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<br />DISCUSSION <br /> <br />We found that abundance of adult nonnative smallmouth bass declined after <br />mechanical removal at two study sites in the Yampa River. We propose that our annual <br />removal rates of 40-48% at Little Yampa Canyon and 44-65% at Lily Park from 2004 <br />through 2006 assisted with the decline in abundance. At Little Yampa Canyon we <br />removed 3,879 adult smallmouth bass from 2004 through 2006 and abundance <br />declined 17% from 2,888 fish in 2004 to 2,394 fish in 2007. At Lily Park we removed <br />2,588 adult smallmouth bass from 2004 through 2006 and abundance declined 19% <br />from 1,519 fish in 2004 to 1,233 fish in 2007. Additional evidence of a decline of <br />smallmouth bass numbers from 2004 to 2007 included declining CPUE at both sites <br />during the study period. CPUE was well correlated with density and CPUE may serve <br />as an occasional substitute for annual abundance estimates; however, abundance <br />estimation using mark-recapture methods is superior for measuring changes in <br />smallmouth bass populations in the Yampa River and we encourage its continued use. <br /> <br />Removal rates improved with increased effort. In Little Yampa Canyon in 2004 and <br />2005, removal rates were not very high because our treatment (removal) area at the <br />time was only 12 miles long or 50% of the 24-mile study site for which abundance was <br />estimated. In 2006 even though smallmouth bass were removed from the entire 24- <br />mile reach, removal rate was low because we only completed five removal occasions <br />that year due to a short-duration water year. We achieved the highest removal rates at <br />Little Yampa Canyon (64%) and Lily Park (83%) in 2007; however, those removals did <br />not affect the observed decline in abundance because removals in 2007 were done <br />after abundance was estimated. . Increasing the rate of removal will require applying <br />removal at a geographic scale that matches the distribution and home-range of the <br />targeted species, increasing effort, or increasing capture efficiency. Removal rate could <br />be improved with more effort such as increasing the number of electrofishing boats <br />operating concurrently. However, we suggest increasing effort by adding one or two <br />more removal occasions earlier in the year. Capture efficiency also affects removal rate <br /> <br />22 <br />