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DOE/ORO/2327 Oak Ridge Reservation Annual Site Environmental ...

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<strong>Annual</strong> <strong>Site</strong> <strong>Environmental</strong> Report<br />

Table 3.22. Analytical results from sampling performed at storm water outfall 490<br />

Gross alpha<br />

(pCi/L)<br />

Gross beta<br />

(pCi/L)<br />

U-233/234<br />

(pCi/L)<br />

U-235/236<br />

(pCi/L)<br />

U-238<br />

(pCi/L)<br />

Tc-99<br />

(pCi/L)<br />

Total U<br />

(µg/L)<br />

Screening level 15 50 20 24 24 4000 31<br />

July 2001 5 52 1.22 U 0.24 U a 0 U 17 1 U<br />

January 2002 17.3 81.5 2.01 0.05 U 0.38 60.9 2.75 U<br />

August 2005 2.45 J 7 1.57 No data 0.44 108 No data<br />

February 2007 9.71 22.8 3.32 No data 0.9 28.6 U No data<br />

October 2008 7.57 29.6 0.82 No data -0.08 U 38.5 –0.18 U<br />

February 2009 10.6 57.1 No data 0.079 0.41 95.4 1.3<br />

a U—analyte not detected in sample.<br />

Gross alpha radiation was detected in the discharges from storm water outfalls 160, 292, and 350 at<br />

levels that exceeded the screening level for gross alpha activity of 15 pCi/L (Tables 3.14, 3.20, and 3.21).<br />

Results for gross alpha radiation collected at these locations since 2001 indicate that the gross alpha<br />

radiation results collected during this portion of the 2009 SWPP Program sampling effort are within the<br />

historical range.<br />

Gross beta radiation was detected in the discharges from storm water outfalls 160, 350 and 490 at<br />

levels which exceed the MCL of 50 pCi/L for this analyte (Tables 3.14, 3.21 and 3.22). Results for gross<br />

beta radiation collected at these location since 2001 indicate that the gross beta radiation results collected<br />

during this portion of the 2009 SWPP Program sampling effort are within the historical range.<br />

Uranium 233/234 was detected in the discharges from storm water outfalls 160, 292, and 350 at levels<br />

which exceed the 4% of DCG level of 20 pCi/L for this radionuclide (Tables 3.14, 3.20 and 3.21). Results<br />

for U-233/234 collected at these locations since 2001 indicate that the U-233/234 results collected during<br />

this portion of the 2009 SWPP Program sampling effort are within the historical range.<br />

Uranium 238 was detected in the discharges from storm water outfalls 160 and 350 at levels which<br />

exceed the 4% of DCG level of 24 pCi/L for this radionuclide (Tables 3.14 and 3.21). Results for U-238<br />

collected at these locations since 2001 indicate that the U-238 levels in data collected during this portion<br />

of the 2009 SWPP Program are within the historical range.<br />

Total uranium was detected in the discharges from outfalls 160, 292 and 350 at levels which exceeds<br />

the screening level of 31 µg/L for this analyte (Tables 3.14, 3.20 and 3.21). Limited historical data for<br />

total uranium indicate that the total uranium level in data collected during this portion of the 2009 SWPP<br />

Program are within the historical range.<br />

3.5.1.5 Monitoring Conducted as Part of the Demolition of Building K-1035<br />

Building K-1035 was built in 1945 as a maintenance general stores warehouse. In the early 1960s it<br />

was converted to an instrument maintenance facility. Shop activities have included an instrument shop,<br />

metal cabinet fabrication, a photoelectroplating process, printed circuit board fabrication shop, acid<br />

cleaning area, line recorder cleaning, and pneumatic repair shop. To the south of the building are the K-<br />

1035 Acid Pits. These two pits, an acid pit and neutralization pit, received acid and solvent wastes from<br />

two dedicated instrument shops, the Printed Circuit Board Fabrication Facility and the Acid Cleaning<br />

Area, within the building. The process drains from the acid pit and the neutralization pit flow to a single<br />

catch basin that discharges to the storm drain 190 network. The Acid Cleaning Area operated from the<br />

early 1960s to 1985, and the Printed Circuit Board Fabrication Facility operated from the early 1960s to<br />

1977.<br />

In April 2009, work began on the demolition of Building K-1035 (Fig. 3.22). All materials that<br />

potentially contained asbestos, including siding, pipe insulation, roofing material, etc. were removed prior<br />

to general demolition using heavy equipment. The remainder of the building was demolished using heavy<br />

equipment. In June 2009, the building was reduced to rubble (Fig. 3.23). Final removal of building rubble<br />

East Tennessee Technology Park 3-41

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