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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The results <strong>in</strong> the amphipod tests per<strong>for</strong>med <strong>in</strong> central and northern <strong>Puget</strong> <strong>Sound</strong> differed from<br />
those developed <strong>in</strong> studies with A. abdita conducted elsewhere <strong>in</strong> the U.S. The frequency<br />
distributions of the data from both areas are compared to that <strong>for</strong> data compiled <strong>in</strong> the<br />
NOAAIEMAP national database (Table 35). Whereas amphipod survival was less than 80% of<br />
controls <strong>in</strong> 12.4% of samples from studies per<strong>for</strong>med elsewhere, only one of the samples from<br />
central <strong>Puget</strong> <strong>Sound</strong> showed survival that low. None of the northern <strong>Puget</strong> <strong>Sound</strong> samples<br />
<strong>in</strong>dicated survival of less than 80%. In the national database 47% of samples <strong>in</strong>dicated survival<br />
of 90-99.9%. Similarly, <strong>in</strong> central <strong>Puget</strong> <strong>Sound</strong> 48% of samples had survival with<strong>in</strong> the range of<br />
90-99.9%. In northern <strong>Puget</strong> <strong>Sound</strong>, 76% of samples showed comparable survival. In both<br />
<strong>Puget</strong> <strong>Sound</strong> areas, the lower "tail" of the distribution (i.e., samples <strong>in</strong> which survival was very<br />
low) was absent.<br />
With the results of the amphipod tests weighted to the sizes of the sampl<strong>in</strong>g strata with<strong>in</strong> which<br />
samples were collected, the spatial scales of toxicity could be estimated. A critical value of<br />
40% of control response was used to estimate the spatial extent of toxicity <strong>in</strong> this test.<br />
However, because only one of the test samples <strong>in</strong>dicated less than 80% survival relative to<br />
controls, the spatial extent of toxicity was estimated as 0.1% of the central <strong>Puget</strong> <strong>Sound</strong> survey<br />
area.<br />
To add perspective to these data, the results from central and northern <strong>Puget</strong> <strong>Sound</strong> were<br />
compared to those from other estuaries and mar<strong>in</strong>e bays surveyed by NOAA <strong>in</strong> the U.S. The<br />
methods <strong>for</strong> collect<strong>in</strong>g and test<strong>in</strong>g the samples <strong>for</strong> toxicity were comparable to those used <strong>in</strong> the<br />
<strong>Puget</strong> <strong>Sound</strong> surveys (Long et al., 1996). In surveys of 26 U. S. regions, estimates of the spatial<br />
extent of toxicity ranged from 0.0% <strong>in</strong> many areas to 85% <strong>in</strong> Newark Bay, NJ (Table 36). The<br />
central and northern <strong>Puget</strong> <strong>Sound</strong> areas were among the many regions <strong>in</strong> which the spatial extent<br />
of toxicity <strong>in</strong> the amphipod tests was estimated to be 0% to 0.1 %. With the data compiled from<br />
studies conducted through 1997, the samples that were classified as toxic represented about 5.9%<br />
of the comb<strong>in</strong>ed area surveyed. The data <strong>for</strong> both regions of <strong>Puget</strong> <strong>Sound</strong> fell well below the<br />
national average. These data suggest that acute toxicity as measured <strong>in</strong> the amphipod survival<br />
tests was neither severe nor widespread <strong>in</strong> <strong>in</strong> sediments from the northern and central <strong>Puget</strong><br />
<strong>Sound</strong> study areas.<br />
Sea Urch<strong>in</strong> Fertilization - Pore Water<br />
^<br />
Several features of the sea urch<strong>in</strong> fertilization test comb<strong>in</strong>ed to make it a relatively sensitive test<br />
(Long et al., 1996). In these tests, early life stages of the animals were used. Early life stages of<br />
<strong>in</strong>vertebrates often are more sensitive to toxicants than adult <strong>for</strong>ms, ma<strong>in</strong>ly because fewer<br />
defense mechanisms are developed <strong>in</strong> the gametes than <strong>in</strong> the adults. The test endpo<strong>in</strong>t -<br />
fertilization success - is a sublethal response expected to be more sensitive than an acute<br />
mortality response. The gametes were exposed to the pore waters extracted from the samples;<br />
the phase of the sediments <strong>in</strong> which toxicants were expected to be highly bioavailable. This test<br />
was adapted from protocols <strong>for</strong> bioassays orig<strong>in</strong>ally per<strong>for</strong>med to test wastewater effluents and<br />
has had wide application throughout North America <strong>in</strong> tests of both effluents and sediment pore<br />
waters. The comb<strong>in</strong>ed effects of these features was to develop a relatively sensitive test - much<br />
more sensitive than that per<strong>for</strong>med with the amphipods exposed to solid phase sediments.<br />
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