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

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at several times during an experiment. The test fish are usually fed twice daily, ad libitum, i.e.,<br />

an over abundance of food is available to the fish. Therefore, any reductions in size are a result<br />

of fish being affected to such an extent that they are not feeding even when presented with an<br />

abundance of food. Subtle changes in feeding behaviors or availability of food would not be<br />

detected from these types of experiments. If growth is affected in these experiments, it is highly<br />

probable that growth of fish in natural aquatic systems would be severely affected. If effects to<br />

growth are likely, we assess salmonid population-level consequences based on reductions in<br />

juvenile growth <strong>and</strong> subsequent reduction in size prior to ocean entry.<br />

Reproduction, at the scale of an individual, can be measured by the number of offspring per<br />

female (fecundity), <strong>and</strong> at the scale of a population by measuring the number of offspring per<br />

females in a population over multiple generations. The BEs summarized reproductive endpoints<br />

at the individual scale from chronic freshwater fish experiments where hatchability <strong>and</strong> juvenile<br />

<strong>and</strong> larval survival are measured. NMFS considers many other assessment measures of<br />

reproduction, including egg size, spawning success, sperm <strong>and</strong> egg viability, gonadal<br />

development, reproductive behaviors, <strong>and</strong> hormone levels. These endpoints are not generally<br />

measured in st<strong>and</strong>ardized toxicity assays used in pesticide registration.<br />

Sometimes qualitative observations of sublethal effects are summarized from 96 h lethality doseresponse<br />

bioassays in EPA’s risk assessments. These observations generally were limited in the<br />

BEs for carabaryl, carbofuran, <strong>and</strong> methomyl, <strong>and</strong> when noted, pertained to unusual swimming<br />

behaviors. None of these behaviors were rigorously measured <strong>and</strong> therefore are of limited value<br />

in assessing the effects of the three insecticides on Pacific salmonids. We do, however note a<br />

few of the observations when they pertained to a relevant assessment endpoint, such as impaired<br />

swimming. Some BEs presented toxicity information on degradates, metabolites, <strong>and</strong><br />

formulations. However, toxicity information on other or “inert” ingredients found in pesticide<br />

formulations was usually not presented.<br />

Results from multiple species tests, called microcosm <strong>and</strong> mesocosm studies, were also<br />

discussed in the BEs to a varying degree. These types of experiments are likely closer<br />

approximations of potential ecosystem-level responses such as interactions among species<br />

(predator-prey dynamics), recovery of species, <strong>and</strong> indirect effects to fish. However, the<br />

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