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Razorback Suckers <br />Net long-range movement by radiotagged adult razorback suckers in the Green River <br />averaged 3.4 km (n=8, range of 0.0-16.9 km) and 4.7 km (n=9, range of 0.8-11.7 km) in Winter 1 <br />and Winter 2, respectively. Over 75 percent (13) of 17 fish monitored remained within 5 km of their <br />origination location. Valdez and Masslich (1989) concluded that, like adult Colorado squawfish, adult <br />razorback suckers in the Green River probably ovecwinter within reaches 2 to 5 km long. <br />Adult razorback suckers also showed a fidelity for specific overwinter locations. One <br />razorback sucker, radiotagged and monitored in Rainbow Park (RM 327-328) on October 28, 1986, <br />was recaptured at a suspected spawning area (Razorback Bar, RM 311), about 25 km downstream <br />in April, 1987 (Personal Communication, Harold Tyus, U.S. Fish and Wildlife Service, November <br />1987). The fish was relocated, via radiotelemetry, in the same eddy complex (RM 327.3) over 13 <br />months later on December 4, 1987, and monitored near this site until the radiotransmitter failed on <br />March 24, 1988. This fish apparently traversed Split Mountain Canyon to and from the spawning <br />area. A different adult razorback sucker was radiotagged near Mitton Park (RM 344.1) on October <br />27, 1986, and relocated aearly 16 months later, on February 19, 1988, about 2 km downstream. <br />Valdez and Masslich (1989) suspected that other adult razorback suckers and Colorado squawfish <br />would have been relocated at specific wintering sites, had the radiotransmitters lasted a full year. <br />Adult razorback suckers, like adult Colorado squawfish, were locally active throughout winter. <br />Movement was typically within a given habitat (e.g., slow run or slackwater), between several favorite <br />spots. Local movement by overwintering razorback suckers was characterized by rates of 25 and 31 <br />m/hr, for Winter 1 and Winter 2, respectively. This movement was usually between microhabitats that <br />the fish occupied for extended periods of time. One fish (#OR-3257) monitored for 24 hours <br />occupied three spots for periods of 15, 4, and 5 hours (Figure 13). The fish moved a total of 103 m, <br />with net displacement of only 20 m from the original location. These movement rates were <br />considered normal, and did not differ with habitat types, as with Colorado squawfish, i.e., greater <br />movement by squawfish in backwaters was attributed to foraging for small fish prey. <br />Habitat Use <br />Colorado Squawflsh <br />Habitat used by radiotagged adult Colorado squawfish in the two winters (1986-87 and 1987- <br />88) differed in both the Green and Yampa rivers (Figure 14). Different habitat use for Green River <br />fish was attributed to flow and ice conditions (Winter 1 with high flow and no ice, Winter 2 with low <br />flow and ice), and different use by Yampa River fish was attributed to flows (Winter 1 with high flow, <br />24 <br />