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

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

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invertebrates exposed to elevated temperatures, so where elevated temperatures co-occur with<br />

OPs <strong>and</strong> carbamates the effect to aquatic life is likely greater than at lower temperatures. Many<br />

salmonid populations reside in watersheds which have been listed by the four western states as<br />

impaired due to temperature exceedances. We therefore discuss qualitatively temperature<br />

impacts on salmonids population responses to the stressors of the action.<br />

J. Exposure to specific pH ranges can affect the toxicity of the stressors of the action.<br />

Some data indicate acute toxicity of carbaryl <strong>and</strong> carbofuran increases as pH increased based on<br />

the available freshwater fish assays (Mayer <strong>and</strong> Ellersieck 1986). Other data indicated that<br />

toxicity was reduced in pH greater than 9 due to rapid hydrolysis i.e., a half-life of 30 minutes in<br />

pond mesocosms. For methomyl, pH seems to have less of an influence on hydrolysis rates.<br />

Within the Pacific Northwest <strong>and</strong> California pH varies seasonally <strong>and</strong> typically may range from<br />

6 – >9. We expect that salmonids exposed to both pH ranges at or near physiological tolerance<br />

limits <strong>and</strong> the three insecticides concurrently may die at relatively lower concentrations<br />

compared to salmonids exposed in laboratory assays. We therefore discuss qualitatively pH<br />

impacts on salmonids population responses to the stressors of the action.<br />

Effects to Salmonid Populations from the Proposed Action<br />

Here we translate individual fitness consequences to potential population-level effects using both<br />

quantitative <strong>and</strong> qualitative methods. We quantitatively translate reduced survival of juveniles<br />

based on four-day exposures to four populations of salmonids including ocean-type Chinook,<br />

stream-type Chinook, coho, <strong>and</strong> sockeye salmon. We employ a life history population model<br />

that incorporates changes in first-year juvenile survival rates <strong>and</strong> then translates them into<br />

predicted changes in the modeled population’s intrinsic rate of growth, i.e., lambda (Appendix<br />

1). We discuss the percent change in lambda in the context of expected concentrations of the<br />

three insecticides in salmonid habitats. We focus on the concentrations at which a significant<br />

departure occurs from the unexposed population <strong>and</strong> compare them to expected environmental<br />

concentrations described in the Exposure Analysis. We also discuss in general terms the<br />

likelihood of exposure to the range of pesticide concentrations that occur in salmonid habitats.<br />

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