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

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AChE levels recovered slightly. The treatment concentrations used in this study are very high<br />

<strong>and</strong> indicate that brook trout are not sensitive to diet-induced toxicity of fenitrothion. The<br />

experiment did show that AChE inhibition from the diet is possible, yet it is difficult to<br />

determine the relative toxicity of carbaryl, carbofuran, <strong>and</strong> methomyl found in contaminated<br />

insects consumed by Pacific salmonids.<br />

Habitat assessment endpoints:<br />

Prey survival, prey drift, nutritional quality of prey, abundance of prey, health of aquatic prey<br />

community, <strong>and</strong> recovery of aquatic communities following N­methyl carbamate exposures<br />

Assessment measures: 24, 48, <strong>and</strong> 96 h survival of prey items from laboratory bioassays<br />

reported as EC/LC50s; sublethal effects to prey items; field studies on community abundance;<br />

indices of biological integrity (IBI); community richness; <strong>and</strong> community diversity.<br />

Death of aquatic invertebrates in laboratory toxicity tests were reported in each of the BEs.<br />

Salmonid aquatic <strong>and</strong> terrestrial prey are highly sensitive to the three carbamate insecticides.<br />

Death of individuals <strong>and</strong> reductions in individual taxa <strong>and</strong> prey communities have been<br />

documented <strong>and</strong> are expected following applications of N-methyl carbamates that achieve effect<br />

concentrations-several of which are at the low μg/L levels (Schulz 2004). Complete or partial<br />

elimination of aquatic invertebrates from streams contaminated by insecticides has been<br />

documented for carbaryl (Muirhead-Thomson 1987) as well as many other insecticides. A<br />

review of field studies published from 1982-2003 on insecticide contamination concluded that<br />

“about 15 of the 42 studies revealed a clear relationship between quantified, non-experimental<br />

exposure <strong>and</strong> observed effects in situ, on abundance [aquatic invertebrate], drift, community<br />

structure, or dynamics” (Schulz 2004). Although the top three insecticides most frequently<br />

detected at levels expected to result in toxicity were chlorpyrifos (OP), azinphos-methyl (OP),<br />

<strong>and</strong> endosulfan, the N-methyl carbamates carbaryl, carbofuran, oxymyl, <strong>and</strong> fenobucarb all<br />

showed clear or assumed relationships between exposure <strong>and</strong> effect (Schulz 2004).<br />

Drift, feeding behavior, swimming activity, <strong>and</strong> growth are sublethal endpoints of aquatic prey<br />

negatively affected by exposure to AChE inhibitors (Courtemanch <strong>and</strong> Gibbs 1980; Haines 1981;<br />

Hatakeyama, Shiraishi et al. 1990; Davies <strong>and</strong> Cook 1993; Beyers, Farmer et al. 1995; Schulz<br />

2004). Drift of aquatic invertebrates is an evolutionary response to aquatic stressors. However,<br />

insecticides, particularly carbamates <strong>and</strong> OPs, can trigger catastrophic drift of salmonid prey<br />

346

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