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

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Risk Characterization<br />

We follow the framework presented in Figure 2 to conduct the analysis <strong>and</strong> risk<br />

characterization phases. First we conduct exposure <strong>and</strong> response analyses to<br />

estimate/determine the type, likelihood, magnitude, <strong>and</strong> frequency of adverse responses<br />

resulting from predicted exposure based on the best available information. We evaluate<br />

species information <strong>and</strong> pesticide information to determine when, where, <strong>and</strong> at what<br />

concentrations listed salmonids <strong>and</strong> their habitat may be exposed. We then correlate<br />

those exposure estimates with probable response based on available toxicity data. Once<br />

we have conducted the analysis phase, we move to the risk characterization phase (Figure<br />

2).<br />

In the risk characterization phase, we revisit the risk hypotheses <strong>and</strong> apply tools to<br />

address whether any individual fitness consequences assessed in the analysis phase would<br />

be expected to impact populations <strong>and</strong> ultimately species. One of the tools we employ is<br />

individual-based population models predicated on a juvenile salmonids’ probability of<br />

survival in its first year of life. We also assess interactions between the stressors of the<br />

action <strong>and</strong> stressors in the Environmental Baseline (Figure 2). Some pesticides’ toxicity<br />

profiles are influenced by environmental parameters such as pH <strong>and</strong> temperature.<br />

Temperature can affect pesticide metabolism in fish <strong>and</strong> is seasonally elevated in many<br />

salmonid supporting watersheds. As described earlier in this section we translate<br />

expected effects to identified PCEs by evaluating the available information to support<br />

risk hypotheses. If we expect PCEs to be reduced we discuss whether the expected<br />

reductions translate to reductions in the conservation value of designated critical habitat.<br />

To conclude consultation, cumulative effects are described <strong>and</strong> the extent to which<br />

species <strong>and</strong> habitat are affected is documented. Cumulative effects as defined in 50 CFR<br />

§404.2 include the effects of future, state, tribal, local, or private actions that are<br />

reasonably certain to occur in the action area of this Opinion. Integrating the Effects of<br />

the Proposed Action, the Status of Listed Resources, <strong>and</strong> the Environmental Baseline,<br />

NMFS determines whether EPA’s pesticide registration action jeopardizes the continued<br />

53

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