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

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Summary of Toxicity Information from Open Literature<br />

To organize the available toxicity information on listed salmonids <strong>and</strong> habitat, we developed risk<br />

hypotheses with associated assessment endpoints as described in the Approach to the Assessment<br />

section. Recall that assessment endpoints are biological attributes of salmonids <strong>and</strong> their habitat<br />

potentially susceptible to the stressors of the action. In addition to toxicity data presented in the<br />

BEs, we also considered information from other sources to evaluate both individual <strong>and</strong><br />

population-level endpoints. The results of those studies are summarized below under<br />

corresponding assessment endpoints. We qualitatively assigned the most significance to study<br />

results that were: 1) derived from experiments using salmonids (preferably listed Pacific<br />

salmonids or hatchery surrogates); 2) measured an assessment endpoint of concern e.g.,<br />

survival, growth, behavior, reproduction, abundance etc., identified in a risk hypothesis; 3)<br />

resulted from exposure to stressors of the action or relevant chemical surrogates (i.e., other<br />

AChE inhibitors); <strong>and</strong> 4) had no substantial flaws in the experimental design. When a study did<br />

not meet these criteria, we highlighted the issue(s) <strong>and</strong> discussed how the information was used<br />

or why the information could not be used.<br />

Assessment endpoint: Swimming<br />

Assessment measures: Burst swimming speed, distance swam, rate of turning, baseline speed,<br />

tortuosity of path, acceleration, swimming stamina, <strong>and</strong> spontaneous swimming activity<br />

Swimming is a critical function for anadromous salmonids that is necessary to complete their life<br />

cycle. Impairment of swimming may affect feeding, migrating, predator avoidance, <strong>and</strong><br />

spawning (Little <strong>and</strong> Finger 1990). It is the most frequently assessed behavioral response of<br />

toxicity investigations with fish (Little <strong>and</strong> Finger 1990). Swimming activity <strong>and</strong> swimming<br />

capacity of salmonids have been measured following exposures to a variety of AChE-inhibiting<br />

insecticides including the carbamates carbaryl <strong>and</strong> carbofuran <strong>and</strong> a variety of OP insecticides.<br />

Swimming capacity is a measure of orientation to flow as well as the physical capacity to swim<br />

against it (Howard 1975; Dodson <strong>and</strong> Mayfield 1979). Swimming activity includes<br />

measurements of frequency <strong>and</strong> duration of movements, speed <strong>and</strong> distance traveled, frequency<br />

<strong>and</strong> angle of turns, position in the water column, <strong>and</strong> form <strong>and</strong> pattern of swimming. A review<br />

paper summarized many of the experimental swimming behavioral studies <strong>and</strong> concluded that<br />

effects to swimming activity generally occur at lower concentrations than effects to swimming<br />

336

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