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

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Table 38. Spatial extent of toxicity (km2 and percentages of total area) in microbial biolumines~ence tests performed with solvent extractsof sediments from 19 U. S. bays and estuaries. Microbial bioluminescence Survey areas Year No. of Total area Toxic area Pct. of area sampled sediment of survey (km2) toxic Choctawhatchee Bay 1994 St. Andrew Bay 1993 Apalachicola Bay 1994 Pensacola Bay 1993 Galveston Bay 1996 Sabine Lake 1995 Winyah Bay 1993 Long Island Sound 199 1 Savannah River 1994 Biscayne Bay 199511996 St. Simons Sound 1994 Boston Harbor 1993 Charleston Harbor 1993 Hudson-Raritan Estuary 199 1 Leadenwah Creek 1993 Delaware ~a~~ 1997 northern Puget Sound A 1997 Tampa Bay 199211 993 central Puget Sound 1998 Cumulative National estuarine average based upon data collected through: 01997 1215 7 160 2802.4 A Critical value of
Table 39. Spatial extent of toxicity (km2 and percentages of total area) in cytochrome P450 HRGS tests performed with solvent extracts of sediments from 8 U. S. bays and estuaries. Cytochrome P450 Cytochroine HRGS (>11.1 P450 HRGS (>3 7.1 pglg) Survey areas Year No. of Total Toxic PCT. of Toxic PCT. of sampled sediment area of area area area area samples survey (km2) toxic (km2) toxic (km2) northern Chesapeake Bay Delaware Bay central Puget Sound Sabine Lake northern Puget Sound Southern Cal. Estuaries Biscayne Bay, 1996 Galveston Bay Cumulative national estuarine averages based upon data collected through: - 1997 627 8023.5 1604.2 20.0 Page 197
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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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Page 169 and 170: Table 14. Continued. > E RM~ - > SQ
Page 171 and 172: Table 16. Spearman-rank correlation
Page 177 and 178: Table 22. Total abundance, major ta
Page 179 and 180: Table 22. Continued. Annelida Arthr
Page 181 and 182: Table 22. Continued. Annelida Arthr
Page 183 and 184: Table 23. Continued. Central Basin
Page 185 and 186: Table 23. Continued. Stratum Sample
Page 189 and 190: if; c if; c Page 167
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Page 208 and 209: is-
Page 215 and 216: Table 35. Distribution of results i
Page 217: Table 37. 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
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Page 260 and 261: Appendix D. Table 2. Total organic
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Appendix D, Figure 1. continued. St
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Appendix D, Figure 1. continued. St
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Appendix E. 1998 Central Puget Soun
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Appendix E. Continued. Phylum Class
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Appendix F Percent taxa abundance f
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Appendix F. Percent taxa abundance
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Page 279
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2 Â¥^ 2 ca so a * .0 cn 00 a 5 I
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Appendix G Infaunal taxa eliminated
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Aooendix R. Infaunal taxa eliminate
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Appendix H Triad data - Results of
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Page 292 nine
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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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Page 3 10
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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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