Sediment Quality in Puget Sound Year 2 - Center for Coastal ...
Sediment Quality in Puget Sound Year 2 - Center for Coastal ...
Sediment Quality in Puget Sound Year 2 - Center for Coastal ...
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Triad Synthesis: A Comparison of Chemistry, Toxicity, and Infaunal<br />
Parameters<br />
To generate a more comprehensive picture of the quality of the sediments throughout the study<br />
area, a weight-of-evidence approach was used to simultaneously exam<strong>in</strong>e all three sediment<br />
"triad" parameters measured. Data from the toxicity test<strong>in</strong>g, chemical analyses, and benthic<br />
community analyses from all stations were comb<strong>in</strong>ed <strong>in</strong>to one table (Appendix H) <strong>for</strong> review.<br />
From this data compilation, thirty-six stations were identified <strong>in</strong> which at least one chemical<br />
concentration exceeded an ERM, SQS, or CSL value and at least one of the toxicity tests<br />
<strong>in</strong>dicated statistically significant results relative to controls (Table 33). These stations were<br />
located <strong>in</strong> Port Townsend (I), the central bas<strong>in</strong> (3), the Ba<strong>in</strong>bridge Bas<strong>in</strong> (2), Dyes Inlet (2),<br />
S<strong>in</strong>clair Inlet (6), and Elliott Bay and the Duwamish River (22). Together, these stations<br />
represented an area of 99.73 km2 or about 14% of the total survey area.<br />
Twenty-five stations showed no <strong>in</strong>dications of significant sediment toxicity or chemical<br />
contam<strong>in</strong>ation (Table 34). These stations were located <strong>in</strong> Port Townsend (1 ), Admiralty Inlet (3),<br />
Possession <strong>Sound</strong> (2), the central bas<strong>in</strong> (3), Port Madison (3), Liberty Bay (3), the Ba<strong>in</strong>bridge<br />
Bas<strong>in</strong> (4), Rich Passage (3), Dyes Inlet (I), and outer Elliott Bay (2). These 25 stations<br />
represented an area of 359.3 1 km" equivalent to 49% of the total survey area. Both sets of<br />
stations are highlighted <strong>in</strong> Figures 38-42.<br />
The rema<strong>in</strong><strong>in</strong>g thirty-n<strong>in</strong>e stations displayed either signs of significant chemical contam<strong>in</strong>ation<br />
but no toxicity, or significant toxicity, but no chemical contam<strong>in</strong>ation. These stations were<br />
located <strong>in</strong> Port Townsend (4), Possession <strong>Sound</strong> (I), the central bas<strong>in</strong> (lo), Eagle Harbor (3),<br />
Liberty Bay (3), the Ba<strong>in</strong>bridge Bas<strong>in</strong> (6), and Elliott Bay and the Duwamish River (12).<br />
Together, these stations represented an area of 272.62 km2, equivalent to 37% of the total central<br />
<strong>Puget</strong> <strong>Sound</strong> study area.<br />
The complete suite of triad parameters <strong>for</strong> all stations was exam<strong>in</strong>ed to determ<strong>in</strong>e whether the<br />
<strong>in</strong>faunal assemblages, as characterized by benthic <strong>in</strong>dices, appeared to be impacted by the<br />
presence or absence of toxic compounds. Details regard<strong>in</strong>g the "triad" relationship <strong>for</strong> all 100<br />
stations are summarized below.<br />
Exam<strong>in</strong>ation of the six stations from the two strata <strong>in</strong> Port Townsend <strong>in</strong>dicated that one station,<br />
106, had both significant toxicity results and elevated chemical contam<strong>in</strong>ation, and one station,<br />
1 10, had no significant results. <strong>Sediment</strong>s from stations 106- 108 (stratum 1 ) and stations 109-<br />
11 1 (stratum 2), situated <strong>in</strong> southern and northern Port Townsend respectively (Figure 38), were<br />
collected from depths rang<strong>in</strong>g from 13-34m, with sediment types rang<strong>in</strong>g from primarily sand to<br />
primarily silt-clay particles. All (with the exception of station 1 10) had levels of 4-methylphenol<br />
above state SQS and CSL criteria. No toxicity was displayed at these stations, with the exception<br />
of significantly reduced amphipod survival at station 106. Measures of <strong>in</strong>faunal diversity at these<br />
6 stations were, <strong>in</strong> most cases, high and similar between stations, with little similarity <strong>in</strong> the<br />
dom<strong>in</strong>ant species list from station to station. Station 106, which displayed both impacted<br />
toxicity and chemical measures, also displayed the lowest total abundance (302 <strong>in</strong>dividuals), but<br />
exhibited a relatively high SDI (20). Several of the 10 numerically dom<strong>in</strong>ant species were those<br />
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