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

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station 168, as with two of the stations <strong>in</strong> S<strong>in</strong>clair Inlet, Apheloclzaeta sp. N1 was found <strong>in</strong> high<br />

~lu~nbers (1023) <strong>in</strong> a sl~allow station with a strong sulhr odor, although this station had lower<br />

percent f<strong>in</strong>es (35%) than those <strong>in</strong> S<strong>in</strong>clair Inlet (93% and 87%). Aphelochaeta sp. Nl was also<br />

found <strong>in</strong> sandy stations 166 and 167, but <strong>in</strong> much lower densities (29 and 100 <strong>in</strong>dividuals,<br />

respectively). Conversely, Alvania conzpacta was found <strong>in</strong> higher densities at the two sandy<br />

stations (79 and 193, respectively), and <strong>in</strong> lower numbers (35 <strong>in</strong>dividuals) at the silty sand<br />

station. Although there are similarities <strong>in</strong> the significant toxicity measures and <strong>in</strong>faunal <strong>in</strong>dices<br />

and species composition among station 168 and stations 161 and 164 <strong>in</strong> S<strong>in</strong>clair Inlet, the lack of<br />

significant cllemistry results does not provide a clear association among triad parameters at these<br />

stations. However, as was speculated <strong>for</strong> the data from S<strong>in</strong>clair Inlet, it is possible that other<br />

environmental measures suc11 as dissolved oxygen concentrations <strong>in</strong> the sediment pore water and<br />

overly<strong>in</strong>g waters may play a role <strong>in</strong> <strong>in</strong>flue~~c<strong>in</strong>g <strong>in</strong>faunal co~nmunity composition at this station.<br />

The three stations <strong>in</strong> stratum 22, Dyes Inlet (1 69- 17 1) (Figure 4 1 ), consisted of one station (1 69)<br />

with no significant toxicity results or elevated chemical concentrations, and two stations with<br />

both significant levels of chemical coi~tam<strong>in</strong>ation and toxicity results. The sample from station<br />

169, collected from 7m, was primarily sandy (8% f<strong>in</strong>es), had no significant toxicity results or<br />

elevated cl~emical concentrations, and displayed extremely high total abundance and species<br />

richness. The high total abundance (1 123 <strong>in</strong>dividuals) was due primarily to a large abundance of<br />

the polychaetes Phyllochaetopte~~~~s prolifica (455 <strong>in</strong>dividuals), Ci1-ceis sp. (240 <strong>in</strong>dividuals), and<br />

a small number of Apl~elochaeta sp. Nl (137 i11dividuals).<br />

Stations 170 and 17 1, located <strong>in</strong> approxi~nately 13.5m depths, both were co~nposed of a 11ig11<br />

percent silt clay (93 and 88% f<strong>in</strong>es, respectively), and both had dark olive gray or brown<br />

sediments with a strong sulfbr s~nell. Both stations had significant levels of clle~nical compounds<br />

(benzyl alcol~ol and either nickel or mercury), and displayed significant cytocllrome P450 HRGS<br />

toxicity results. These two stations shared 8 of 10 dom<strong>in</strong>ant species, <strong>in</strong>clud<strong>in</strong>g the same four<br />

species that dom<strong>in</strong>ated the stations <strong>in</strong> S<strong>in</strong>clair Inlet, the ciustaceans Pirznix~z schnzitti and<br />

E~/dorellci pacifica, the brittle star A~~zphio~iia ~~~~tica(uerie~rta complex, and the polychaete<br />

Aplieloc~zaeta sp. Nl. Similar to station 165 <strong>in</strong> S<strong>in</strong>clair Inlet, the crustacea and brittle stars<br />

dom<strong>in</strong>ated the two contam<strong>in</strong>ated and toxic stations <strong>in</strong> Dyes Inlet, wit11 a much-reduced number of<br />

Aphelochaeta sp. Nl present. As wit11 station 165, it is possible that tlle composition of the<br />

<strong>in</strong>faunal communities at these two stations, dom<strong>in</strong>ated by these four taxa, is a result of the<br />

relatively high contami~lation and toxicity <strong>in</strong> the sediments at these stations, <strong>in</strong>dicat<strong>in</strong>g triad<br />

support <strong>for</strong> classification of these stations as affected by pollution. It is also possible, however,<br />

that the <strong>in</strong>faunal co<strong>in</strong>positio~~ at these stations may be the result of other enviroi~me~ltal factors<br />

exist<strong>in</strong>g at these stations that have not been measured, such as naturally occurri~lg anoxic<br />

co~lditions <strong>in</strong> the sediments. Alternatively, benthic community effects may also be due to an<br />

unmeasured chemical, or a comb<strong>in</strong>ation of chemicals that were measured at lower levels.<br />

Exam<strong>in</strong>ation of the thirty-six stations from the 10 strata <strong>in</strong> Elliott Bay and the Duwamish<br />

<strong>in</strong>dicated that 22 stations, located primarily along the bay's northeastern shorel<strong>in</strong>e, <strong>in</strong> both tlle<br />

east and west waterways around Harbor Island, and <strong>in</strong> the Duwamish Waterway, had both<br />

significant toxicity results and elevated chemical conta~n<strong>in</strong>ation. Only two of these thirty-six<br />

stations (stations 175 and 178, both <strong>in</strong> outer Elliott Bay) had no significant toxicity results and no<br />

elevated clle~nical contam<strong>in</strong>ation (Figure 42).<br />

Page 50

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