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Wick et al. (1983) reported migration from the Upper Yampa to the Lower 321an of the Yampa <br />Canyon during late June and early July. Tyus (1990) reported migrations occurring between late <br />May and mid June on the Yampa River and late May to late June on the Green River. Miller et al. <br />(1982) reported migrations between late June to early July. Osmundson and Kaeding (1989) <br />reported increased movement of Colorado squawfish from late June and early July to late August <br />on the Colorado River near Grand Junction, Colorado. <br />Migration to spawning areas roughly coincides with the decrease of spring runoff and an increase in <br />water temperatures. Tyus (1990) reported migration beginning approximately 28 days (d) after peak <br />spring flows when mean water temperatures were approximately 14°C. Wick et al. (1983) <br />observed migration in radio-tagged squawfish after temperatures rose to 16°C. Tyus (1990) noted <br />the midpoint of migration coincided with the summer solstice and suggested photoperiod may be <br />important in initiating migration. Tyus (1990) reported spawning migrations occurring earlier in <br />low water years and later in high water years. Wick et al. (1983) suggested other environmental <br />factors besides flow may be important in initiating migrations. <br />Spawning migrations may be an important adaptation to a highly variable environment (M.L. Smith <br />1981; Tyus 1986). Migration to suitable spawning habitat may have some advantages in widely <br />fluctuating environmental conditions (Tyus 1986). <br />Non-Reproductive Movement <br />Non-migrating behavior in the Yampa River was noted by several authors (Wick et al. 1983; Tyus <br />and McAda 1984; Tyus 1990). These authors attributed this behavior to sexual immaturity in <br />Green River sub-basin squawfish. Only half of females (< 503 mm) captured by Seethaler (1978) <br />were sexually mature in the Yampa River. Tyus and McAda (1984) found one 510 mm TL <br />immature male. Miller et al. (1983) reported the average size of 4 non-migrants tagged on the <br />Green, and White rivers was 476.5 mm TL and the average size of 11 migrants was 565 mm. Tyus <br />(1990) and Hawkins (1991) reported a longitudinal separation between adults and juveniles; non- <br />migratory behavior in juveniles may maintain this boundary. Tyus (1986) suggested that this <br />strategy may be an evolutionary adaptation to reduce intraspecific competition and predation. <br />Although adult Colorado squawfish may migrate long distances, movement within their home <br />range is relatively limited. In the Yampa River, Wick and Hawkins (1989) found that squawfish <br />were often active within a particular habitat but rarely moved outside the reach (average of 0.3 <br />miles) selected for overwintering. Valdez and Masslich (1991) also found that Colorado squawfish <br />generally overwinter in localized Green River regions (3-5 km long). <br />Habitat Use <br />During spring runoff, many native and nonnative fish species (including Colorado squawfish and <br />northern pike) utilize backwater habitats as refuge from high flows (Wick et al. 1983, 1986; Tyus <br />and McAda 1984; Osmundson and Kaeding 1989; Tyus 1990). Water temperatures are higher in <br />backwaters and provide better conditions for growth and gonad maturation (Wick et al. 1983,1986; <br />Osmundson and Kaeding 1989; Tyus 1990). Wick et al. (1983) suggested that the warmer spring <br />backwaters may influence the spawning time of migrant fish. Osmundson and Kaeding (1989) <br />Final Report - Colorado squawfish habitat Page 4 <br />Miller Ecological Consultants, Inc. December 17, 1997