Sediment Quality in Puget Sound Year 2 - Center for Coastal ...

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Appendix D. Table 1. Continued. 22 Dyes Inlet % % Very % Coarse Medium % Fine % Very Total % Stratum Sample Station solids3 % Gravel Coarse Sand Sand Sand Sand Fine Sand Sand % >2000 mni 2000-1000 nim 1000-500 mrn 500-250 rnm 250-125 mm 125-62.5 mni 2000-62.5 mni 62.5-3 23 Outer Elliott Bay 24 Shoreline Elliott Bay 25 Shoreline Elliott Bay 26 Shoreline Elliott Bay 27 Mid Elliott Bay
Appendix D. Table 1. Continued. % % Very % Coarse Medium % Fine % Very Total % Stratum Sample Station Solids" % Gravel Coarse Sand Sand Sand Sand Fine Sand Sand % >2000 nim 2000-1000 nim 1000-500 nini 500-250 rnm 250-125 rnm 125-62.5 mrn 2000-62.5 nim 62.5-3 2 8 189 1 63 0.2 0 1 9 36 3 0 76.2 Mid Elliott Bay 1 90 2 7 1 0.6 0 1 2 7 59 9 96.5 191 3 38 0.1 1 2 5 6 10 24.9 5 192 4 5 7 10.4 6 8 17 15 7 53.2 2 29 193 1 Mid Elliott Bay 194 2 195 3 196 4 3 0 114 4 West Harbor 197 1 Island 198 2 199 3 3 1 200 1 East Harbor Island 201 2 202* 3 I Organics included. Corrected for dissolved solids. Particle size intervals based on US Army Corps of Engineers and Wcntworth Soil Classification Systems. Â¥ Percent Solids measured according to Plum, 198 1. EPAICE-8 1-1. * Mean of three lab replicates. - - -
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National Status and Trends Program
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Sediment Quality in Puget Sound Yea
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Human Reporter Gene System (Cytochr
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List of Appendices Appendix A . Det
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Figure 10. Results of 1998 Microtox
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Figure 38. Central Puget Sound stat
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Table 14. Number of 1998 central Pu
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Table 34. Triad results for 1998 ce
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Abstract As a component of a three-
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tests; and 3% of the area in the cy
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Data from this central Puget Sound
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Project Background Introduction hi
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Considerable research has been cond
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toxicants in regions of Puget Sound
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This report includes a summary of t
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stations within each stratum were c
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jugs which had been washed, acid-st
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clean, filtered (0.45 um), Port Ara
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have been exposed to one or more of
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enforcement studies. Seven addition
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analyses will be reported elsewhere
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100 samples were compared to the up
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Correlations were determined for al
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Results A record of all field notes
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As a corollary to and verification
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to station 15 1, then decreased ste
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variance of the other tests with re
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espectively, and each station had 1
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exceeded state criteria and nationa
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assays, enzyme induction was very h
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Isomers of DDT and most PCB congene
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Total abundance of miscellaneous ta
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(i.e., increasing toxicity), there
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Triad Synthesis: A Comparison of Ch
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Stratum 6, in Puget Sound's central
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grain size, rather than the toxicit
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Eight samples collected along the s
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Inlet), 170- 17 1 (Dyes Inlet), 1 1
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The results in the amphipod tests p
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Human Reporter Gene System (Cytochr
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The highest concentrations of mixtu
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and Conner, 1980; Gray, 1982: Becke
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However, benthic data have been gen
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data for benzoic acid, 44 samples h
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Literature Cited Adams, D.A., J.S.
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California Department of Fish and G
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and vicinity. NOAA Tech. Memo. NOS
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Strait of Juan De Fuca Figure 1. Ma
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Figure 3a. Central Puget Sound samp
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Figure 3c. Central Puget Sound samp
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Figure 3e. Central Puget Sound samp
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I / Amphipod survival 0 not toxic s
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Figure 6. Summary of 1998 amphipod
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Amphipod survival 0 not toxic 0 sig
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Whidbey Rlsland Figure 14. Results
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Figure 16. Results of 1998 cytochro
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Seattle Figure 18. Results of 1998
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Figure 20. Sampling stations in Por
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1 6 0 Sinclair 1 9 Inlet ]\ 0 No Cr
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0 Rho = 0.928 o p < 0.0001 Sample 1
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0 10000 20000 30000 40000 50000 600
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Rho = -0.584 p < 0.0001 0 20 40 60
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Rho = 0.875 p < 0.0001 0 500 1000 1
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I 0 1 Stations lacking any signific
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0 Stations lacking any significant
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Table 1. Central Puget Sound sampli
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Table 2. Continued. Oxychlordane To
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Table 3. Chemistry Parameters: Labo
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Table 5. Benthic infaunal indices c
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Table 6. Continued. Stratum Locatio
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Table 6. Continued. Stratum Locatio
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Table 7. Continued. 100% pore water
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Table 7. Continued. 100% pore water
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Table 8. Results of MicrotoxTM test
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Table 8. Continued. ~icrotox~~ EC50
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Table 8. Continued. Microtox"" EC50
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Table 10. Spearman-rank correlation
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Table 12. Samples from 1998 central
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Table 13. Samples from 1998 central
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Table 13. Continued. Stratum, Sampl
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Table 14. Number of 1998 central Pu
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Table 14. Continued. - > ERMa > sQs
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Table 14. Continued. > E RM~ - > SQ
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Table 22. Total abundance, major ta
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Table 22. Continued. Annelida Arthr
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Table 22. Continued. Annelida Arthr
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Table 23. Continued. Central Basin
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Table 23. Continued. Stratum Sample
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if; c if; c Page 167
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Page 215 and 216: Table 35. Distribution of results i
Page 217 and 218: Table 37. Spatial extent of toxicit
Page 219 and 220: Table 39. Spatial extent of toxicit
Page 221: Appendix A Detected chemicals from
Page 224 and 225: Appendix A. Continued. SQS Chemical
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Page 240 and 241: Appendix B. Continued. Stratum Samp
Page 250 and 251: Appendix C. Continued. Tenip- Salin
Page 256 and 257: Appendix D. Table 1. Continued. % %
Page 260 and 261: Appendix D. Table 2. Total organic
Page 262 and 263: Appendix D. Table 2. Continued. Str
Page 272 and 273: Appendix D, Figure 1. continued. St
Page 274 and 275: Appendix D, Figure 1. continued. St
Page 279 and 280: Appendix E. 1998 Central Puget Soun
Page 281 and 282: Appendix E. Continued. Phylum Class
Page 297 and 298: Appendix F Percent taxa abundance f
Page 299 and 300: Appendix F. Percent taxa abundance
Page 303 and 304: 2 Â¥^ 2 ca so a * .0 cn 00 a 5 I
Page 305 and 306: Appendix G Infaunal taxa eliminated
Page 307 and 308: Aooendix R. Infaunal taxa eliminate
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Appendix H Triad data - Results of
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nine OJllIO,) JO % Sl! [L'A!AJIls p
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atuni. Sample, Location umber of ER
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Page 308
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Stratum, Sample. Location Number of
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a~i11*31~!~3! [OJ1UO,) JO % Sl! J31
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Appendix I. Ranges in detected chem
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Appendix I. Continued. 9(H)Carbazol
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Appendix I. Continued. Mercury Nick
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Appendix J SEDQUAL surveys for the
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Appendix J. Continued. Agency Name
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Appendix K. Continued. Chrysene Dib
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