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Temperature <br />Main channel temperatures were monitored at six sites, one within each of study strata 1, 6, 7, <br />8, 10, and 11 (see Figure 1); two additional sites, one upstream and one downstream of <br />Stratum 12 in the Gunnison River were also monitored. At five sites, thermographs (Ryan <br />Instruments, Redmond, Washington) were deployed and the data downloaded twice yearly. <br />Data from strata 7 and 10, and from the site downstream of Stratum 12, were collected by the <br />U. S. Geological Survey (USGS) at their gaging stations (Colorado River near Colorado-Utah <br />State Line and near Cameo, and Gunnison River near Grand Junction, respectively). Mean <br />daily values were calculated from readings taken every two hours (to the nearest 0.1 ° Q. <br />We compared temperature indices for Colorado pikeminnow growth among thermograph sites <br />for the 1992-1997 period to measure spatial variation in thermal regime suitability along the <br />river continuum. We derived these indices by using an approach developed specifically for <br />Colorado pikeminnow by Kaeding and Osmundson (1988) in which mean daily temperatures <br />are converted to values relative to the maximum potential (1.0) for growth at the optimum <br />temperature (25 ° C); these thermal units are then summed to provide an annual value. <br />RESULTS <br />Fish Abundance <br />Fish catch rates varied both spatially and temporally. To examine spatial differences (among <br />strata), an overall catch rate was calculated for each stratum using data from all sampling <br />periods. To do this, data (catch and effort) from the various sampling periods were first <br />pooled for each shoreline sample. The catch rate for each grand shoreline sample was then <br />calculated and the mean of these was then taken. Data were pooled only from the three <br />periods during which sampling was done in all strata, (i.e., spring 1994 data were excluded). <br />Catch rates within strata varied with period, and inclusion of data from the four strata sampled <br />in spring 1994 would bias results of those strata relative to the other strata for which there <br />were no spring 1994 data. To examine changes in distribution through time (temporal <br />variation), catch rates are also presented by individual sampling period. <br />Spatial variation <br />All fish.--Mean total catch rates (species combined) in strata upstream of Westwater Canyon <br />(`upstream strata') were considerably higher (-2-5 fish per electrofishing minute) than those in <br />strata downstream (< 1 fish/min) of Westwater Canyon (`downstream strata'). The lowest <br />catch rate (0.1 fish/min) was in Stratum 1 (Figure 2). Log-transformed catch rates in strata 7, <br />8, 9, 11 and 12 were significantly higher than in downstream strata 1-6 (Tukey-Kramer [T-K] <br />multiple comparison test, P < 0.05). Strata 8, 9, 11 and 12 catch rates were not statistically <br />different from one another. The Stratum 10 catch rate was significantly higher than in <br />downstream strata 1-5, but significantly lower than catch rates in upstream strata 8, 9, 11 and <br />12 (Appendix Table 3). <br />8