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

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Appendix C. Continued. Tenip- Salinity erature 2 Stratum Station Sample Station Description (ppt) , (Oc) Sediment Type Sediment Color Sediment Odor and in % to 13 2 143 suburban 3 1 14.5 silt-clay olive over black strong sulfur to 00 13 3 144 suburban 3 1 14 silt-clay NR strong sulfur suburban 3 0 1.4 suburban 30 14 suburban 3 1 14 NR 32 13.5 suburban 3 1 14 suburban 31 12.5 suburban 3 1 12 suburban 3 1 13 suburban 3 1 12 suburban 3 1 13 suburban 3 1 14 suburban 3 0 13 suburban 3 0 12 suburban 30 12.5 urban 3 1 13 suburban 3 1 12 urban 3 1 12 urban 3 0 12 NR 3 0 13 suburban 3 0 13 urban 31 12.5 suburban 3 0 14 suburbanlresidential 3 1 14 suburban 3 1 13 suburban 3 1 13 suburban 3 0 13 suburban 30 13 urban 3 0 11 urban 30 11.5 urban 3 0 12 urban 3 1 13 urban 3 1 13 urban 3 0 14 urban 3 0 12 urban residential 3 0 13 sand silt-clay silt-clay sand shell silt-clay sand silt-clay silt-clay silty sand silt-clay sand sand sand sand sand plant frags cobbles gravel sand shell silt-clay silt-clay wood shell silt-clay wood silt-clay silt-clay silt-clay sand silty sand sandy silt clay sand silt-clay sandy silt clay silt-clay silt-clay slag pieces gravel sand very corse sand sand sand sand silty sand wood gray brown olive gray gray olive gray gray brown gray brown olive gray olive gray olivc gray gray gray brown gray brown brown brown brown black olivc olive over black olive over black olive gray gray olive gray gray gray NR gray brown olive gray olive brown olive gray olive gray gray brown gray brown gray gray gray gray black slight sulfur strong sulfur moderate sulfur moderate sulfur none none none NR NR NR NR none none none none strong sulfur strong sulfur moderate sulfur strong sulfur moderate sulfur strong sulfur none none strong sulfur NR strong sulf~ir strong sulfur none none none sulfur one grab only none none none petroleum strong
Appendix C. Continued. Temp-. Salinity erature Stratum Station Sample Station Description (ppt) (Oc) Sediment Type Sediment Color Sediment Odor and NR = not recorded RPD = redox potential depth urban urban urban urban urban urban urban urban urban urban urban urban urban urban urban urban urban urban urbanlindustrial urbanlindustrial urbanlindustrial urbanlindustrial urbanlindustrial urbanlindustrial urbanlindustrial urbanlindustrial urbanlindustrial NR silty sand silt-clay sand silt-clay wood sandy silt clay sandy silt clay wood sand wood plant frags sand shell plant frags silt clay sand silt clay silt-clay silt clay shell sand silt clay sand silt clay gravel sand sand silt clay sand silt clay sand silt clay silt clay silt clay sand silt clay sand silt clay wood sand silt clay NR silt clay silt clay sand silt clay sand silt clay silt clay wood gray brown gray gray brown gray brown gray black brown over gray olive gray gray brown brown over gray brown over gray none gray brown NR gray brown NR brown over gray none gray brown NR brown over dark olive NR brown brown gray gray black gray brown brown gray brown NR brown over black olive brown olive gray olive brown over black dark brown strong sulfur none none none none none NR none none NR NR NR NR NR NR NR NR NR NR NR moderate sulfur and NR
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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 208 and 209: is-
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 256 and 257: Appendix D. Table 1. Continued. % %
Page 258 and 259: Appendix D. Table 1. Continued. 22
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
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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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Page 3 16
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Page 3 18
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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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Page 327
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Appendix J SEDQUAL surveys for the
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Appendix J. Continued. Agency Name
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Page 338
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Appendix K. Continued. Chrysene Dib
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