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Carbaryl, Carbofuran, and Methomyl - National Marine Fisheries ...

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interpretation of results is complicated by how well the results represent natural aquatic<br />

ecosystems <strong>and</strong> how well the studies apply to salmonid-specific assessment endpoints <strong>and</strong> risk<br />

hypotheses. These studies typically measured individual responses of aquatic organisms to<br />

contaminants in the presence of other species. Some are applicable to questions of trophic<br />

effects <strong>and</strong> invertebrate recovery, as well as providing pesticide fate information. The most<br />

useful mesocosm study results for this Opinion are those that directly pertain to identified<br />

assessment endpoints <strong>and</strong> risk hypotheses. We discuss study results in the context of salmonid<br />

prey responses, emphasizing survival <strong>and</strong> recovery of prey taxa as well as shifts from preferred<br />

taxa to other taxa if measured. One of the notable limitations of these study types is they do not<br />

take represent real world aquatic ecosystems that are degraded from various stressors including<br />

contaminants <strong>and</strong> elevated water temperature..<br />

Results from aquatic field studies were generally not discussed in great detail within the BEs.<br />

We discuss field studies that evaluated identified assessment endpoints, particularly those which<br />

address salmonid prey responses in systems with ESA-listed salmonids.<br />

Ranges in toxicity values presented in the BEs for each a.i. are summarized in Table 64. Ranges<br />

in toxicity values (μg/L) are organized by assessment endpoint <strong>and</strong> associated assessment<br />

measures. The BEs provided toxicity information from EPA’s EFED Pesticide Toxicity<br />

Database <strong>and</strong> from the ACQUIRE database.<br />

322

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