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

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experimental concentrations tested, number of treatments <strong>and</strong> replicates used, solvent controls,<br />

etc.- are needed. The slope of the observed dose-response relationship is particularly useful in<br />

interpolating incidences of death at concentrations below or above an estimated LC50. The<br />

variability of an LC50 is usually depicted by a confidence interval (95% CI) or st<strong>and</strong>ard<br />

deviation/error <strong>and</strong> is illustrative of the degree of confidence associated with a given LC50<br />

estimate i.e., the smaller the range of uncertainty the higher the confidence in the estimate.<br />

Without an estimate of variability, it is difficult to infer the precision of the estimate.<br />

Furthermore, survival experiments are of most utility when conducted with the most sensitive<br />

life stage of the listed species or a representative surrogate. In the case of ESA-listed Pacific<br />

salmonids, there are several surrogates that are available for toxicity testing including hatchery<br />

reared coho salmon, Chinook salmon, steelhead, <strong>and</strong> chum salmon, as well as rainbow trout 2 .<br />

The available toxicity data include a varitety of salmonids. Unfortunately, slopes, estimates of<br />

variability for an LC50, <strong>and</strong> experimental concentrations frequently are not reported. In our<br />

review of the BEs, we did not locate any reported slopes of dose-response curves, although some<br />

of this information was presented in some of the corresponding Science Chapters. Consequently,<br />

we must err on the side of the species in the face of these uncertainties <strong>and</strong> select LC50s from the<br />

lower range of available salmonid studies. We selected LC50s <strong>and</strong> associated slopes as input in<br />

the population modeling exercises discussed later. We evaluate the likelihood of concentrations<br />

that are expected to kill fish <strong>and</strong> apply qualitative <strong>and</strong> quantitative methods to infer populationlevel<br />

responses of ESA-listed salmonids within the Risk Characterization section (Figure 2).<br />

Growth of individual organisms is an assessment endpoint derived from st<strong>and</strong>ard chronic fish<br />

<strong>and</strong> invertebrate toxicity tests summarized in the BEs. It is difficult to translate the significance<br />

of impacted growth derived from a guideline study to fish growth in aquatic ecosystems. The<br />

health of the fish, availability <strong>and</strong> abundance of prey items, <strong>and</strong> the ability of the fish to<br />

adequately feed are not assessed in st<strong>and</strong>ard chronic fish tests. These are important factors<br />

affecting the survival of wild fish. What is generally assessed is size or weight of fish measured<br />

2 Rainbow trout <strong>and</strong> steelhead are the same genus species (Oncorhynchus mykiss), with the key differentiation that<br />

steelhead migrate to the ocean while rainbow trout remain in freshwaters. Rainbow trout are therefore good<br />

toxicological surrogates for freshwater life stages of steelhead, but are less useful as surrogates for life stages that<br />

use estuarine <strong>and</strong> ocean environments.<br />

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