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

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system <strong>and</strong> consequently affect swimming ability of fish. Behavioral modifications, such<br />

as changes in swimming performance, are regularly considered in NMFS’ Opinions.<br />

Swimming performance therefore is an assessment endpoint. Measurable changes in<br />

swimming speed are the assessment measure used to evaluate this endpoint. Reductions<br />

in swimming performance could also affect other assessment endpoints such as migration<br />

<strong>and</strong> predator avoidance. We may or may not have empirical data that address these<br />

endpoints, resulting in a recognized data gap. This uncertainty would be identified<br />

during the problem formulation phase, <strong>and</strong> discussed in the risk characterization phase.<br />

Critical Habitat Risk Hypotheses:<br />

To determine potential effects to designated critical habitat, NMFS evaluates the effects<br />

of the action by first looking at the effects on PCEs of critical habitat. Effects to PCEs<br />

include changes to the functional condition of salmonid habitat caused by the action in<br />

the action area. Properly functioning salmonid PCEs are important to the conservation of<br />

the ESU/DPS. The stressors of the action for this Opinion are chemicals. As such, the<br />

key PCEs that are potentially affected are salmonid prey availability <strong>and</strong> degradation of<br />

water quality in freshwater spawning sites, freshwater rearing sites, freshwater migration<br />

corridors, estuarine areas, <strong>and</strong> nearshore marine areas. We developed two risk<br />

hypotheses based on these PCEs:<br />

1. Exposure to the stressors of the action is sufficient to reduce abundance of aquatic<br />

prey items of salmonids; <strong>and</strong><br />

2. Exposure to the stressors of the action is sufficient to degrade water quality in<br />

designated critical habitat.<br />

These hypotheses are evaluated using the best scientific <strong>and</strong> commercial data available<br />

presented in the Response section. Examples of assessment endpoints evaluated include<br />

prey survival, prey growth, prey drift, prey reproduction, abundance of prey, health of<br />

invertebrate aquatic communities, recovery of aquatic communities following pesticide<br />

exposure, etc. If the available evidence supports the risk hypotheses, then NMFS<br />

evaluates whether the potential reductions in PCEs are localized or widespread. The<br />

potential reduction of PCEs affect on the conservation value of designated critical<br />

48

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