na = not available 

= not applicable 

[z] - Extracted from Beyer & Stafford (1993). Converted to wet weight basis assuming 84% water wnlcnt for earthworm (Sample & Sutcr, 1994). 

1 = Bamrhousc etd. 1988

Table 6.6. Species-specific exposure parameters for wildlife' 

Receptor Body Dietary Water Fraction Fraction Fraction 

Species Weight Ingestion Rate Ingestion Rate Soil Invertebrate Plant 

(kn) Wd) Wd) 

Meadow Vole 0.044 0.005 0.006 0.024 0 0.976 

Short-tailed Shrew 0.015 0.009 0.0033 0.13 0.87 0 

White-footed Mouse 0.022 0.0034 0.0066 0.01 0.49 0.5 

Belted Kingfisher 0.148 0.075 0.016 0 0 0 

a = Values extracted from Opresko et. al. 1995 (Revision). Toxicological Benchmarks for Wildlife. 

Risk Assessment Program. Lockheed-Martm Energy Systems, Inc. ES/ER/IhI-86/R2.

Table 6.7. Ecological hazard quotients for surface water-associated in the northhouth ditch psrallel to 4th street at PGDP, WAG 1, Fire Training Area (SWMU 100) 

Representative Eatinatd Eatimatd Eatinated LCV Ir Scndtive 

Commtntion LCV" LCVtC EC,& Aquatic LCV''. LCV'" EC," Specin Tnt Population Secondary Secondary NAWQC'" NAWQC"' 

Cbedcal (mJL) Daphnida Fiah nab Planla Daphnids Flsb Imvertebrata Daphnida EC," EC," Acute V~lua' Chronic Valun Acute Chronic 

Aluminum I22E+OI - 265E-02 6428-03 371E-03 

2 268-02 I 638-01 

Brium 116E-01 ZOOE-05 - I 68E-03 3 OSE-02 

1638-02 14OE-01 

Cdmium 1338-02 - 665E-03 887E-02 7828-03 1778-02 l.OZE+OO 309E-03 3 4lE-03 I21E-02 

Cddum 4 IOE+OI - 3S3E-04 - 

Chromium 6 09E-02 - 305E-02 993E-03 832E-04 122E-01 2298-01 I93E-04 3 81E-03 5 54E-03 

cobslt 3 208-03 - 627E-04 I IOE-05 7 27E-04 804804 1648-05 I OSE-03 

Copper 6 87EM - 687E-02 2998-01 I8lEM I13E-02 33SE-01 ZME-OI 7998-03 3 82E-03 5 738-03 

lrOn I34E+Ol - 848EM 103E-02 8 388-01 I 348-02 

tad I 568-02 - 3 128-05 1278-03 826E-04 613E-04 4 468-02 2 20E-04 I90E-04 4888-03 

Magnesium 5 17E+00 - 6308-05 

2 73E41 - 248E-04 I54E-04 2 48E-04 2448-03 1868-04 3 40E-03 

Nickel 1668-02 - 3328-03 3328-03 474E-04 I29E-04 3698-04 1518-03 7728-05 

Potauium 2 37E+00 - 4478-05 

Sodium 102E+OI I50E-05 - 

Vanadium I98E-02 - 2 IiE-05 248804 4 60E-05 6 19E-04 6 978-05 I 04E-03 

Zinc I44E-01 - 480E-03 308E-03 395E-03 275E-05 686E-03 I 80E-03 I 20E-03 I 3 I E-03 

Hazard Index IME-05 - I40E-01 4 98E-01 464EM I21E-02 1.34E+W l.'lSE+W I 728-02 I95E-03 3 60E-02 I 248-02 4 30E-02 

I - LCV -Lowest Chronic Vdw 

2 - Et? - Effective Concmtnh 'on that a reduction of 20% of the pwih pmduction occurs 

3 - NAWQC -National Ambient WUer Quality Critma 

a All toxicity values were extracted &om'PC-Data Base Screening Benchmarks for Ecological Risk Assessment (revised December 1994)' 

Environmental Sciences Division. Hdth Sciences Rerearch Division, ORNL 

Huard Quotients M unitlnr 

- - no( able to quantify because tnnsfn factor or toxicological benchmark was unavailable 

Bold Vdue indicates hazard quotient OT huvd index is veater than I 

I 19E-05 

I04E-04

~ ~~ - 

Table 6.8. Ecological baurd quotients for surface water-associated in the castlwcst ditch parallel to railroad tracks which intersect 4th street at PGDP, WAG I, Fire Training Area (SWMU 100) 

RcprntaUve Estimated Estimated Estimated LCV la Sensitive 

' 

CMcatmtion LO''* ECn- Aq.atlc LCV'" LCV"' LCV'* ECnL Spccia Tat Population Secondary Secondary NAWQC '" NAWQC'" 

Cbcmlc.l (mJL) Dapbnids Fib Flsb PIanb Dapbnids FM Iaverlebrata Dapbnlds ECnb ECna' Acute Vaiua. Cbronic Valua Acute Chronic 

Aluminum 

3 8IEiOO 

- 8.28E-03 20iE-03 I16E-03 

7068-03 508E-02 

5 OBE-03 4 388-02 

Anmic 

Barium 

I40E-03 

1378-01 2 36E-05 

1988-03 3 61 E-02 

Calcium 

Chromium 

5 98E+Oi 

8 8OE-03 

4 40E-03 

5 16E-04 

I44E-03 I2OEM 

I 768-02 3 3 I E-02 2 788-05 

5 SOE-04 8 WE-04 

COPW 

6 20E-03 

6 20E-03 2 70E-02 I 631-03 I OZE-03 3 02E-02 2 388-02 721864 

3 448-04 5 17E-04 

Iron 

4 MEiOO 

2 56E-02 3 I IE-03 

2 S3E-01 

4 04E-03 

Lud 

2 7lE-02 

5 42E-05 2 21E-03 I 44E-03 I06E-03 

7 748-02 3 828-04 

3 30E-04 8 478-03 

Magnesium 

I34E+OI 

163E-04 

M ~ g m 2 58E-01 

235EM I46EM 

23SE-00 

2 30E-03 I 76E-M 3 21E-03 

Potassium 

2 92EiOO 

5 5IE-05 

Sodium 

2 5OE+01 3 68E-05 

Vanadium 

4 20E-03 

4 478-06 5 25E-05 

9 778-06 

I31E-04 I48E-05 2 20E-M 

Zinc 

2 68EM 

8 93EM 574EM 7368-04 5 ilE-06 I 28E-03 3 35E-04 2238-04 2448-04 

Huurd Index 6 ME45 I 158-02 5 77E-02 7 238-03 2 09E-03 3 OIE-01 I 36E-01 3 90E-03 2 17E-03 3 958-02 I 4SE-03 I 41E-02 

I LCV la~nr 

Chronic Value 

2 - EC? - EfTcctive Concmtrmiim tha a reduction of 20% of the vow& production occurs 

3 - NAWQC - National Ambient Wder Quality Criteria 

a All toxicity dun were d htn 'PC-Dam Bue Screening Benchmarks for Ecological Risk Aueummt (revid Decemba 1994)' 

Environmental Sciences Division. Health Scienm Ruuch Divirim, ORNL 

* H d pwCienb re unitlm 

- - no( hie to quantify kuur transfer factor or toxicological bmchmark wu unavailable 

Bold Value indiatn haud quotient or h d index is pats thur I

Table 6.9. Ecological hazard quotients for sediment-associated in the northhouth ditch parallel to 4th street 

at PGDP, WAG 1, Fire Training Area (SWMU 100) 

Representative 

Concentration EKects EKects EPA 

Cht mica1 (mg/kg) Range Low Range Medium OMOE ” EPA ’*’ Region V H&S ’’ WIDNR ‘,’ 

Aluminum 

Arsenic 

Barium 

Beryllium 

Calcium 

Chromium 

Cobalt 

Copper 

Iron 

Lead 

Magnesium 

Manganese 

Nickel 

Potassium 

Selenium 

Sodium 

Vanadium 

Zinc 

Acetone 

bis~2-Ethvlhexvl~ohthala~ 

I .23E+04 

5.70E+00 

2.74E+02 

8.30E-01 

1.31E+04 

1.94E+O I 

I .64E+OI 

1.66E+01 

2.478+04 

I. I5E+OI 

2.348+03 

1.758+03 

I .47E+OI 

9.908+02 

1.60E-01 

I .35E+02 

3.94E+01 

I .63E+02 

1.90E-01 

I .30E-01 

6.958-01 

2.40E-01 


2.468-01 

7.00E-01 

1.09E+00 

8.14E-02 

5.248-02 

6.158-02 

5.288-02 

2.858-01 

3.988-01 

9.50E-0 1 

7.468-01 

3.80E+00 

1.45E+00 

2.97E+00 

I .46E-07 

5.488-01 

Hazard Index 3.46E+00 9.3 1E-01 S.SOE+OO 1.45E+00 2.97E+00 5.48E-01 





a = All toxicity values were extracted from ”PC-Data Base: Screening Benchmarks for Ecological Risk Assessment (revised December 1994)” 


= Hazard Quotients arc unitless 

- = not able to quantify because transfer factor or toxicological benchmark was unavailable 

Bold Value indicates hazard quotient or hazard index is greater than 1.

Table 6.10. Ecological hazard quotients for sediment-associated organisms in the east ditch parallel to railroad tracks 

which intersect 4th street at PGDP, WAG 1, Fire Training Area (SWMU 100) 

Representativc 

Concentration EKects EKects EPA &' 

Chemical (mgkg) Range Low Range Medium OMOE '' EPA **' Region V H&S WIDNR '*' 

Aluminum 9.588+03 

Arsenic 5.20E+00 6.348-01 7.438-02 8.67E-01 

Barium 

Beryllium 

Calcium 

Chromium 

Cobalt 

1.01 E+02 

6.40E-01 

2.06E+03 

3.00E+OI 

8.308+00 

3.70E-01 8.1 IE-02 l.lSE+OO 

Copper 

Iron 

Lead 

Magnesium 

Manganese 

Nickel 

1.04E+01 3.06E-01 3.858-02 

I .69E+04 9.948-01 

I .01 E+OI 2.16E-01 4.638-02 

1.448+03 

7.14E+02 

1.55E+00 

I.OIE+OI 4.81E-01 I .96E-01 

Potassium 5.638+02 

Selenium 

2.00E-01 

Sodium 

I .26E+02 

Vanadium 

2.46E+Ol 

Zinc 3.898+01 2.598-01 9.498-02 

Acetone 3.808-02 5.94E-01 

2.02E-0 1 

Hazard Index 2.27E+00 5.3 IE-01 3.57E+00 9.94E-01 5.948-01 2.02E-01 





a = All toxicity values wen extracted from "E-Data Base: Screening Benchmarks for Ecological Risk Assessment (revised December 1994)" 


= Hazard Quotients are unitless 

- - not able to quantify because transfer factor or toxicological benchmark was unavailable 

Bold Value indicates hazard quotient or hazard index is gnatcr than I.

Table 6.1 1 Ecological hazard quotients for plants, soil microbes, and earthworms associated 

with surface soil at PGDP, WAG 1, Fire Training Area (SWMU 100) 

Rcprcscnta tivc 

Concen tration 

Soil 

Chcmical (mg/lrL!) Plants Microbes Earthworms 

Aluminum 

Ammonia as Nitrogen 

Antimony 

Arsenic 

Barium 

Beryllium 

Cadmium 

Calcium 

Chromium 

Cobalt 

Copper 

Cyanide 

Iron 

Lead 

Magnesium 

Manganese 

Mercury 

Nickel 

Potassium 

Selenium 

Sodium 

Vanadium 

Zinc 

8.39E+03 

7.90E+00 

I .39E+00 

5.638+00 

1.03E+02 

4.348-01 

I .5 I E-01 

7.22E+04 

I. 10E+OI 

6.548+00 

8.7 I E+OO 

3.20E-01 

I .27E+04 

1.74E+01 

1.64E+03 

7.408+02 

1.33E-01 

8. I7E+00 



1.54E+02 

2.36E+OI 

2.89E+O I 

236E+02 

3.40E-01 

9.50E-01 

3.12E-01 

S.00E-02 

1.13E-01 

1.54E+01 

5.60E-0 I 

9.60E-02 

7.58E-01 

2.24E+00 

8.678-0 I 

3.80E-01 

6.60E-0 I 

1.59E+01 

7.948-01 

1.97E+01 

9.50E-02 

5.208-02 

I .70E-02 

1.54E+00 

I.12E-02 

9.608-02 

7.80E+01 

4.2 I E62 

1.12E+01 

8.67843 

I .27E-01 

6.608-03 

1.59E+00 

3.97E-01 

1.58E-01 

I .70E-02 

3.85E+01 

I .92E-01 

7.588-02 

2.60E+00 

5.70E-02 

9.43E-03 

1.99E-01 


Acetone 


Toluene 

8.10E-02 

3.20E-02 

2.1 BE-01 

1.00E-03 

2.55E-03 

5.00E-06 

Xylene 

3.00E-03 

Hazard Index 2.75E+O2 1.13E+02 4.18E+01 

a = All toxicity values were extracted fiom "PC-Data Base: Screening Benchmarks for Ecological Risk Assessment (revised December 1994)" 



- = not able to quanti@ because transfer factor or toxicological benchmark wm unavailable 


Table 6.12 Ecological bazard quotients for wildlife receptors associated with surface soil at 

PGDP, WAG 1, Fire Training Area (SWMU 100) 

Rcprcsentattvc Meadow Vole ' White-footed Mouse ' Short-tailed Shrew ' 

Conccntratlon DaUyIntnke MMEL' Hwrd DnUyIntPkc NOAEL' H w d DdyIntnkr NOAELb H~znrd 


Antimony 

7.90E+00 

1.39E+00 

#N/A 

3.80E-03 

#N/A 

l.lOE-O1 3.45E-02 

#N/A 

2.15E-03 

Arsenic 

5.63E+00 1.91E-02 l.llE-01 1.72E-01 7.34E-02 

Barium 

1.03E+02 3.95E-01 1.08E+01 3.6733-02 6.88E-01 

&rytlium 

4.34E-01 1.26E-03 1.31E+00 9.60E-04 7.2 1E-04 

Cadmium 

1.51E-Ol 1.798-03 1.69E-01 1.06E-02 9.61E-03 

Calcium 

Chium 

7.228+04 

l.IOE+Ol 

#N/A 

3.00E-02 

#N/A 

6.50E+00 4.62843 

#N/A 

8.23E-02 

Cobalt 

copper 

6.54E+00 

8.71 E+OO 

2.18E-02 


#N/A 

3.28E+01 1.25E-03 

1.28E-02 

8.05E-02 

cyanids 

3.20E-01 2.89E-0 I 1.25E+01 2.30E-02 2.02E-01 

Iron 

Lead 

I .27E+04 

1.74E+01 

#N/A 


#N/A 

1.59E+01 3.02E-03 

#NIA 

1.22E-01 

Magnesium 

Manganese 

I .64E+03 

7.40E+02 

#NIA 

7.60E+00 

#N/A 


#NlA 

8.62E+00 

Mercury 

1.33E-01 

4.79E-03 1.30E-02 3.68E-01 4.84E-03 

Nickel 

8.17EMO 3.86842 7.93E+01 4.87E-04 6.468-02 

Potassium 

Selenium 


4.67E-O 1 

#N/A 

6.45E-03 

#N/A 

6.60E-02 9.78E-02 

#N/A 


Sodium 

Vanadium 

1.54E+02 

2.368+01 

5.48E-01 

6.658-02 

#NIA 

3.77E-01 1.76E-01 

3.27E-01 

3.80E-02 

Zinc 

2.89E+OI 3.96841 3.17E+02 1.25E-03 2.66E-01 

3-Nitromilinc 

Acetone 

8.10E-02 

3.20E-02 

#N/A 

2.83E-02 

#N/A 

1.98E+O1 1.43E-03 

#N/A 

1.98E-02 

Di-n-but ylphthalate 

2.18E-01 6.763-04 4.85E+02 1.39E-06 1.19E-03 

Toluene 

I .00E-03 1.98E-05 2.29E+OI 8.63E-07 1.71E-05 

Xylene 3.00E-03 #N/A 1.82E+00 #N/A 

#N/A 

1.38E-01 3.568-02 

1.40E-01 5.24E-01 

1.35E+01 5.08E-02 


2.12E-01 4.53842 

#N/A 

8.17E+00 1.01E-02 

#N/A 

4.13E+O 1 1.95E-03 

1.58E+Ol 1.28E-02 

#N/A 

1.99E+01 6.12E-03 

#N/A 

2.19E+02 3.93E-02 

1.60E-02 3.02E-01 

9.97E+01 6.48844 

#N/A 

8.30E-02 5.22E-02 

#N/A 

4.74E-0 1 8.01 E-02 

3.99E+02 6.67E-04 

#N/A 

2.49E+01 7.96E-04 

6.09E+02 1.968-06 

2.88E+OI 5.93E-07 

2.28E+00 

#N/A 

1.08E-01 

8.678-01 

1. I lE+O 1 

3.39E-02 

6.988-02 

#N/A 

I .31 E+OO 

5.1 OE-01 

1.06E+00 

3.31E-02 

#N/A 

2.0 I E+OO 

#N/A 

8.24E+01 

2.10E-02 

9.17E-0 1 

#N/A 

3.64842 

1.20E+01 

1.84E+00 

2.25E+00 

#N/A 

3.31E-03 

2.25E-02 

1.03E-04 

#N/A 

#N/A 

1.57E-01 

1 S8E-0 1 

1.54E+01 

1.87E+00 

2.40E-01 

#NIA 

9.28E+00 

#N/A 


1.79E+O I 

#N/A 

2.26E+01 

#N/A 

2.498+02 

1.80E-02 

1.13E+02 

#N/A 

9.40E-02 

#NIA 

5.38E-01 


#N/A 

#N/A 

6.91 E+O2 

3.27E+01 

2.59E+00 

6.91E-01 

5.49E+OO 

7.24E-0 I 

1.8 1E-02 

2.9 1 E-0 1 

1.4 1E-0 1 

2.26E-02 

3.85E-03 

8.89E-02 

3.3 1 E-0 1 

l.l7E+OO 

8.11E-03 

3.88E-01 

3.42E+OO 


3.26E-05 

3.16E-06 

Hazard Index 1.44E+O1 2.30E+01 3.72E+02 

a = All toxicity vduu were eldraded from "PC-Data Base: Scmning Bench& for Ecological Risk Assessment (revised December 1994)" 


b = NOAEL - NO Advn~e Ef' Level 


- = not able to quantify because transfa factor or to~wlogical benchmark was unavailable 

Bold Value indicatu hazard quotient or hazard index is greater than 1.

Table 6.13. Ecological hazard quotients for plants, soil, and earthworms associated 

with surface soil at PGDP, WAG 7, Underground Storage Tanks (SWMU132) 


Concentration 

Soil 

Chemical (me/kel Plants a Microbes Earthworms 

Lead 1.38E+02 2.76M00 1.53E-01 2.768-0 1 

Di-n-butylphthalate 3.30E-01 1.65E-03 

bis(2-Ethy lhexy l)phthalate 

m,p-Xylenes 

0-Xylene 

2.30E-01 

3.00E-03 

2.00E-03 

Hazard Index 2.76&+00 1.53E-01 2.76E-0 1 

a = All toxicity values wen extracted fiom “PC-Data Base: Screening Benchmarks for Ecological Risk Assessment (revised December 1994)” 

Environmental Sciences Division. Health Sciences Research Division, ORNL 

* = Hazard Quotients arc unitless 



Table 6.14. Ecological hazard quotients for wildlife receptors associated with surface soil at 

PGDP, WAG 7, Underground Storage Tanks (SWMU132) 

Repmenhtkc Meadow Vole a White-footed Mouse Short-hUed S hm 

Concentration DdyInWrc NOAEL‘ Hsvrd DnilyIn@ke NOAEL’ Hazard Dallylntake NOAEL’ Hazard 

chemled (msny) (mrW (mgW Quotients (mg/Lb) (wflts) Quotients (mgkg) (nigh) Quotients 

Lead 1.38Ea2 3.80E-01 1.59E+01 2.39E-02 9.68E-01 1.99E+OI 4.86E-02 1.60E+01 2.26E+Ol 7.OSE-01 

Di-n-butylphthalate 3.30E-01 1.02E-03 4.8SE+02 2.11E-06 1.81E-03 6.09E+02 2.97E-06 3.418-02 6.91E+02 4.93E-05 

bis(2-Ethylhexyl)ate 2.30E-01 6.628-02 1.62E+01 4.10E-03 4.69E-02 2.03E+OI 2.3 1 E-03 2.38E-02 2.30E+01 1.03E-03 

nsPxYlmes 3.00E-03 3.34E-05 #NIA 8.76E-05 #N/A 6.8SE-04 #N/A 

0-Xylene 2.00E-03 #NIA #N/A #N/A #N/A #N/A #N/A 

Hazard lndex 2.80E-02 S.09E-02 7.06E-01 

a = All toxicity values wen extracted !?om“PC-Data Base: Screening hchmarks for Ecological Risk Assessment (revised December 1994)” 

Emironmental Sciences Division, Health Scimces Research Division, ORNL 

b = NOAEL -NO Advmc E5& Level 

= Hazard Quotimds are unitlas 

#N/A 01 - = not able to quanti@ because truufa factor or toxicological benchmark was unavailable

Table 6.15. Ecological hazard quotients for plants, soil microbes, and earthworms associated 

with surface soil at PGDP, WAG 7, Undergound Storage Tanks (SWMU 133) 


Concentration 

Chemical (mg/kg) Plrnb Microbes ’ Earthworms ’ 



Lead 

Acenaphthene 

Accnaphthylenc 

Anthracene 

Benzo(a)anthraccnc 

Benzo(a)p yrenc 

Bcnzo(b)fluoranthenc 


Benzo(k)fluoranthenc 

Carbazole 

Chrysenc 


Dibenzo(qh)anthracenc 

Fluoranthene 

Fluorene 

Indene( 1.2f-cd)pyrene 

Phenanthrene 

Pyrene 

bis(2-Ethyl hexy1)phthalate 

1.628+02 

3.00E-01 

6.60E-01 

9.00E-0 I 

5.20E+00 

3.90E+00 


2.30E+00 

3.50E+00 

3 .OOE-01 

6.20E+00 

I .60E-0I 

2.50E-01 

8.50E+00 

2.30E-01 

1.90E+00 


9.40E+00 

2.10E-01 

334E+00 

8.00E-04 

Soil 

I .80E-01 3.24841 

7.67E-03 

Hazard Index 3.24E+00 I .80E-01 3.32E-01 

a = All toxicity values were extracted from “PC-Data Base: Screening Benchmarks for Ecological Risk Assessment (revised December 1994)” 

Environmental Sciences Division, Health Sciences Research Division, ORNL. 

* =Hazard Quotients arc unitless 



Table 6.16. Ecological hazard quotients for wildlife receptors associated with surface soil at 

PGDP, WAG 7, Undergound Storage Tanks (SWMU 133) 

Rcpmcntativc Meadow Vole ’ Whltc-footed Mouse Short-tailed Shrew ‘ 

Conccntrntlon DaUy Intake NOAEL ’ H.zPrd DaUy Intake NOAEL ’ Hazard Daily lntnke NOAEL’ Hazard 

ChrmlCd (mgnc6) (mrk) (mgnc6) Quotients (m&) (mEkg) Quotients (Wnc6) (mgkg) Quotients 

4.1 OE+OO 

1.62E+02 

3.00E-01 

6.60E-01 

9.00E-01 

5.20E+00 

3.90E+00 


2.30E+00 

3.50E+00 

3.00E-0 I 

6.20E+00 

1.60E-O 1 

2.50E-01 

8.50EdO 

2.30E-01 

1.90E+00 


9.40E+00 

#N/A 


#N/A 

3.87E-03 

4.01 E-03 

1.61E-02 

1.14E-02 

1.23E-02 

6.50E-03 

1.03E-02 

#N/A 

1.92E-02 


7.74E-04 

3.12342 

1. I8E-03 

5.40E-03 

2.08E-02 

3.07E-02 

#N/A 

1.59E+Ol 

#N/A 

#N/A 

#N/A 

#N/A 

8.81 E-0 1 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 


#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

2.81E-02 

1.30E-02 

1.02E-06 

#N/A 

1.14E+00 

#N/A 


5.96E-03 

2.64E-02 

2.26E-02 

1.788-02 

7.89E-03 

1.48E-02 

#N/A 


8.76E-04 

1.93E-03 

5.69E-02 

1.30E-03 

1.2SE-02 

2.88842 

6.25E-02 

#N/A 

1.99E+Ol 

#N/A 

#N/A 

#N/A 

#N/A 

l.llE+OO 

#N/A 

#N/A 

#N/A 

#N/A 

#NIA 

6.09E+02 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

5.70E-02 

2.04E-02 

1.44E-06 

.- 

#N/A 

1.87E+01 

#N/A 

6.80E-02 

9.43E-02 

5.23E-01 


4.01 E-01 

2.08E-01 

3.34E-01 

#N/A 

7.11E-01 

1.6SE-02 

2.97E-02 

9.26E-01 

2.18E-02 

2.13E-01 

4.778-0 I 

1.04E+00 

#N/A 

2.26E+01 

#N/A 

#N/A 

#N/A 

#N/A 

1.26E+00 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

6.91E+02 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

8.28E-01 

3.30E-01 

2.39E-OS 

bis(2-Ethylhexyl)phihdats 2.10E-01 6.04E-02 1.62E+01 3.74E-03 4.28E-02 2.03E+01 2.11E-03 2.17E-02 2.30E+01 9.42E-04 

Hazard Index 4.48E-02 7.9SE-02 1.16E+00 

a = All toxicity values were extracted fiom “PC-Data Base: Screening Benchmarks for Ecological Risk Assessment (revised December 1994)” 

Environmental Sciemxs Division, Health Sciences R*learch Division, ORNL 

b = NOAEL - NO Adverse E ffd Level 

= Hazard Quotients arc ~ Ntles~ 

#N/A or - = not able to quantify because transfer factor or toxicological benchmark was unavailable 

Bold Value indicates hazard quotient or hazard index is pter than 1.

Table 6.17; Ecological hazard quotients for plants, soil microbes, and earthworms associated 

with surface soil at PGDP, WAG 7, Underground Storage Tanks (SWMU 134) 


Concentration 

Chemical (mgkg) Plants a Microbes Earthworms 

Lead 1.50EMI 3.00E-01 1.67E-02 3.00E-02 

Benzo(a)anthracenc 

1.40E-01 

Benzo(a)pynne 

1.40E-01 

Bcnzo(b)fluoranthenc 

2.1 OE-0 I 

Bcnzo(g,h,i)pcrylene 7.208-02 

Bcnzo(k)fluoranthene 

Carbazole 

7.90E-02 

1. I OE-0 I 

Chrysene 

1.70E-01 

Di-n-buty lphthalate 5.50E-01 2.758-03 

Fluoranthenc 


Indeno( I ,2,3-cd)pynnc 7.908-02 

Phenanthnne 

2.60E-0 I 

Pynnc 3.30E-01 

Soil 

Hazard Index 3.03E-01 1.678-02 3.00E-02 

a = All toxicity values wen extracted from "PC-Data Base: Screening Benchmarks for Ecological Risk Assessment (revised December 1994)" 

Environmental Sciences Division, Health Sciences Research- Division, ORNL 


- = not able to quantify because transfer factor or toxicological benchmark was unavailable


PGDP, WAG 7, Underground Storage Tanks (SWMU 134) 

Repnsentative Meadow Vole ' White-footed Mouse ' Short-Med S hm ' 

Concentration DnUy Intake NOAEL' Hazard DPUy Intake NOAEL ' Hazard DailyIntake NOAEL' Hazard 

Chemled (wk) mny) (m&) Quotients (ww (mgkg) Quotients (W/kg) (mg/kg) Quotients 

Lead 1.50EMI 4.13E-02 1.59EM1 2.60E-03 1 .OSE-Ol 1.99E+01 5.28E-03 1.73E+00 2.26E+01 

Bmzo(a)anthracene 

ho(a)Wrme 

Bmzo(b)fluoranthene 

&nzo(g,h.i)perylene 

Bcnzo(k)fluoranthms 

Carbazole 

chryrme 


Fluoranthene 

Indmo(l,2J-cd)pyrene 

Phmuahrens 

1.40E-01 

1.40E-01 

2.1 OE-0 I 

7.20E-02 

7.90E-02 

l.lOE-O1 

1.70E-0 I 

5.5OE-01 


7.90E-02 

2.60E-0 I 



6.15E-04 

2.03E-04 

2.31E-04 

#NIA 

5.26E-04 

1.70E-03 

1.65E-03 

2.24E-04 

1.15E-03 

#N/A 

8.8 I E4 1 

#N/A 

#NIA 

#N/A 

#N/A 

#N/A 

4.85EM2 

#NIA 

#N/A 

#N/A 


3.52E-06 

7.11 E-04 

8.13344 

8.88E-04 

2.47E-04 

3.348-04 

#N/A 

I .2lE-03 

3.01 E-03 

3.01E-03 

5.21E-04 

1.59E-03 

#N/A 

I.llE+OO 

#N/A 

#N/A 

#N/A 

#N/A 

#NIA 

6.098+02 

#NIA 

#NIA 

#N/A 

7.34E-04 


1.41E-02 

1.49E-02 

2.01E-02 

6.52E-03 

7.55 E-03 

#N/A 

1.95E-02 

5.68E-02 


8.878-03 

2.64E-02 

#NIA 

1.26E+00 

#N/A 

#N/A 

#N/A 

#N/A 

#N/A 

6.91E+02 

#N/A 

#N/A 

#NIA 

4?ene 

3.30E-01 1.08E-03 #N/A 2.19E-03 #N/A 3.65E-02 #N/A 

Hazard Index 3.07E-03 6.02E-03 8.868-02 

a = All toxicity values werc extracted fiom "PC-Data Base: Screening Benchmarlo for Ecological Risk Assessmmt (revised December 1994)" 

Environmental Sciencw Division, Health Scimces Research Division, ORNL 

b = NOAEL - No Advem Effeds Level 


#N/A or - = not able to quantify because transfer factor or tolriwlogical benchmark was unavailable 

7.66E-02 

1.19E-02 

8.22E-05


with surface soil at PGDP, WAG 1, TCE Spill Site (SWMU 136) 

Reprcsen t i tive 

Concentration 

Soil 

Chemical (mgkg) Plants Microbes Earthworms 

Aluminum 7.248+03 1.45E+02 1.21 E+01 


Antimony 

Arsenic 

Barium 

Beryllium 

Cadmium 

Calcium 

Chromium 

Cobalt 

9.90E-01 

1.70E+00 

6. I OE+OO 

7.248+01 


2.60E-01 

2.58E+04 

2.90E+O I 

2.70E+01 

3.40E-01 

6.10E-01 

1.45E-01 


8.67842 

2.90E+01 

6.10E-02 

2.41E-02 

1.30E-02 

2.90E+00 

1.02E-01 

1.30E-02 

7.25E+01 

Copper 

Iron 

Lead 

Magnesium 

Manganese 

Nickel 

Potassium 

Sodium 

Sulfate 

Thallium 

Vanadium 

Zinc 

Benzene 

Benzo(a)anthraccnc 

Benzo(a)pyrcne 

Benzo(b)fluoranthcnc 


6.00E+00 

2.13E+04 

6.508+00 

6.038+02 

8.56E+02 

7.70E+00 

2.788+02 

8.678+01 

9.728+02 

1.40E-01 

2.43E+OI 

2.14E+O I 

2.00E-03 

3.80E-01 

5.2OE-Ol 

6.40E-01 

2.70E-01 

1.35E+00 2.708-02 

6.00E-02 6.00E-02 

1.07E+02 

I .30E-01 7.228-03 

1.71E+00 

2.57E-01 

I .40E-01 

l.22E+01 


8.56E+00 

8.56E-02 

1.22E+00 

2.14E-01 

I .20E-01 

1.30E-02 

3.858-02 

1.07E-01


with surface soil at PGDP, WAG 1, TCE Spill Site (SWMU 136) (continued) 

Represen tathe 

Concentration 

Chemical (mg/kg) Plants Mieroba ' Earthworms ' 


2.30E-01 

Chrysene 


Di-n-butyl phthalate 2.2OE-01 l.lOE-03 


Fluoranthene 

Indeno(l,2,3cd)pyrene 

Phenanthrene 

Pyrene 


8.10E-02 

3.40E-01 

3.1 OE-01 

7.908-02 

2.80E-0 1 


Soil 

Hazard Index 1.91E+02 1.32E+O2 7.29E+01 

a = All toxicity values were extracted from "PC-Data Base: Screening Benchmarks for Ecological Risk Assessment (revised December 1994)" 

Environmental Sciences Division, Health Sciences Research Division. ORNL 


- =not able to quantify because transfer factor or toxicological benchmark was unavailable 

Bold Value indicates hazard quotient or hazard index is greater than I.


PGDP, WAG 1, TCE Spill Site (SWMU 136) 

Representative Meadow Vole ' White-footed Mouse ' 

Short-tailed Shrew 

Concentration DaUy InW NOAEL ' Hazard DdyIntakc NOAEL' Hazard DaUy Intake NOAEL' Hazard 

chemical (W/kb) (mak) (mmW Quotients (mmkg) (mgkg) Quotients (wkg) (mgkg) Quotients 

Aluminum 

Ammonia (u Nitrogen 

Antimony 

Arsenic 

Barium 

Beryllium 

Cadmium 

Calcium 

Chromium 

Cobalt 

copper 

Iron 

Lead 

Magnesium 

Manganese 

Nickel 

Potassium 

Sodium 

Sulfate 

Thallium 

Vanadium 

zinc 

Bcnzene 


Benzo(a)pyrcne 

Bcnzo@)fluoranthene 

Bcnzo(&i)perylene 

7.24E+03 

9.90E-01 

1.70E+00 

6.10E+00 

7.24E+01 


2.60E-01 

2.58E+04 

2.90E+01 

2.70E+01 

6.00E+00 

2.13EM4 

6.5OE+00 

6.03E+02 

8.56E+02 

7.70E+00 

2.78EM2 

8.67E+01 

9.72E+02 

1.40E-01 

2.43E+01 

2.14E+01 

2.00E-03 

3.80E-01 

5.20E-01 

6.40E-01 

2.70E-01 

2.OZE+01 

#N/A 


2.07E-02 

2.78E-01 

1.24E-03 

3.09E-03 

#N/A 

7.92E-02 

8.98E-02 

2.83E-02 

#N/A 

1.798-02 

#N/A 

8.79E+00 

3.648-02 

#N/A 

3.09E-01 

#N/A 

3.83E-04 

6.85842 

2.93E-01 

8.21 E-05 

1.18E-03 

1.52E-03 

1.87E-03 

7.63E-04 

1.70Ei-00 

#NIA 

1.10E-0 I 

1.1 I E-01 

1.08E+01 

I .31 E+OO 

1.69E-01 

#N/A 

6.50E+00 

#N/A 

3.28E+01 

#N/A 

1.59E+Ol 

#N/A 

1.74E+02 

7.93E+Ol 

#N/A 

#N/A 

#N/A 

1.5OE-02 

3.77E-01 

3.17E+02 

2.32E+01 

#N/A 

8.8 IE-0 1 

#N/A 

#N/A 

1.19EMI 


1.86E-01 

2.58E-02 

9.51 E-04 

1.83E-02 

1.22E-02 

8.63E-04 

1.13E-03 

5.04E-02 


2.55E-02 

1.82E-01 

9.25E-04 

3.53E-06 

1.73E-03 


#N/A 

2.63E-03 

7.95E-02 


7.14E-04 

I .66E-02 

#N/A 

2.17E-0 I 

5.30E-02 

5.54E-02 

#N/A 


#N/A 

9.978+00 

6.09E-02 

#N/A 

1.84E-0 I 

#N/A 

2.17E-04 

3.9 1 E-02 

1.97E-01 

6.38E-05 

1.93E-03 

3.02E-03 

2.71E-03 

9.26E-04 

2.14E+00 

#NIA 

1.38E-01 

1.40E-01 

1.35E+01 

1.65E+00 

2.12E-01 

#N/A 

8.17E+00 

#N/A 


#N/A 

I .99E+01 

#N/A 

2.19E+02 

9.978+01 

#N/A 

#NIA 

#N/A 

1.90E-02 


3.99E+02 

2.92E+01 

#N/A 

1.1 1E+00 

#N/A 

#N/A 

1.93E+01 

I .9 I E-02 

5.683-01 

3.57E-02 


7.81E-02 

2.66E-02 

1.34E-03 

2.29E-03 


6.11E-04 

I. I4E-02 

8.25E-02 


2.19E-06 

2.72E-03 

7.708+02 

#NIA 

1.33E-01 

9.39E-03 

7.82E+00 

3.35E-02 

1.20E-01 

#N/A 

3.45E+00 

2. I 1 E+OO 

7.29E-01 

#N/A 

7.51E-01 

#N/A 

9.548+01 

8.64E-01 

#NIA 

6.76E+00 

#N/A 

I .09E-02 

1.90E+00 

1.67E+00 

2.07E-04 

3.82E-02 

5.53E-02 

6.11 E-02 

2.44E-02 

2.43E+00 

#N/A 

1.57E-01 

I S8E-01 

1.54E+01 

1.87E+00 

2.40E-01 

#N/A 

9.288+00 

#N/A 


#N/A 

2.26E+01 

#N/A 

2.49E+02 

1.13E+02 

#N/A 

#N/A 

#N/A 

2. IOE-02 

5.38E-01 


3.31 E+01 

#NIA 

1.26E+00 

#N/A 

#N/A 

3.18E+02 

8.45E-01 

5.953+00 

5.09E-01 

1.80E-02 

5.0 I E-01 

3.72E-01 

1.56E-02 

3.32E-02 

3.83E-01 

7.64E-03 

5.20E-0 I 

3.52E+00 

3.69E-03 

6.24E-06 


Q Hazard 


PGDP, WAG 1, TCE Spill Site (SWMU 136) (continued) 

Representative Meadow Vole a White-footed Mouse Short-tailed Shrew ’ 

Concentration DdIyInWrc NOAEL’ Hazard DnilyIntPke NOAEL’ Hazard DaUy Intake NOAEL ’ Hazard 

Chemlcd (W4) (WCr) (mgkg) Qootienta CmtL) (mgkg) Quotients (nvYk) 

&nz*)fluoranthene 2.30E-01 6.748-04 #N/A 9.738-04 #N/A 2.20E-02 #N/A 

Chrysme 4.50E-01 1.39E-03 #N/A 3.2 1 E43 #N/A S.16E-02 

Din-butylphthalate 2.20E-0 I 6.828-04 4.85E+02 l.41E-06 1.20E-03 6.09E+02 2.27E-02 6.91E+02 3.29E-OS 

1.98E-06 

8.10E-02 2.51E-04 #N/A 6.278-04 #N/A 9.63E-03 #N/A 

3.40E-01 1.25E-03 #N/A 2.27E-03 #N/A 3.70E-02 #N/A 

3.10E-0 I 8.80E-04 #N/A 2.04E-03 #N/A 3.488-02 #N/A 

7.908-02 3.50E-04 #N/A 4.84E-04 #NIA 8.0 1E-03 #N/A 

2.80E-01 9.15E-04 #N/A 1.86E-03 #N/A 3.10E-02 #N/A 

Trichloroahcne 4.00E-03 1.19E-04 6.17E-01 1.94E-04 9.64E-05 7.7SE-01 I .24E-04 4.13E-04 8.80E-01 4.70E-04 

(nigkg) 

#N/A 

Quotients 

Hazard Index 1.24E+01 2.02E+01 3.303+02 

a = All toxicity values were extracted from “PC-Data Base: Screening Benchmarks for Ecological Risk Asscssmmt (revised December 1994)” 

Environmental Scienca Division, Health Sciences Research Division, ORNL 

b = NOAEL - NO A~VCISC Effcds Level 

Quotients arc unitless 

#N/A or - = not able to quanti@ because transfer fador or toXicological benchmark was unavailable 


Table 6.21. Ecological hazard quotients for surface water-associated in the northlsouth ditch along fence parallel to Portal Road No. 1 at PCDP, WAG 1, Sewage Treatment Plant (SWMU 38) 

Representative Eatinatd EaUaald EaBnatd LCV IC Sensitive 

Concratntlon LCV1* LCV'* ECn'. Aqnatic LO''* LCV"* LCV'" EC," Species Test Population Sceondary Secondary NAWQC '" NAWQC'" 

Cbemical (mtW Daphnidr Fish Fish Phats Daphnidr Fish Iuvertebrata Daphnidr ECn" ECn" Acute Values' Chronic Valma' Acute Chronic 

Anenk 

BllrlUm 

Caldum 

Chmmlum 

CWPW 

Im 

Lead 

Mag n e 8 l u m 

Mll~~~ZIE 

Nldrd 

Potassium 

S e l en I u m 

Silver 

Sodlum 

Chlomform 

TOhMlle 

i lOE-03 

I WE02 

I57EMI 

3 IOE-03 

6 20E-03 

3 79E-01 

5 70E-03 

5 75EMO 

3 15E-02 

7 30E-03 

2 IOEMO 

I WE43 

5 30E-03 

2 06EIOI 

4 00E-03 

5 008-03 

3.288-06 

3 038-05 

1.92E-07 

I98E-07 

3.94E-06 

I55E-03 

- 6208-03 

I14E-05 

1.468-03 

I 908-05 

I .77E4 

- 2.04E-08 

I35E-04 

5 06E-04 

2 70E-02 

2 40E-03 

4 658-04 

7 OlE-05 

2 86E-05 

1468-03 

3 %E45 

2 078-05 

2 ME43 

blr(2-Elhylhexyl)phlhalata 2.00E-03 - - 6.67EM 2.3118-04 - 6.678-04 - 4.00E-05 6.998-06 6.218-05 - 

4 24E-05 

1638-03 

2 928-04 

3 02E-04 

1788-05 

2 WE44 

2 ISE-05 

4 42E-02 

3 238-06 

I .02E-03 

2 248-04 

5.69E-05 

6.2OE-03 

3.028-02 

2.37842 

2.86E-05 

1.62E-04 

7.60E-05 

9.468-03 

I 17E-02 

2 388-02 

I63E-02 

6 648-04 

7 31E-04 

3 798-02 

9818-06 

7 21E-04 

8 OIE-05 

2818-04 

3 408-05 

1668-02 

7 12E-06 

2 50E-05 

2 758-04 

2 14E-05 

I 19E-06 

I 598-06 

5 00E-03 

3 92E-04 

147E-02 

2 I3E-OS 

2 84E-05 

1948-04 

3 448-04 

6 95E-05 

521E-06 

7 31E-06 

I 29E-03 

2 828-04 

5 17E-04 

3 798-04 

1788-03 

4 56E-05 

5 43E-05 

Hwrd Index 347EM 3948-06 - 9421-03 34118-02 4698-02 I30E-03 705E-02 9 IOE-02 I78E-02 306E-04 2 OZE-02 1 91E-03 3 ME-03 

I LCV -Lowest Chronic Value 

2 - E P - Effective Conantdon La a reduction of 20% of Le growlh produdion occurs 

3 - NAWQC - National Ambient Walu Quality C hrh 

a - All toxicity values were emed 

fmm 'PC-D.u Bue Sersening Benchmarks for Ecological RI* Auammt (mid December 1994). 

Envimnmmul Scimcu Division. HdL Scimcer R d Division. OWL 

* * Hacard Quotients are un~tlua 

- - not able to quantify becars msfer faor or toxicologicd benchmark wm unavulabk

Table 6.22. Ecological hazard quotients for surface water-associated organisms in the eastlwest ditch parallel to Water Works Road at PGDP, WAG 1, Sewage Treatment Plant (SWMU 38) 

Representative Estimated Erliantd Ltimnted LCV Scnrilive 

Comrmtrntloa LCV IC LCV '*' EC," Aquatic LCV "* LCV LCV ECZ," Species Tat Population Sccoodnry Secondary NAWQC'" NAWQC'" 

Cbcalcnl (-m) Dapbaidr Fisb Fish nanb Dnpbmldi Fisb Iavertebrntn Dapbnidr EC," EC,"' Acute Vnlua' Chronic Values' Acute Chronic 

Aluminum 5 84E-01 1278-03 307EM I78E-04 I WE43 7 798-03 7 798-04 6 71 E-03 

Barium 9 5ZE-02 I64E-05 138E-03 2 5 I E-02 

Cdcium 

Coppr 

Ira, 

M.gnerium 

Mmgmre 

Potassium 

Sodium 

Zinc 

Ethylbenzene 

7 l4E+01 6 16E-04 

3 IOE-03 - 3 108-03 l35E-02 8 i6EM 5 llE-04 I 5IE-02 I l9E-02 36OE-04 i 728-04 ZSBE-04 

I I4E+00 7228-03 877E-04 7 13E-02 I14E-03 

6 8UE+OO - 8398-05 

6 56E-01 - S%EM 371EM 5 % E4 5 868-03 4 468-04 8 17E-03 

5 6oE+00 I06EM 

I59EMI 2348-05 - 

8 668-02 - 289803 I85E-03 2388-03 165E-05 4 I2E-03 I O8E-03 7228-04 787E-04 

I WE43 1478-07 - - 434E-09 - 432846 4 778-06 2 738-07 4 88E-06 

Toluene I soe-03 5.95E-08 l.llE-06 - 612E-Ob - 7 50E-06 4 768-07 8 52E-06 

Hazard Index 400E-05 l.lEE-06 - 7268-03 2.43842 462E-03 5.28E-04 8.80E-02 2388-02 7318.03 I8ZE-03 3 328-02 I67E-03 8.908-03 

I - LCV - Lo- 

Chronic Vdue 

production O~CUN 

Ambient Wlter Quality Critaia 

- All toxicity vdua were exbrtrd h 'PC-Data Bue: Saeming Benchmvks fa Ecologid Risk Assesmenl (mid Deu?mba 1994)' 

Environmental Sciences Division. Hdth Scimm Research DivirioR OWL 

2 - EC? - ERCAVC conanbairn IIW I ruiuaion ofzw. of the uo~rh 

3 - NAWQC - N d d 

- H urd Quotimu pe unitleu 

- - no( able to quanti* bemuse transfa factor M toxidogid benchmark w u unavailable

Table 6.23. Ecological hazard quotients for sediment-associated organisms in the north/south ditch along fence parallel 

to Portal Road No. 1 at PGDP, WAG I, Sewage Treatment Plant (SWMU 38) 


Concentmtion Efkb Eflects EPA 

Chemlenl (mgkg) Range Low Range Medium OMOE '*' EPA*" Region V H&S '*' WIDNR 4' 

Aluminum 


Arsenic 1.5OE+00 1.83E-01 2. I4E-02 2.5OE-01 

Barium 3.47E+01 6.94E-02 

Beryllium 

1.60E+00 

Calcium 

I. l3E+03 

Chromium 8.53E+01 l.OSE+OO 2.31E-01 3.2SE+OO 

Cob& 

I .01E+01 

copper 1.53E+O 1 4.5OE-01 5.67E-02 

Iron 4.85E+04 2.8SE+OO 

Lcad 9.20E+00 1.97E-01 4.22E-02 

Magnesium 

3.34E+02 

Manganese 


l.OOE+OO 

M- 1.30E-01 8.67E-01 1.83E-01 

Nickel 1.62E+01 7.71E-01 3.14E-0 1 

Potassium 

1.70E+02 

Selenium 

2.30E-01 

Sodium 

4.1 SE+Ol 

Vanadium 

9.72E+01 

Zinc 5.91E+01 3.94E-01 1.44E-01 

Benzene 5.00E-03 9.62E-02 

Di-n-butylphlhalatc 2.60E-01 6.18E-03 

Fluoranthme 1.60E-01 

2.58E-02 

Phenanthrene 1.00E-01 5.56E-02 

Pyr*le 

1.90E-01 

bis(2-Ethylhexyl)late 2.90E-01 3.26E-07 

Hazard Index 3.923+00 9.92E-01 4.543+00 8.14E-02 2.85E+OO 1.OZE-01 6.94E-02 

1 = OMOE - Ontario Ministry of the E&rOnm& 


3 = H&S - Hull and SU~N 

4 = WINDR - Wisconsin Division ofNalural Resources 

a = All toxicity values were extracted 6um "PC-Data Base: Screening Benchmarks for Ecological Risk Assessment (revised December 1994)" 



- = not able to because transfer factor or toxicological benchmark was unavailable 


Table 6.24. Ecological hazard quotients for sediment-associated organisms in the east/west ditch parallel to 

Water Works Road, Sewage Treatment Plant (SWMU 38) 


Concentnation Effeets EffCCt.9 EPA 

Chedcd (mg/kg) Range Low Range Medium OMOE ’*’ EPA”’ Region V H&S WIDNR 4’ 

Aluminum 

8.88E+03 

Arsenic 3.60E+00 4.39E-01 5.14E-02 6.00E-01 

Barium 7.54E+01 1.5 1 E-0 1 

Beryllium 4.70E-0 1 

Calcium 

3.40E+03 

Chromium 1.59E+OI 1.96E-01 4.30E-02 6.12E-01 

Cobalt 

6.70E+00 

cow 1.92E+Ol 5.65E-01 7.1 lE-02 

Iron 1.27E+04 7.47E-01 

Lead 1.82E+O 1 3.90E-01 8.35E-02 

Magnesium 

1.27E+03 


Nickel 1.28E+OI 6.10E-01 2.48E-01 

Potassium 

5.58E+02 

Selenium 

3.40E-01 

Sodium 

7.04E+01 

Vanadium 

I .98E+01 

Zinc 2.65E+02 1.77K+OO 6.46E-0 I 

Acetone 6.50E-02 1.02EM0 

Fludene 2.10E-01 3.39E-02 

M a e 

2.00E-01 

Hazard Index 3.97E+00 1.14E+00 2.21EMO 3.39E-02 7.478-03 l.OZE+OO 1.5 1E-01 


2 = EPA - United Stat- Environmmtal Rotection Agency 

3 = H8S - Hull Md Suer 

4 = WINDR - Wiscoruin Division of Natural Resources 

a = All toxicity values were extmcted h “PC-Data Base: Screening Benchmarks for Ecological Risk Assessment (revised December 1994)” 






with surface soil at PGDP, WAG 1, Sewage Treatment Plant (SWMU 38) 

Rcprescn ta tivc 

Concentration 

Chemicd (mglkg) Planb ' Microbes ' Earthworms ' 

Aluminum I. I7E+04 2.78EM2 232E+Ol 


1.35E+OI 

Antimony 1.50E+00 3.008-01 

Arsenic 

Barium 

Beryllium 

Calcium 

Chromium 

Cobalt 

Copper 

Iron 

Lead 

Magnesium 

Manganese 

Mercury 

Nickel 

Potassium 

Selenium 

Silver 

Sodium 

Vanadium 

6.88E+00 

8.06E+OI 

5.73E-0 1 

9.228+04 

2.13E+01 

1.06E+O I 

I .86E+01 

2.028+04 

2.09E+01 

2.508+03 

7. I I E+02 

1.08E+00 

I .27E+01 

6.598+02 

2.868-01 

I .03E+00 

9.40E+01 

3.08E+OI 

134EM0 

1.90E-01 

7.60E-02 

2.78E+Ol 

8.658-01 

2.668-01 

6.52E-01 

2.16E+00 

1.20Et01 

5.438-01 

3.908-01 

7.50E-01 

1.96E+01 

Soil 

I .34E-01 

3.168-02 

2.78E+00 

1.738-02 

2.668-01 

1.34E+02 

3.628-02 

1.08E+01 

1 .2OE-Ol 

1.818-01 

3.908-03 

3.00E-02 

1.96E+00 

2.238-01 

6.95E+01 

5.328-01 

6.528-02 

3.60E+01 

8.158-02 

5.5 7E-03 

Zinc 6.65E+01 3.00E+00 1.50E+00 7.50E-OI 

Acenaphthenc 

6.00E-02 

Acetone 3.708-02 

Anthracene 7.208-02 

Aroclor- I260 


Benzo(a)anthracene 1.508-01


with surface soil at PGDP, WAG 1, Sewage Treatment Plant (SWMU 38) (continued) 


Concentration 

Chemica~ (mglkg) Plants ' Microbes ' Earthworms ' 

Benzo(a)pyrene 1.308-01 

Benzo(b)fluoranthene I ,908-01 

Benzo(k)fluoranthene 6.408-02 

Carbazole 4.808-02 

Chrysene 

I SOE-01 

Di-n-butyl phthalate 5.998-01 9.008-03 

Phenanthrene 2.668-01 

Pyrene 2.698-01 

Soil 

Hazard index 3.48E+02 1.75E+02 1.07E+02 






Table 6.26. Ecological hazard quotients for wildlife receptors asociated with surface soil at 

PGDP, WAG 1, Sewage Treatment Plant (SWMU 38) 

Representative Meadow Volt ' White-footed Mouse ' Short-tailed Shrcw ' 

Concentration DaUyIntnkc NOAEL' Hazard DPilyIntalrc NOAEL' Hazard DailyIntake NOAEL' Hazard 

chemlcd (mrh) (mgny) (w4) Quotients (mrW (mgk) Quotients (mg/ks) (mg/kg) Quotlents 

Aluminum 


Antimony 

Arsenic 

Barium 

Bayllium 

Calcium 

Chromium 

Cobalt 

copper 

Iron 

Lead 

Magnesium 

Mangan- 

MaCUl-y 

Nickel 

Potassium 

Selenium 

Silva 

Sodium 

Vanadium 

Zinc 

Acenaphthene 

Acetone 

Anthracene 

Aroclor-1260 

Bmzo(a)anthrame 

1.17E+04 

I .35E+O 1 

I.5OE+00 

6.88E+00 

8.06E+01 

5.73E-01 

9.22E+04 

2.13E+O I 

1.06E+OI 

1.86E+O 1 

2.OZE+04 

2.09E+01 

2.50E+03 

7.1 1 E+OZ 

1.08E+00 

1.27E+01 

6.59E+02 

2.86E-01 

1.03E+00 

9.40E+O 1 

3.08E+01 

6.65E+01 

6.00E-02 

3.70E-02 

7.20E-02 

4.7lE-02 

l.SOE-0 1 

3.27E+01 

#N/A 

4.1 OE-03 

2.33E-02 

3.09E-01 

1.6633-03 

#N/A 

5.823-02 

3.53E-02 

8.79E-02 

#N/A 

5.75E-02 

#N/A 

7.30E+00 

3.89E-02 

6.00E-02 

#N/A 

3.958-03 

5.38E-03 

3.35E-01 

8.688-02 

9.IZE-01 

#N/A 

3.28E-02 

3.2 1 E-04 

1.31E-04 


1.70E+00 

#N/A 

1. IOE-01 

I.IIE-0I 

1.08E+OI 

1.31E+00 

#NIA 

6.50E+00 

#N/A 

3.28E+OI 

#N/A 

1.59E+01 

#N/A 

1.74E+02 

1.30E-02 

7.93E+01 

#N/A 

6.60E-02 

#N/A 

#N/A 

3.77E-01 

3.17E+02 

#N/A 

1.98E+01 

#N/A 

#N/A 

#N/A 

1.92EMl 

3.73E-02 

2.10E-01 

2.87E-02 

1.27E-03 

8.95E-03 

2.68E-03 

3.62E-03 


2.99EMO 

7.57E-04 

5.99E-02 

2.30E-01 

2.87E-03 

1.65E-03 

6.683+01 

#N/A 

2.32E-03 

8.978-02 

5.38E-01 

9.52E-04 

#N/A 

1.59E-01 

2.08E-02 

1.72E-01 

#N/A 

1.47E-01 

#N/A 

8.28E+00 

3.93E-02 

I .OOE-0 I 

#N/A 

2.65E-03 

3.38E-03 

2.00E-01 


6.1 1E-01 

#N/A 

2.29E-02 


2.47E-04 

7.628-04 

2.14E+00 

#N/A 

1.38E-01 

1.40E-01 

1.35E+01 

1.65E+00 

#N/A 

8.17E+00 

#N/A 


#NIA 

1.99E+O 1 

#NIA 

2.19E+02 

1.60E-02 

9.97E+0 I 

#N/A 

8.308-02 

#N/A 

#N/A 


3.998+02 

#N/A 

2.49E+01 

#NIA 

#N/A 

#NfA 

3.13E+01 

1.68E-02 

6.41E-01 

3.97E-02 

5.79E-04 

1.953-02 


7.35 E-03 

3.78E-02 

2.45&+00 

1 .O I E-03 

3.20E-02 

I .OSE-01 

3.538-03 

9.21 E-04 

1.24E+03 

#N/A 

1.17E-01 

1.06E+00 

8.71E+00 


#N/A 

2.53E+00 

8.27E-01 

2.26E+00 

#N/A 

2.42E+00 

#N/A 

7.92E+01 

1.71 E4 1 

1.43E+00 

#NIA 

2.23E-02 

8.03E-02 

7.33E+00 

2.40E+00 

5.19E+00 

#N/A 

3.828-03 

7.54E-03 


I .5 1 E-02 

2.43E+00 

#N/A 

1 S7E-01 

1 BE-01 

1.54E+01 

1.87E+00 

#N/A 

9.28E+00 

#N/A 


#N/A 

2.26E+Ol 

#NIA 

2.49E+02 

1.80E-02 

I. 13E+02 

#N/A 

9.40E-02 

#N/A 

#N/A 

5.388-0 I 


#N/A 

#N/A 

#N/A 

#N/A 

#NJA 

5.13E+02 

7.458-01 

6.71E+00 

5.67E-01 

2.40E-02 

2.73E-01 


1.07E-0 I 

3.18E-01 

9.49E+00 

1.26E-02 

2.37E-01 


1.15E-02

Table 6.26. Ecological hazard quotients for wildlife receptors asociated with surface soil at 

PGDP, WAG 1, Sewage Treatment Plant (SWMU 38) (continued) 

Repmcntative Mudow Vole ' White-footed Mouse ' Short-tailed Shrew ' 

Concentrntlon DpuyInt.lrr NOAEL' Hazard DaUyIntake NOAEL' Hazard DdyIntake NOAEL' Hazard 

Chemlcd (mglkb) (web) (mmW Quotlenb (mmW (nigkg) Quotients (nigkg) (mgkg) Quotients 

-o(ah)me 1.30E-01 3.8 I E44 8.81E-01 4.328-04 7.55E-04 l.llE+OO 6.81E-04 1.38E-02 1.26E+00 I.lOE-02 

Bmzo(b)fluoranthene 1.90E-01 5.57E-04 #NIA 8.04E-04 #N/A 1.828-02 #N/A 

&nzO(k)flUoranthens 6.40E-02 1.878-04 #N/A 2.71E-04 #N/A 6.11E-03 #N/A 

Carbazole 4.80E-02 #N/A #N/A #N/A #N/A #N/A #N/A 

Chrysme I. 5OE-01 4.64E-04 #N/A I .07E-03 #N/A 1.72E-02 #N/A 

Di-n-butylphthalate 5.99E-01 1.86E-03 4.85EM2 3.83E-06 3.28E-03 6.09E+02 5.38E-06 6.39E-02 6.91E+02 8.95E-05 

PhenanthrenS 2.66E-01 I.lsE-03 #N/A 1.63E-03 #N/A 2.70E-02 #N/A 

41me 2.69E-01 8.79E-04 #N/A 1.798-03 #N/A 2.978-02 #N/A 

Hazard Index 2.28E+Q1 3.46E+01 5.36E+Q2 

a * All toxicity values were extracted fiom "E-Data Base: Scnming Benchmarks for Ecological Risk Assessment (revised December 1994)" 

Environmental Scimces Division, Health Sciences Research Division, ORNL 

b = NOAEL - NO Adverse Effcds Level 

* = Hazard Quotimts are unitless 

#N/A or - = not able to quantify because transfer fador or toxicological benchmark was unavailable 

Bold Value indicates hazard quotient or hazard index is greats than I.

Table 6.27. Ecological hwrd quotients lor surface water-associated organisms in the unnamed tributary of Big Bayou Creek at PGDP, WAG 7, C-746-K Sanitary Landfill (SWMU 8) 

Rcpracntatlv Estimated Estimated EStimated LCV Scnsitlve 

Concentration LCV IC LCV ECm- Aquatic LCV IC LCV IC LCV IC ECnb Spzcles Test Population Secondary Secondary NAWQC ’.’ NAWQC‘.’ 

Chemical (mgk) Daphnidr Fish Fish PIanb Daphnlda Fisb Invertebrata Daphnids ECmb ECmL’ Acute Values’ Chronic Values’ Acute Chronic 

Almnimna 

2.15E+OO 

4.678-03 1.13E-03 6.54E-04 

3.98843 2.87E-02 

2.87843 

Antimony 

Awic 

1.68E-02 

l.18E-03 

2.75E-05 3. I lE-06 I.05E-05 

8.84E-06 

2.13E-04 1.71E-05 1.628-04 

BUiuin 

Cadmium 

Calcium 

chloride 

Cbmmium 

Copper 

lrofi 

Lead 

Magnesium 

Mm8- 

Nickel 

Potassium 

Selenium 

Silicon 

SOdilrm 

Smntium 

Sulfate 

Thallium 

Vmadiuin 

Zinc 


cis-l.2-DicNdene 

5.28E-02 

2.38E-03 

2.49EM1 

1.40EMI 


5.78E-03 

8. I5E+OO 

3.40843 

5.80E+OO 

1.39EMI 

7.40E-03 

3.2IEMO 

1.06E-03 

5.04EW 

1.80EMI 

I.I4E+OO 

4.48EMI 

1.25E-03 

5.04E-01 


3.00E-03 

6.83E-03 

9.10E-06 

2.65E-05 

1.19E-03 

5.78E-03 

6.80E-06 

l.48E-03 

1.06E-05 

1.2SE-05 

1.478-02 

1.59E-02 

2.15E-04 

2.51E-02 

5.16E-02 

2.77E-04 

7.07E-05 

1.268-02 

1.48E-03 

6.06E-05 

I. 16E-05 

2.7 I E-05 

9.62E-06 

5.36E-04 

9.448-03 

1.40E-03 

1.52E-03 

6.27E-03 

l.8OE-04 

7.85E-03 

2.11E-04 

I.2OE-05 

2.19E-05 

6.30843 

1.21E-02 

Huud Index 3.56E-05 - 2.79842 1.18E-01 3.65E-02 1.23E-03 5.59E-01 2.66E-01 1.47E-01 1.22E-02 2.15E-01 7.528-03 4.07E-02 

I = LCV - Lowest Chronic Value 

2 - E? - Effective Concenmtion that a reduction of 20% of the moWh production OCCM 

3 - NAWQC - National Ambient Water Quality Criteria 

- Huud Qdenb me unitlesr 

- =not able to quantify because transfer factor or toxicological benchmark was unavailable 

9.538-04 

1.348-04 

5.768-05 

8.41E-05 

a - All toxicity values were exmctcd &om “PC-Dab Base: SEmning Benchmarks for Ecological Risk Assessment (revised Dcccmbcr 1994)” 

Envimnmentd Sciences Division, Health Scicncn Research Divisim OWL 

3.17E-03 

2.82842 

5.09E-01 

1.268-02 

1.64E-04 


1.95E-05 

1.l7E-03 

1.83E-01 

2.22E-02 

9.71843 

6.73E-04 


2. IOE-02 

5.53E-04 

6.728-04 


1.24E-01 

3.44845 

I87E-05 

1.588-02 

5.518-03 

7.64E-04 

9.46843 

1.87E-04 

7.62E-06 

1.77843 

1.39E-02 

I .73E-01 

1.848-03 

6.94E-05 

2.64E-02 

6. IOE-04 

3.218-04 

4.ISE-OS 

5.298-06 


3.68843 

2.16E-03 


8.1SE-03 

1.06E-03 

4.63E-OS 

3.03E-OS 

4 .O 1 E-03

~~ 

~ ~ ~ ~ - 

Table 6.28. Ecological hazard quotients for sediment-associated organisms in the unnamed tributary of Big Bayou Creek 

at PGDP, WAG 7, C-746-K Sanitary Landfill (SWMU 8) 

Represcnta tive 

Concentration Effects Effects EPA '*' 

Chemical (mglkg) Range Lon Range Medium OMOE '' EPA *.' Region V H&S 3*' WIDNR "' 

A I u m i n u m 

Antimony 

Arsenic 

Barium 

Beryllium 

Calcium 

Chromium 

Cobalt 

Copper 

Iron 

Lead 

Magnesium 

Manganese 

Nickel 

Potassium 

Selenium 

Sodium 

Vanadium 

Zinc 

Di-n-butvlahthalate 


I .90E+00 

8.5 I E+OO 

9.7 I E+OI 

8.98E-03 

5.76 E+02 


1.52E+OI 

5.30E+00 

3.60E+04 

1.14E+O 1 

2.918+02 

9.83E+02 

7.09E+00 

1.858+02 

2.648-01 

I .33E+02 

5.348+01 

1.84E+01 

2.72E-0 I 

9.50E-01 

1.04E+00 

5.738-01 

1.56E-01 

2.44E-03 

3.38841 

1.23E-01 

7.60E-02 

I .22E-01 

1.25E-01 

1.968-02 

5.23E-02 

1.37E-01 


2.14E+00 

2.12Et00 

6.468-03 

I .94E-0 I 

Hazard Index 

3.42E+00 5.77E-01 5.34E+00 2.12E+00 6.468-03 I .94E-01 

I = OMOE - Ontario Ministry of the Environment 


3 = HBS - Hull and Suter 

4 = WMDR - Wisconsin Division ofNatural Resources 

a = All toxicity values wen extracted from "PC-Data Base: Screening Benchmarks for Ecological Risk Assessment (revised December 1994)" 

Environmental Sciences Division. Health Sciences Research Division, ORNL 




. 

e 

= a 

a; 

f 

4- 

N 

? 

. g , 

09 

9 

0 0 

0 0 

+ + 

' g g 

33


with surface soil at PGDP, WAG 7, C-746-K Sanitary Landfill (SWMU 8) (continued) 


Concentration 

Chemical (mg/kg) Phb ' Microbes ' rrthworms 

Acetone 

1.58E-01 

Anthracene 

2.878-0 I 

Aroclor-1260 7.608-02 

Benzene 6.748-03 

Bcnzo(a)anthracenc 

3.1 OE-01 

Bcnzo(a)pyrenc 

2.95E-01 

Bcnzo(b)fluoranthcne 3.76841 

Benzo(k)fluomthene I .80E-0 I 

Carbazole 

2.00E-01 

Chryscnc 

3.40E-01 

Di-n-butylphthalate 2.67E-01 1.35843 

Dibcnzohran 2.76841 

Fluoranthcne 

8.01 E41 

Fluorene 2.91 E-01 I .278-02 

Indeno( 1.2.3-cd)pyrcne 2.30E-01 

Naphthalene 2.97841 

Phenanthrene 

Pyrene 

9.79841 

5.19E-0 I 

Hazard Index 1.99E+02 l.38E+02 4.13E+OI 

Soil 







PGDP, WAG 7, C-746-K Sanitary Landfill (WMU 8) 

Rcpmentathre Meadow Vole ' Whlte-footed Mouse a Short-tailed Shrew ' 

Concentration Dilly Intake NOAEL ' Hazard Dilly Intake NOAEL' Hazard Daily Inlake NOAEL ' Hazard 

Chcmlml (~&) (msntp) (msntp) Quotlcnb (mgntp) (mgkg) Quotlents (melke) (me/kp) Quotlenb 

Ahrminum 

7.00Et03 

1.96Etol 1.7OEt00 1. ISE+Ol 4.00E+01 2.14E+00 1.87E+01 7.45Et02 2.43E+OO 

~ 

3.07E+02 

Antimony 

ArscniC 

Buium 

Snyllium 

CJdmiUm 

C l k i 

Chromium 

Cobalt 

copper 

Iron 

Lead 

MagnelIim 

Mmg.nesc 

Nickel 

Phosphate (do) 

Potauaium 

Sclcnium 

1.92E+OO 

3.78Et00 

8.46EtOl 

7.06E-01 

2.82E-01 

8.25Et04 

I. l6E+01 

9.61E+00 

1.03E+01 

1.27Et04 

I. I8Et01 

1.53Et03 

1.14Et03 

1. 50E-01 

1.17EtOl 

5.70EtOl 

4.13Et02 

7.68E-01 

5.25E-03 

1.28E-02 

3.25841 

2.048-03 

3.35E-03 

#N/A 

3.1 IE-02 

3.20E-02 


#N/A 

3.25E-02 

#NIA 

1.17Eto1 

5.40E-03 

5.53E-02 

#N/A 

#N/A 

1.06E-02 

l.lOE-O1 

I.llE-01 

1.08EtOI 

1.31E+00 

1.69E-01 

#N/A 

6.50EtOO 

#N/A 

3.28Et01 

#N/A 

1.59E+01 

#N/A 

1.74E+02 

I .30E-02 

7.93Et01 

#NlA 

#N/A 

6.608-02 


1.16E-01 

3.01E-02 

1.56E-03 

1.98E-02 


1.48E-03 

2.05E-03 

6.713-02 


6.97E-04 

1.61E-01 

2.97E-03 


5.65E-01 

1.17E-03 

I.80E-02 

#N/A 

8.68E-02 

1.89E-02 

9.5 I E42 

#N/A 

8.28E-02 

#N/A 

1.33EtoI 

5.45E-03 

9.25E-02 

#NlA 

#N/A 

7.12E-03 

1.38E-01 

1.4OE-01 

1.35Et01 

1.65E+OO 

2.12E-01 

#N/A 

8.17EtUO 

#N/A 


#N/A 

1.99Et01 

#N/A 

2.19E+02 

1.60E-02 

9.97E+O1 

#N/A 

#NIA 

8.30E-02 

2.16E-02 

3.52E-01 


7.13E-04 

8.47E-02 

1.06E-02 

2.31E-03 


6.05E-02 

3.41E-01 

9.283-04 

8.58E-02 

1 SOE-01 

5.82E-01 

9.14EtOO 

5.5 1E-02 

1.3OE-01 

#N/A 

1.38EtW 

7.50E-01 

1.25Et00 

#N/A 

1.36E+OO 

#N/A 

1.27Et02 

2.37E-02 

1.31E+00 

#N/A 

#N/A 

5.99E-02 

1.57E-01 

1.58E-01 

1.54Et01 

1.87E+OO 

2.40E-01 

#N/A 

9.28Et00 

#N/A 


#N/A 

2.268+01 

#N/A 

2.49E+02 

1.8OE-02 

1.13E+02 

#N/A 

#N/A 

9.4OE-02 

9.54E-01 

3.68E+OO 

5.95E-01 

2.9SE-02 

5.438-01 

1.49E-01 

2.67E-02 

6.03E-02 

5.1OE-01 

1.32E+OO 

1.16E-02 

6.37E-01 

S M 

7.39E-01 

3.86E-03 #N/A 

2.43E-03 #N/A 

5.76E-02 

#N/A 

SOdiUm 

Thallium 

VmdiUIll 

zinc 

2-Methytnaphthalme 

4,4'-DDT 

Acmaphthmc 

6.32Et01 

1.38E-0 I 

1.78E+01 

3.77EtOt 

1.20E-01 

2.50E-03 

2.50E-01 

2.25841 

3.77E-04 

5.02E-02 

5.17E-01 

7.82E-04 

7.24E-06 

#N/A 

#N/A 

1.50E-02 

3.77E-01 

3.17Et02 

#N/A 

I. 59Et00 

#N/A 

2.52E-02 

1.33E-01 

1.6313-03 


1.34E-01 

2.14E-04 

2.86E-02 

3.47E-01 

7.93E-04 

l.33E-05 

#N/A 

#N/A 

1.90E-02 


3.99E+02 

#N/A 

1.99E+00 

#N/A 

I. 13E-02 

6.04E-02 

8.69E-04 

6.69E-06 

4.93EtOO 

1.08E-02 

1.39EtOO 

2.94E+00 

1.14E-02 

2.58E-04 

#N/A 

#NfA 

2.1OE-02 

5.388-01 


#N/A 

2.26E+00 

#N/A 

5.13E-01 

2.58EtOO 

6.5OE-03 

1.14E-04


PGDP, WAG 7, C-746-K Sanitary Landfill (SWMU 8) (continued) 

Represenlatlve Meadow Vole ’ White-footed Mouse Short-tailed Shrew 

Concentration Dailylnlake NOAEL’ Huvd Ddy Intake NOAEL ’ Hazard Daily Intake NOAEL ’ Hazard 

Chemlal (ms/lrs) (ms/lrs) (me) Quotients (wm) (msnCg) Quotients (wntg) (mgnCe) Quotlents 

I. 58E-0 I 

1.4OE-01 

I .98E+01 

2.87E-01 

7.60E-02 

6.74E-03 

3.1OE-01 

2.95841 

3.76E-01 

l.8OE-01 

2.00E-01 

3.40E-01 

2.67E-01 

2.76E-01 

8.0 IE-0 I 

2.91E-01 

2.30E-01 

2.97E-01 

9.79E-01 

1.288-03 

2.11E-04 

2.77E-04 

9.61E-04 

8.64E-04 

l.10E-03 

5.27E-04 

#NlA 

l.OSE-03 

8.28E-04 

#NIA 

2.948-03 

1.5OE-03 

6.53E-04 

3.41E-03 


UN/A 

#NlA 

2.32EMI 

#NlA 

8.81E-01 

#N/A 

INIA 

#NlA 

YNIA 


INIA 

UNIA 

#NlA 

INIA 

INIA 

MIA 

5.19E-01 1.70E-03 #NlA 

7.0633-03 9.80E-02 2.49E+OI 

1 ME-03 #N/A 

3.99E-04 UNIA 

1.19E-05 2.1 SE-04 2.92E+Ol 

1.57E-03 UNIA 

9.81E-04 1.71E-03 l.llE+OO 

1.59E-03 #N/A 

7.62E-04 #N/A 

UN/A 

#N/A 

2.4313-03 INIA 

1.71E-06 1.468-03 6.09E+02 

#N/A 

#NlA 

5.36E-03 #NlA 

I HE-03 UNIA 

1.52E-03 #NlA 

3.02E-03 UN/A 

6.00E-03 #NlA 

3.4SE-03 #N/A 

3.93E-03 1.631-02 #N/A 

3.01E-02 

UNIA 

7.85E-03 

UN/A 

7.378-06 6.96844 3.3 IE+OI 

3.12E-02 UNIA 

1 S5E-03 3.14E-02 1.26E+00 

3.59842 UN/A 

l.72E-02 UNIA 

UN/A 

UNIA 

3.90842 UNIA 

2.4OE-06 2.76E-02 6.91 E+02 

UNIA 

UNIA 

8.728-02 UN/A 

2.76E-02 UNIA 

2.58E-02 #N/A 

2.84E-02 UN/A 

- . 9.93E-02 UN/A 

5.741-02 UNIA 

2.10E-05 

2.5OE-02 

3.99E-05 

Hazud Index 

l.ZSE+Ol 

1.98E+01 

3.19E+02 

I = An toxicity dues wcrc extracted from “PCData Bue: Screening Benchmarks for Ecological Risk Assessment (ntised December 1994)” 

Environmental Scienccs Won, Health Sciences Research Division, ORNL. 

b = NOAEL -NO Advcrse Eff~~ts h l 

= Hazard Quotients arc ~Ntless 

#N/A or - = not able to quantify because transfer factor or toxicological bcnchmuk wan unavailable 

Bold Value indicated huud quotient or hupd mdcx h &!mater than I.

Table 6.31. Ecological hazard quotients for the piscivore (Kingfisher) associated with surface water in 

the unnamed tributary of Big Bayou Creek at PGDP, WAG 7, C-746-K Sanitary Landfill (SWMU 8) 

Chemical 

Fish Kingfisher Benchmark 

Rcpresentrt ve ncentrrtion BCF for Fish' Hazard Quotient 

im$r Concentration (waterIb 

Aluminum I .43E+02 O.OOE+OO O.OOE+OO 

Antimony 

Barium 

Beryllium 

Cadmium 

Calcium 

Chloride 

Chromium 

Cobalt 

Copper 

Iron 

Lead 

Magnesium 

Manganese 

Mercury 

Nickel 


Potassium 

Ruthenium 

Silicon 

Sodium 

Strontium 

Sulfate 

Tantalum 

Thallium 

Tungsten 

Vanadium 

Zinc 

Zirconium 

I, I-Dichloroethane 

5.468-02 

8.44E-01 

6.268-02 

2.9OE-03 

7.338+01 

I .20E+O I 

7.00E-02 

I .00E+00 

5.57E-02 

9.748+02 

6.91E+00 

5.698+01 

8.59E+Ol 


9.99E-01 


6.13E+00 

l.OOE+OO 

3.89E+Ol 

3.57E+OI 

l.OOE+OO 

5.06E+02 

I .00E+00 

8.39E-0 I 

l.OOE+OO 

1.22E+00 

1.93E+00 

I .00E+00 


l.OOE+OO 


2.00E+00 

5.00E+OI 

3.00E+02 

2.1 OE+O2 

3.00E+02 


6.30E+04 

I .00E+02 

I .OOE+O2 

1.00E+04 

I .OOE-02 

I .00E+03 

O.OOE+OO 

5.46E-02 

3.38E+00 

1.25E-OI 

1.45E-01 

3.00E+02 

1. I7E+OI 

2.07E+03 

3,44E+04 

2.65E+Ol 

9.998+01 

3.578+03 

8.39E+03 

I .22E-02 

I .93E+03 

O.OOE+OO 

2.408-02 l.lOE+OJ

Table 6.31. Ecological hazard quotients for the piscivore (Kingfisher) associated with surface water in the 

unnamed tributary of Big Bayou Creek at PGDP, WAG 7, C-746-K Sanitary Landfill (SWMU 8) (continued) 

Chemical 

Fish Kingfisher Benchmark 

RepresentatpgJijmcentration BCF for Fish' Conecntration 

m 

(water)b 

Hazard Quotient 

I, I-Dichloroethene 5.278-03 7.00E+00 3.698-02 

1,2-Dichloroethenc 5.50E-02 7.00E+00 3.858-01 

Acetone 5 SOE-02 2.00E-01 I. IOE-02 

Trichloroethene 2.10E-03 1.70E+OI 3.57E-02 

Xylene 3.408-03 

bis(2-Ethylhcxyl)phthalate 2.00E-03 3. I OE+02 6.20E-0 I 2.228+00 2.79E-01 

cis- I ,2-Dichloroethene 4.21 E-02 

trans-I .2-Dichloroethene 4.98843 7.00E+00 3.49E-02 

Hazard Index 

1.10E+O3 

Bold value indicates hazard quotient or hazard index is greater than 1 

- = not able to quantify because transfer factor or benchmarks were unavailable 


a = bioconcentration factors were extracted from "Relative Toxicity Estimates and Bioaccumulation Factors for the Defense Priority Model", 


b = Benchmark values were extracted from "PC-Data Base: Screening Benchmarks for Ecological Risk Assessment (revised December 1994).

Table 6.32. Ecological hazard quotients* for wildlife receptors associated with surface water in the 

unnamed tributary of Big Bayou Creek at PGDP, WAG 7, C-746-K Sanitary Landfill (SWMU 8) 

Vole Vole Hazard Mouse 

Chemical Re reseptat've hh~se HQ Shrew Benchmark' Shrew HQ Deer Benchmark' Deer HQ 

Conccktratlon [ md) Benchmark' Quotient (HQ) Benchmark' 

Aluminum I .43E+02 1.25E+OI l.lSE+OI 7.13E+00 2.01E+01 I. I OE+OI 1.30E+01 2.45E+00 5.843+01 

Antimony 

8.08E-01 6.768-02 4.628-01 

I. 188-01 7.14E-01 7.65E-02 

I .59E-01 

3.438-01 

Barium 

7.90E+OI I ,078-02 4.528+01 1.878-02 6.998+01 I .21 E-02 

I .55E+OI 

5.44E-02 

Beryllium 

9.60E+00 6.528-03 5.488+00 I. 148-02 8.488+00 7.38E-03 

I .88E+00 

3.32E-02 

Cadmium 

1.24E+00 2.35843 7.068-0 I 4.11E-03 1.09E+00 2.658-03 2.43E-01 

1.19E-02 

Calcium 

Chloride 

Chromium 

Cobalt 

Copper 

Iron 

Lead 

Magnesium 

Manganese 

Mercury 

Nickel 

Phosphorus (PI 

Potassium 

Ruthenium 

Silicon 

Sodium 

Strontium 

Sulfate 

Tantalum 

Thallium 

Tungsten 

Vanadium 

Zinc 

Zirconium 

I ,I-Dichloroethane 

I, I -Dichlorocthene 

5.468-02 

8.44E-01 

6.268-02 

2.908-03 

7.338+01 

I .20E+OI 

7.008-02 

I .00E+00 

5.578-02 

9.748+02 

6.91E+00 

5.698+0 I 

8.598+0 I 


9.99E-0 I 

4. I7E+00 

6.13E+00 

I .00E+00 

3.898+01 

3.578+01 

I .00E+00 

5.068+02 

I .00E+00 

8.398-0 1 

l.OOE+OO 

I .22E+OO 

1.93E+00 

I .00E+00 


5.278-03 

2.4 IE+02 

I. 16E+02 

1.28E+03 

9.30E-02 

5.82E+02 

3.82E+03 

I .09E-01 

2.77E+OO 

2.338+03 

I. 12E+OI 


2.3 I E-04 

5.948-02 

6.71E-02 


I .72E-03 

2.628-04 

7.70E+00 

4.4 I 8-01 

8.308-04 

8.90E-02 

1.2 I E-05 

I .38E+02 

6.65E+01 

7.318+02 

5.30E-02 

3.32E+02 

2. I8E+03 

6.208-02 

1.58E+00 

1.33E+03 

6.42E+00 

2.498+02 


1.04E-01 

1.188-01 

7.928-03 

3 .O I E-03 


I .35E+01 

7.728-01 

1.458-03 

1 S6E-0 1 

2.1 IE-05 

2.338+02 

1.03E+02 

1. I38+03 

8.208-02 

5.14E+02 

3.38E+03 

9.60E-02 

2.458+00 

2.06E+03 

9.93E+00 

3.86E+02 

2.628-04 

6.72E-02 

7.598-02 

5.12E-03 

I .94E-03 

2.96E-04 

8.74E+00 


9.38E-04 

1.01E-01 

1.378-05 


2.288+01 

2.5 I E+02 

1.80E-02 

I. I4E+02 

7.5 OE+02 

2. I OE-02 

5.43E-01 


2.2OE+OO 

8.56E+0 1 

I. I8E-03 

3.03E-01 

3.428-01 

2.33 E-02 

8.768-03 

1.338-03 


2.25E+00 



6. I6E-05

Table 6.32. Ecological hazard quotients* for wildlife receptors associated with surface water in the 

unnamed tributary of Big Bayou Creek at PGDP, WAG 7, C-746-K Sanitary Landfill (SWMU 8) (continued) 

Chemical 

Vole Vole Hazard Mouse 

Re rescotat ve Mouse HQ Shrew Benchmark' Shrew HQ Deer Benchmark' Deer HQ 

COnC&tlOn bfl) Benchmark' Quotient (HQ) Benchmark' 

I ,2-Dichloroethene 5.508-02 2.928+02 1.888-04 I .678+02 3.308-04 2.588+02 2. 138-04 5.738+01 9.608-04 

Acetone 5.50E-02 1.458+02 3.788-04 8.31E+01 6.628-04 2.858+01 1.938-03 

Trichloroethene 2. I OE-03 4.528+00 4.648-04 2.598+00 8. I2E-04 4.008+00 5.25E-04 8.88E-01 2.368-03 

Xylene 3.408-03 I .33E+OI 2.558-04 7.61E+00 4.478-04 I. 18E+OI 2.898-04 2.61E+00 I ,308-03 

bis(2-Ethylhexyl)phthalate 2.00E-03 I. 18E+02 1.698-05 6.778+01 2.958-05 I .O5E+O2 1.91E-05 2.32E+OI 8.608-05 

cis- I ,2-Dichloroethene 4.218-02 

trans-I .2-Dichloroethcne 4.98843 

Hazard Index 1.99E+01 3.49E+O1 2.26E+01 l.O2E+O2 

Bold value indicates hazard quotient or hazard index is greater than I 

- = not able to quantify because transfer factor or benchmarks were unavailable 


a = All toxicity values were extracted from "PC-Data Base: Screening Benchmarks for Ecological Risk Assessment 

(revised December 1994), Environmental Sciences Division, Health Sciences Research Division, ORNL

I 

Table 6.31. Estimated radiation doses' (uCy/h) to aquatic organisms exposed to radionuclides in surface water and sediment 

at WAG 1 SWMU 38. 

WAG 1, SWMU 38, Ditcb 1 - SUrfaCC water and sediment 

Sediment RME (pCUg) SurLce water RME (pCi/L) 

Total dose 

Radionuclide invert. fish invert. fish Small insects L8rge insects Small fish . 

Gross Alpha 8.338+00 8.33E+OO I. I5E+OO 1.15E+OO na na na 

Gross Beta 1.09E+01 1.09E+O I 6.18E+00 6.18E+00 na na na 

Technetium-99 2.31E+00 2.31 E+OO 3.88E+00 3.88E+00 I .68E-04 1.688-04 1.688-04 

Uranium-234 2. I4E+00 2.14E+00 9.30E-01 9.30841 1.928-02 I .928-02 I .928-02 

Uranium-235 5.00E-02 5.00E-02 8.00E-02 8.00E-02 I S9E-03 I .59E-03 1.568-03 

Uranium-238 2.61E+00 2.61E+00 I .04E+OO 1.04E+OO 1.898-02 1.89E-02 1.898-02 

Total 398-02 3.998-02 3.988-02 

WAG 1, SWMU 38, Ditch 2 -Surface water and sediment 

Sediment RME (pCVg) Surface water RME (pCVL) Total dose 

Radionuclide invert. fish invert. fish Small insects Lame insects Small fish 

Gross Alpha 9.90E+00 9.90E+00 4.9 I E+01 4.91E+OI na na na 

Gross Beta 2.10E+01 2.1 OEM 1 3 .O 1 E+O 1 3.01E+OI na na na 

Neptunium-237 O.OOE+OO O.OOE+OO 3.40E-01 3.40E-01 2.11E-02 2.11E-02 2. I 1 E-02 

Plutonium-238 0.00E+00 O.OOE+OO 2.00E-01 2.OOE-0 I I .43E-02 1.438-02 1.438-02 

Plutonium-240 O.OOE+OO O.OOE+OO 4.00E-02 4.00E-02 2.688-03 2.688-03 2.688-03 

Plutonium-242 O.OOE+OO O.OOE+OO 2.00E-02 2.OOE-02 I .27E-03 1.278-03 . 1.278-03 

Technetium-99 3.12E+OO 3.12E+00 2.25E+00 2.25E+OO 9.72845 9.728-05 9.72E-05 

Thorium-228 0.00E+00 0.00E+00 I .60E-01 1.60E-01 3.748-02 3.74E-02 3.748-02 

Thorium-230 O.OOE+OO 0.00E+00 I .80E-01 1.80E-01 3.648-02 3.648-02 3.64E-02 

Thorium-232 O.OOE+OO 0.00E+00 7.00E-02 7.00E-02 I .21 E-02 I .2 I 8-02 1.2 I E42 

Uranium-234 I .44E+00 I .44E+OO 1.22E+00 1.22E+00 2.528-02 2.528-02 2.528-02 

Uranium-235 1.00E-01 1.00E-01 8.00E-02 8.00E-02 1.658-03 I .658-03 1.598-03 

Uranium-238 2.07E+OO 2.07E+00 I .50E+00 1.5OE+OO 2.738-02 2.728-02 2.72E-02 

Total 

1.79E-01 1.79E-01 1.798-01 

'Total doses presented are sum of internal and external exposures estimated following Blaylock et al. (1993). Internal exposures were 

insignificant relative to external exposures; therefore, total doses (uGyh) were similar for all groups. 

na = Gross alpha and beta doses were not estimated because specific decay energies are not applicable.

Table 6.32. Estimated internal, external, and total radiation doses (radslyr) from surface soil for 

wildlife receptors at WAG 1 SWMU 38. 

Surface soil 

Meadow vole Short-tailed shrew White-footed mouse 

Radionuclide RME' Internal External Total Internal External Total Internal External Total 

Neptunium237 1.38E+00 1.96E-08 8.84E-04 8.84E-04 1.49E-07 8.84E-04 8.84E-04 1.01E-08 8.84E-04 8.84E-04 

Plutonium-238 1.37E-01 1.72E-11 4.63E-06 4.63E-06 1.67E-10 4.63E-06 4.63E-06 8.45E-12 4.63E-06 4.63E-06 

Plutonium-239 8.00E-02 9.40E-12 1.19E-06 1.19E-06 9.15E-11 1.19E-06 1.19E-06 4.62E-12 1.19E-06 1.19E-06 

Plutonium-240 l.lOE-01 1.30E-11 3.55E-06 3.55E-06 1.26E-10 3.55E-06 3.55E-08 6.37E-12 3.55E-06 3.55E-06 

Plutonium242 1.33E-02 1.49E-12 3.58E-07 3.58E-07 1.45E-11 3.58E-07 3.58E-07 7.31E-13 3.58E-07 3.58E-07 

Technetium99 3.48E+00 2.45E-10 0.00E+00 2.45E-10 7.70E-12 0.00E+00 7.70E-12 1.48E-10 O.OOE+OO 1.48E-10 

Thorium-228 1.21E+00 1 .!%E49 7.45E-05 7.46E-05 1.46E-08 7.45E-05 7.46E-05 7.75E-10 7.45E-05 7.46E-05 

Thorium230 1.59E+00 1.77E-09 4.60E-05 4.60E-05 1.65E-08 4.60E-05 4.60E-05 8.79E-10 4.60E-05 4.60E-05 

Thorium-232 1.34E+00 1.28E-09 3.33E-05 3.33E-05 1.2OE-08 3.33E-05 3.33E-05 6.36E-10 3.33E-05 3.33E-05 

Uranium234 l.l7E+Ol 4.17E-08 3.78E-04 3.78E-04 5.14E-07 3.78E-04 3.78E-04 7.34E-08 3.78E-04 3.78E-04 

Uranium235 1.12E+00 3.85E-09 3.22E-03 3.22E-03 4.74E-08 3.22E-03 3.22E-03 6.76E-09 3.22E-03 3.22E-03 

Uranium-238 1.37E+01 4.30E-08 3.48E-04 3.48E-04 5.30E-07 3.48E-04 3.48E-04 7.56E-08 3.48E-04 3.48E-04 

Total 1.13E-07 4.99E-03 4.99E-03 1.28E-06 4.99E-03 4.99E-03 1.68E-07 4.99E-03 4.99E-03 

'RME = Reasonable maximum exposure in pCi/g. 

na = Gross alpha and beta doses were not estimated because specific decay energies were not applicable.

na 

Table 6.33. Estimated radiation doses' (uGy/h) to aquatic organisms exposed to radionuclides in surface water and sediment 


WAG 1, SWMU 100, Ditch 1 - Surface water and sediment 

Sediment RME (pCi/g) Surface water RME (pCin) Total dose 

Radionuclide invert. fish invert. fish Small insects Large insects Small fish 

Gross Alpha 9.13E+00 9.13E+00 3.96E+00 3.96E+00 0.00E+00 O.OOE+OO O.OOE+OO 

Gross Beta 1.87E+O 1 1.87E+OI 6.99E+00 6.99E+00 0.00E+00 O.OOE+OO O.OOE+OO 

Technetium-99 1.45E+00 1.45E+00 2.06E+OO 2.06Ei-00 8.89E-05 8.89E-05 8.89E-05 

Uranium-234 1.12E+00 1.12E+00 1.16E+00 1.16E+00 2.39E-02 2.39E-02 2.39E-02 

Uranium-235 5.00E-02 5.00E-02 6.00E-02 6.00E-02 1.21 E-03 1.20E-03 1.17E-03 

Uranium-238 1.27E+OO 1.27E+00 1.53E+00 1.53Ei-00 2.78E-02 2.788-02 2.78E-02 

Total 5.30E-02 5.30E-02 5.30E-02 

WAG 1, SWMU 100, Ditch 2 -Surface water and sediment 

Sediment RME (pcilg) Surface water RME (pCin) Total dose 


Gross Alpha 1.43E+01 1.43E+01 7.628+00 7.62E+00 na na na 

Gross Beta 2.30E+O 1 2.30E+01 1. I5E+OI l.ISE+Ol na na ~ 

Technetium-99 2.29E+00 2.29E+00 4.898+00 4.89E+00 2.1 1 E-04 2.1 1 E-04 2.1 IE-04 

Uranium-234 3.74E+00 3.74E+00 5.13E+00 5.13E+00 1.06E-01 1.06E-01 1.06E-01 

Uranium-235 1.35E+00 1.35E+00 2.348+00 2.34E+00 4.63E-02 4.63E-02 4.54E-02 

Uranium-23 8 4.08E+00 4.08E+00 9.498+00 9.49E+00 1.72E-01 1.72E-01 I .72E-01 

Total 3.25E-0 1 3.25E-01 3.248-0 1 

'Total doses presented are sum of internal and external exposures estimated following Blaylock et al. (1 993). Internal exposures were 

insignificant relative to external exposures; therefore, total doses (uGyh) were similar for all groups. 

na = Gross alpha and beta doses were not estimated because specific decay energies are not applicable.

Table 6.34. Estimated internal, external, and total radiation doses (radslyr) from surface soil for 


Surface soil 



Gross Alpha 1.31 E+Ol na na na na na na na na na 

Gross Beta 

Neptunium237 

Plutonium-238 

Plutonium-240 

Technetium-99 

Thorium228 

Thorium-230 

Thorium-232 

Uranium-233/234 

Uranium234 

Uranium-235 

Uranium-238 

Total 

2.06E+Ol 

2.00E-02 

1.60E-03 

2.70E-02 

8.7OE-01 

1.18E+00 

1.31E+00 

1.10E+00 

1.45E+00 

1.82E+00 


1.78E+00 

na 

2.84E-10 

2.01 E-1 3 

3.18E-12 

6.12E-11 

1.52E-09 

1 A6E-09 

1.05E-09 

5.22E-09 

6.49E-09 

1.46E-09 

5.59E-09 

2.31E-08 

na 

1.28E-05 

5.41 E-08 

8.72E-07 

O.WE+W 

7.27E-05 

3.79E-05 

2.73E-05 

3.55E-05 

5.88E-05 

1.22E-03 


1.51E-03 

na 

1.28E-05 

5.41 E-08 

8.72E-07 

6.12E-11 

7.27E-05 

3.79E-05 

2.73E-05 

3.55E-05 

5.88E-05 

1.22E-03 


1.51E-03 

na 

2.16E-09 

1.95E-12 

3.lOE-11 

1.93E-12 

1.42E-08 

1.36E-08 

9.81 E-09 

6.43E-08 

8.00E-08 

1 J30E-08 

6.88E-08 

2.71E-07 

na 

1.28E-05 

5.41E-08 

8.72E-07 

0.00E+00 

7.27E-05 

3.79E-05 

2.73E-05 

3.55E-05 

5.88E-05 

1.22E-03 


1.51E-03 

na 

1.28E-05 

5.41 E-08 

8.72E-07 

1.93E-12 

7.27E-05 

3.79E-05 

2.73E-05 

3.55E-05 

5.89E-05 

1.22E-03 


1.51E-03 

na 

1.46E-10 

9.07E-14 

1.56E-12 

3.70E-11 

7.56E-10 

7.24E-10 

5.22E-10 

9.17E-09 

'1.14E-08 

2.56E-09 

9.82E-09 

3.52E-08 

na 

1.28E-05 

5.4lE-08 

8.72E-07 

O.OOE+OO 

7.27E-05 

3.79E-05 

2.73E-05 

3.55E-05 

5.88E-05 

1.22E-03 


1.51E-03 

na 

1.28E-05 

5.41 E-08 

8.72E-07 

3.70E-11 

7.27E-05 

3.79E-05 

2.73E-05 

3.55E-05 

5.88E-05 

1.22E-03 


1.51E-03 

I 

RME = Reasonable maximum exposure in pCi/g. 


Table 6.35. Estimated internal, external, and total radiation doses (raddyr) from surface soil for 

wildlife receptors at WAG I SWMU 136. 

Surface soil 



Gross Alpha ' 5.63E+00 na na na na na na na na na 

Gross Beta 6.42E+W na na na na na na na na na 

Technetium-99 9.70E-01 6.83E-11 O.OOE+W 6.83E-11 2.15E-12 O.OOE+OO 2.15E-12 4.12E-11 O.OOE+OO 4.12E-11 

Uranium234 8.30E-01 2.96E-09 2.68E-05 2.68E-05 3.65E-08 2.68E-05 2.68E-05 5.20E-09 2.68E-05 2.68E-05 

Uranium-235 4.00E-02 1.37E-10 1.15E-04 1.15E-04 1.69E-09 1.15E-04 1.15E-04 2.4lE-10 1.15E-04 1.15E-04 

Uranium-238 8.70E-01 2.73E-09 2.21E-05 2.21E-05 3.36E-08 2.21E-05 2.21E-05 4.80E-09 2.21E-05 2.21E-05 

Total 5.90E-09 1.64E-04 1.64E-04 7.18E-08 1.64E-04 1.64E-04 1.03E-08 1.64E-04 1.64E-04 

I 

RME = Reasonable maximum exposure in pCVg. 




Surface soil 



Gross Alpha 9.83E+00 na na na na na na na na na 

Gross Beta 1.88E+Ol na na na na na na na na na 

Technetium-99 5.lOE-01 3.59E-11 O.WE+W 3.59E-11 1.13E-12 O.OOE+W 1.13E-12 2.17E-11 O.WE+OO 2.17E-11 

Uranium-234 1 .lOE+OO 3.93E-09 3.55E-05 3.55E-05 4.83E-08 3.55E-05 3.56E-05 6.90E-09 3.55E-05 3.55E-05 

Uranium235 1.40E-01 4.8lE-10 4.03E-04 4.03E-04 5.92E-09 4.03E-04 4.03E-04 8.45E-10 4.03E-04 4.03E-04 

Uranium-238 1.50E+00 4.71E-09 3.8lE-05 3.81E-05 5.80E-08 3.8lE-05 3.8lE-05 8.27E-09 3.8lE-05 3.81E-05 

Total 9.15E-09 4.76E-04 4.76E-04 1.12E-07 4.76E-04 4.76E-04 1.60E-08 4.76E-04 4.76E-04 



Table 6.37. Estimated internal, external, and total radiation doses (rads/yr) from surface soil for 



Surface soil 


Gross Alpha 1.26E+Ol na na na na na na na na na 


Technetium-99 1.20E+00 8.44E-11 0.00E+00 8.44E-11 2.66E-12 O.OOE+OO 2.66E-12 5.lOE-11 O.OOE+OO 5.10E-11 

Uranium-233Q34 1.22E+00 4.39E-09 2.98E-05 2.98E-05 5.41E-08 2.98E-05 2.99E-05 7.72E-09 2.98E-05 2.98E-05 

Uranium234 1.07E+00 3.82E-09 3.46E-05 3.46E-05 4.70E-08 3.46E-05 3.46E-05 6.71 E-09 3.46E-05 3.46E-05 

Uranium-235 5.00E-02 1.72E-10 1.44E-04 1.44E-04 2.1 lE-09 1.44E-04 1.44E-04 3.02E-10 1.44E-04 1.44E-04 

Uranium-238 1.59E+00 4.99E-09 4.04E-05 4.04E-05 6.15E-08 4.04E-05 4.04E-05 8.77E-09 4.04E-05 4.04E-05 

Total 1.35E-08 2.49E-04 2.49E-04 1.65E-07 2.49E-04 2.49E-04 2.35E-08 2.49E-04 2.49E-04 

I 

RME = Reasonable maximum exposure in pCi/g. 



wildlife receptors at WAG 7 SWMU 134. 

Surface soil 



Gross Alpha 7.78E+00 na na na na na na na na na 


Technetium-99 9.60E-01 6.76E-11 0.00E+00 6.76E-11 2.12E-12 O.OOE+OO 2.12E-12 4.08E-11 O.OOE+OO 4.08E-11 

Uranium-234 8.40E-01 3.00E-09 2.71E-05 2.71 E-05 3.69E-08 2.71 E-05 2.72E-05 5.27E-09 2.71E-05 2.71 E-05 

Uranium-235 7.M)E-02 2.40E-10 2.01E-04 2.01E-04 2.96E-09 2.01E-04 2.01E-04 4.22E-10 S2.01E-04 2.01E-04 

Uranium-238 l.l4E+OO 3.58E-09 2.89E-05 2.89E-05 4.41E-08 2.89E-05 2.90E-05 6.29E-09 2.89E-05 2 90E-05 

Total 6.88E-09 2.57E-04 2.57E-04 8.40E-08 2.57E-04 2.57E-04 1.20E-08 2 57E-04 2.57E-04 


na = Gross alpha and beta doses were not estimated because specific decay energies were not applicable. 

$r I

3.20E-02. 

Table 6.39. Estimated radiation doses' (uGylh) to aquatic organisms exposed to radionuclides in surface water and sediment 


WAG 7, SWMU 8, Bayou Creek - Surface water 

Sediment RME (pCVg) Surface water RME (pCuL) Total dose 


Gross Alpha 7.928+00 7.04E+00 9.00E+00 1.21 E+OO na na na 

Gross Beta I .67E+01 1.16E+OI 1.22E+02 7.33E+00 na na na 

Technetium-99 7.968-01 7.968-01 3.OOE+OI I .66E+01 1.30E-03 1.30E-03 7.17E-04 

Uranium-233034 9.1 OE-0 I 9.10E-01 4.50E-0 I 4.50E-01 9.398-03 9.388-03 9.388-03 

Uranium-234 I. IOE+00 8.61 E-01 3.20E-01 2.978-01 6.618-03 6.61 E-03 6.138-03 

Uranium-235 6.00E-02 6.00E-02 9.608-02 9.608-02 1.90E-03 I .90E-03 1.87E-03 

Uranium-238 8.90E-01 8.43E-01 2.16E-01 2.16E-01 3.93E-03 3.938-03 3.92E-03 

Total 2.318-02 2.31842 2.208-02 

WAG 7, SWMU 8, Ieacbate 

Sediment RME (pCVg) Surface water RME (pCVt) Total dose 


Gross Alpha nd nd 6.51E+02 3.47EMl na na na 

Gross Beta nd nd 3.00E+02 1.78E+01 na na na 

Neptunium-237 nd nd 5.30E-01 5.30E-01 3.28EE-Q2r. 

Plutonium-238 nd nd I .30E-01 I .30E-01 9.28E-b3 2 ' 

I 3.28E-02 

'9.28E-03 _-:-_9.28E-O3 

Plutonium-240 nd nd 7.00E-02 7.00E-02 4.69843 "E4.69E-03 '4.69843 I 

Plutonium-242 nd nd 2.00E-02 2.00E-02 1.27E-03 1.278-03 . 1.278-03 

Technetium-99 nd nd I .30E+OI 1.13E+OI 5.61844 5.61E-04 4.888-04 

Thorium-228 nd nd 4.30E-01 4.30E-01 1 .OIE-OI 1.01E-01 1.01 E-01 

Thorium-230 nd nd 5.80E-01 5.80E-01 1.17E-01 1. I7E-01 1.17E-01 

Thorium-232 nd nd 4.90E-01 4.90E-01 8.50842 8.508-02 8.508-02 

Uranium-234 nd nd 6.82E+00 6.82E+00 1.41 E-01 1.41 E-01 1.41 E-01 

Uranium-235 nd nd 4.30E-01 4.30E-01 8.20E-03 8.20E-03 8.20E-03 

Uranium-238 nd nd 7.47E+OO 7.478+00 1.36E-01 1.36E-01 1.36E-01 

Total 6.368-0 1 6.368-01 6.368-01 

'Total doses presented arc sum of internal and external exposures estimated following Blaylock et al. (1993). Internal 

exposures were insignificant relative to external exposures; therefore, total doses (uGylh) were similar for all groups. 

na = Gross alpha and beta doses were not estimated because specific decay energies arc not applicable. 

nd =No data available.

Table 6.40. Estimated internal, external, and total radiation doses (rads/yr) from surface soil for 


Meadow vole Short-tailed shrew White-footed m owe 

Surface soil 

Radionuclide RME Interoal External Total Internal External Total Internal External Total 

Gross Alpha 9.90E+00 na na na na na na ma na na 

Gross Beta 

Neptunium-237 

Plutonium-239 

Technetium-99 

Thorium-230 

Uranium-234 

Uranium235 

Uranium-238 

1.83E+Ol 

2.00E+00 

-2.00E+00 

8.79E+00 

5.20E+02 

3.74E+01 

8.33E-01 

5.25E+01 

na 

2.84E-08 

-2.35E-10 

6.19E-10 

5.79E-07 

1.33E-07 

2.86E-09 

1.65E-07 

na 

1.28E-03 

-2.97E-05 

0.00E+00 

1.50E-02 

$.21E-03 

2.40E-03 

2.33E-03 

na 

1.28E-03 

-2.97E-05 

6.19E-10 

1.50E-02 

1.21E-03 

2.40E-03 

1.33E-03 

na 

2.16E-07 

-2.29E-09 

1.95E-11 

5.40E-06 

1 ME-06 

3.52E-08 

2.03E-06 

na 

1.28E-03 

-2.97E-05 

0.00E+00 

1 SE-02 

1.21E-03 

2.4OE-03 

1.33E-03 

na 

1.28E-03 

-2.97E-05 

1.95E-11 

1.5iE-02 

I.stE*’ 

2.4OE-03 

1.34E-03 

na 

1.46E-08 

-1.t6E-10 

3.74E-10. 

2.87E-07 

2.34E-07 

5.03E-09 

2.90E-07 

na 

1.28E-03 

-2.97E-05 

O.oQE+OO 

1.5oE-02 

l.WE-03 

2.40E-03 

1.33E-03 

na 

1.28E-03 

-2.97E-05 

3.74E-10 

1.5OE-02 

1.21 E-03 

2.40E-03 

1.33E-03 

Total 9.09E-07 2.12E-02 2.12E-02 9.33EQQ 2.12E-02 2.12E-02 8.31E-07 2.12&0% 2.12E-02 

1 

‘WE = Reasonable maximum exposure in pCVg.’ 

na = Gross alpha and beta doses were not estimated because specific decay energies were not applicable.

Volume 4. Appendixes L, Section L.7, and M Resource ...

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