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

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insecticides <strong>and</strong> their formulations may be responsible for a substantial portion. In fact, several<br />

studies have shown toxicity to salmonid prey items from field collected waters <strong>and</strong> sediment due<br />

to pesticide residues (Cuffney, Meador et al. 1997; Hall, Killen et al. 2006).<br />

We therefore expect that spawning, rearing, <strong>and</strong> migratory areas will be affected by the stressors<br />

of the action resulting in reduced abundances of aquatic prey items. The magnitude in reduction<br />

of prey is difficult to ascertain, however where designated critical habitats overlap with high<br />

potential use areas such as agricultural or urban dominated flood plains, we expect pronounced<br />

reductions. These areas support fry <strong>and</strong> juvenile growth <strong>and</strong> development which are predicated<br />

on an abundant <strong>and</strong> diverse source of prey. Reductions in prey availability may affect the<br />

conservation value <strong>and</strong> the ability of the habitat features to support salmonids. In summary, the<br />

available information shows prey items of ESA-listed salmonids are affected by the stressors of<br />

the action to an extent warranting an analysis of whether the conservation value of designated<br />

critical habitat is negatively affected.<br />

Risk hypothesis 2. Exposure to the stressors of the action is sufficient to degrade water<br />

quality in designated critical habitat.<br />

We addressed this hypothesis by comparing exposure concentrations to toxicity data. The results<br />

of the comparison indicate that expected concentrations from the proposed action trigger adverse<br />

effect levels for salmonids <strong>and</strong> their prey (see Exposure Analysis <strong>and</strong> Response Analysis<br />

sections). Based on pesticide uses described in the Description of the Action section coupled<br />

with expected concentrations presented in the Exposure Analysis section (i.e., concentrations<br />

derived from surface water monitoring data, EPA <strong>and</strong> NMFS modeling estimates), we expect<br />

these concentrations to be present in designated critical habitat <strong>and</strong> therefore to degrade water<br />

quality. In many of the watersheds containing designated critical habitats, water quality is<br />

identified as a major limiting factor to salmonid production. The proposed action is likely to<br />

further degrade water quality in spawning, rearing, <strong>and</strong> migratory areas. Collectively, this<br />

information supports the conclusion that designated critical habitats are likely degraded<br />

throughout the four states <strong>and</strong> further analysis is warranted to determine the potential to reduce<br />

the conservation value of designated critical habitats.<br />

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