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electrofishing were similar to the effects of non-electrofishing sampling gears. All <br />sampling gears were assumed to have some negative effects on the captured animal. <br />The critical issue was whether electrofishing had greater negative effects on the animal <br />than other non-electrofishing sampling- gears. Effects were measured at both individual <br />and population levels. Population-level effects were measured with recapture rate that <br />represented a relative index of fish survival for each sampling gear type based on the <br />assumption that recapture rate would be lower if a particular sampling gear caused <br />higher post-sampling mortality. The hypothesis was that recapture rates of each <br />species were similar for the two gear types (electrofishing ornon-electrofishing). <br />Individual-level effects were measured by examining growth rate, an important indicator <br />of fish health. It was assumed that nonlethal, negative effects of a sampling gear would <br />reduce fish growth. I compared growth offish captured by electrofishing to growth of <br />fish captured by non-electrofishing gears to test the hypothesis that growth rates were <br />similar for the two gear types. <br />METHODS <br />Endangered fish capture data were obtained from the data repository at the U.S. <br />Fish and Wildlife Service (USFWS),Grand Junction, Colorado field station, agency <br />reports, and individual researchers to create a working database of capture events in <br />the Upper Colorado River Basin. The database contained unique records for each <br />capture event of a tagged fish. Each uniquely-tagged fish had at least one record for <br />the initial capture and tagging event and if a fish was recaptured there was a record for <br />2 <br />