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1 <br />r Squawf ish could have been attracted to the warmer waters of the Little Snake <br /> River and to better feeding opportunities. <br /> Average movement of radiotagged fish related to spawning was 65 miles <br />r (range 34.5 - 84.5 miles) for both years. This was the one-way distance from <br /> the point of last contact above Yampa Canyon to the lowest river mile location <br /> in Yampa Canyon. In the summer 1987, three fish (A08, All, and B11) were <br /> located within the spawning area of Yampa Canyon (personal communication H.M. <br />r Tyus, USFWS, Vernal, Utah). All three fish were located back at their over- <br /> wintering areas in the fall, 1987. Four fish (A91, B85, C87, and C89) were <br /> known to migrate to the Yampa Canyon spawning area in the summer, 1988, <br />r (personal communication, H.M. Tyus, USFWS, Vernal, Utah). Fish C87 was <br /> located during a radiotelemetry spot check of 'the area by the authors. Fish <br /> B85 was collected by CROW during the Fall 1988, at RMI 80.8 (Table 3). These <br />r fish exhibited a high degree of homing ability and fidelity by locating and <br /> using the same habitats previously used after spawning migration. Three of the <br /> implanted fish (BB7,' C87, and C95) had capture histories that also indicated <br /> fidelity to a specific river reach over one or more years. For example, fish <br />r radlotracked over an entire winter, and relocated during <br />C87 was recaptured <br /> , <br />the fall of the next year only 0.1 mile from where it had been originally <br /> caught and Carlin tagged 7 years earlier (Table 3). <br />r Although fish remained in specific areas during the winter, they were <br /> also quite active within each habitat. Fish in embayments and backwaters <br /> would move between several favored spots within the habitat, staying in a spot <br />r for several minutes to several hours before moving. Fish would often repeat <br /> this pattern of movement. These spots were often used by more than one <br /> squawfish at the same time. Movement did not appear to be influenced by the <br /> presence of other Colorado squawfish. This would often result in small <br />r congregations of two to three Colorado squawfish within a one meter diameter <br /> spot. Fish using run and shoreline habitats appeared to be more active, <br /> <br />r moving within and between habitats more frequently. Fish found in larger <br />pools and eddys behaved similar to those in backwater and embayment habitats. <br /> Those using smaller pools and eddys behaved similar to fish in run and <br /> shoreline habitats. <br />r H <br />bit <br />t U <br /> a <br />a <br />se <br /> There was a distinct difference in winter habitat use between years. <br />r During Winter 1, fish most often used habitats off the main channel (off- <br /> channel habitats). In winter 2, fish used main-channel habitats (Figures 6 <br /> and 7). Predominant habitats used Winter 1 were backwater, embayment, and <br />r run. Run and pool habitat were used more Winter 2. Flows during Winter 1 <br />ri <br />hi <br />t <br /> s <br />o <br />c <br />were higher, whereas flaws during Winter 2 were lower than mean <br /> winter flows (Figure 8 and Appendix C). High use of pool habitat in Winter 2 <br /> was due to the addition of the Lily Park study area, which is characterized by <br />r pool and eddy habitat and absence of backwater and embayment habitat. <br /> Habitat use by Colorado squawfish varied between study areas as did <br /> habitat availability. When a variety of habitats was available within a river <br />r reach, fish often selected off-channel habitats over main-channel types. <br /> Backwater use in Winter 1 was exclusively at the EM 95.7 backwater. This <br /> backwater was drastically altered during ice-off and spring runoff the first <br /> year; this may be a reason for limited use in winter 2. During winter 1, this <br />r backwater habitat apparently satisfied the needs of fish sufficiently that <br /> <br />21 <br />