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<br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br /> <br />Duchesne River Adult fish monitoring <br /> <br />Conversely, cold water fishes, such as mountain whitefish and brown trout, were less abundant in <br />summer collections. Colorado pikeminnow were captured during base flow collections in both <br />1998 and 1999, and between both years pikeminnow were found in each of the three reaches. <br />The lengths of Colorado pikeminnow captured in the Duchesne River ranged between 345 <br />and 725 nun, however, a large percentage of the pikeminnow captured were subadu1ts or young <br />adults with 42% of the fish collected less that 500 nun (Appendix Figure 1a). Lengths of <br />pikeminnow captured between 1997 and 1999 did not show any pattern, although most fish <br />captured in 1999 were subadu1ts or young adults. Consistency was observed in the length <br />distribution of blue head sucker (Appendix Figure 1b), but a shift in the length offlanne1mouth <br />sucker was observed during the three years of data with larger fish (>450 nun) becoming more <br />abundant in 1998 and 1999 (Appendix Figure 1c). Length frequencies of mountain whitefish <br />(Appendix Figure 1d) and the most abundant nonnative fishes did not show patterns of change <br />among the three years of the study (Appendix Figures 2a-d). <br /> <br />Telemetry <br />Seasonal movement patterns <br />One razorback sucker and 27 Colorado pikeminnow were implanted with radio <br />transmitters in the Duchesne River during the spring months between 1997 and 1999 (Table 4). <br />Transmitters were implanted in five Colorado pikeminnow and one razorback sucker in 1997, six <br />Colorado pikeminnow in 1998, and 16 Colorado pikeminnow in 1999. The single razorback <br />sucker was captured near the confluence (rmi 0.1), and Colorado pikeminnow implanted were <br />captured as far downstream as the confluence (rmi 0.1) and upstream to near the Myton Bridge <br />(rmi 33.3). However, the majority of Colorado pikeminnow implanted with transmitters were <br />captured in the lower reach ( 22 or 81.5%). <br />Information from both data loggers and aerial contacts showed that telemetered fish did <br />not remain in the Duchesne River throughout the year, but moved into the Green River at various <br />dates before December (Figure 4). Data from telemetry loggers indicated only two transmitter <br />implanted fish, 40.323 and 40.374, moved into the Uintah River at any time during the study. <br />Fish 40.323 was in the lower Uintah River between 11 and 26 September 1998, and 40.3 74 spent <br />only one day (14 June 1998) in the vicinity in the lower Uintah River. Thus, te1emetered <br />Colorado pikeminnow did not readily use the Uintah River during the three years ofthe study. <br /> <br />6 <br />