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reduction of about 63% over the duration of the sampling period. Confidence limits for <br />abundance estimates in years 2000 and 2003 did not overlap. Regression analysis of loge <br />abundance as a function of time (N = 4) showed a negative relationship (loge abundance = <br />633.26 - 0.3131*year, rZ = 0.97,p = 0.016). Consistent with abundance estimates, numbers of <br />unique animals captured declined steadily over the study period from 265 in 2000 to 106 in 2003. <br />White River abundance estimates had moderately good precision, with CV's ranging from 13 to <br />20%. <br />The only abundance estimate not within expectations for all river reaches and years was <br />for the White River in 2000. In that year, one 1,240-mm TL fish was captured, and because of <br />the extremely low predicted probability of capturing this fish (0.000062), this individual inflated <br />the Huggins model abundance estimate by over 16,000 individuals. That individual was <br />removed from the data and the analysis re-run to arrive at the more realistic abundance estimate <br />reported. <br />Colorado pikeminnow recruits in the White River were rare during the study period and <br />ranged from 45 (SE = 14) in 2001 to 0 in 2003, reflecting a decline in the number of recruits in <br />the White River during this study. Confidence limits for abundance estimates of the few recruits <br />present in the White River 2000 and 2001 did not overlap with and were higher than estimates in <br />2002 and 2003. Estimates of Colorado pikeminnow recruit abundance in the White River were <br />less precise than abundance estimates for adults, with CV's that ranged from 31 to 90%. <br />Abundance of adult Colorado pikeminnow in the middle Green River was the highest of <br />any of the reaches studied in the Green River Basin but exhibited a pattern of decline similar to <br />that observed in the White River. Adult Colorado pikeminnow abundance was high in 2000 at <br />an estimated 1,613 (SE = 149) fish, but declined steadily to 1,184 (SE = 115) in 2001, to 834 (SE <br />27