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INSTREAM FLOWS TO ASSIST THE RECOVERY OF ENDANGERED FISHES 9 <br />Gunnison (i.e., downstream from the Redlands <br />diversion dam; a few are isolated upstream), and <br />mainstem Colorado rivers (downstream from the <br />Grand Valley diversion dams; Fig. 1). <br />Colorado squawfish are long-lived piscivores <br />that grow to more than a meter in length and <br />exhibit long migrations (e.g., between White and <br />Yampa rivers; Tyus 1990) associated with 15-20° <br />C isotherms (my interpretation based on data in <br />Tyus 1984, 1990). The fish spawn on chute chan- <br />nels (Harvey et al. in press) that form on specific <br />alluvial bars in the Yampa and Green rivers (Fig. <br />2) in association with the decline of spring runoff <br />and spates (Nesler et al. 1988; Tyus 1990). Eggs <br />of squawfish hatch within about 5 days after <br />spawning at 20-22° C, which is the critical tem- <br />perature for successful reproduction (Hamman <br />1981; Haynes et al. 1984; Tyus and McAda 1984; <br />Marsh 1985). Upon hatching, larvae drift down- <br />stream (Fig. 3), where they are entrained in back- <br />water nursery habitats in alluvial reaches (shown <br />generally in Fig. 1). In lab experiments, young of <br />500 <br />400 <br />300 <br />200 <br />100 <br />M <br />E <br /> <br />220 <br />4De-erikomdoe <br />1s0 <br />140 100 60 '•4 <br />1985 <br />20 Z Meybeu <br />20 25 30 5 10 15 20 25 30 5 10 <br />JUN JUL AUG <br />the year (YOY) prefer and grow best at 25° C <br />(Black and Bulkley 1985). The YOY and juveniles <br />are most often found in specific low velocity envi- <br />ronments, created by the complex relationship of <br />flow and channel geomorphology (Fig. 2). These <br />nursery and rearing sites also are inhabited by <br />native and nonnative fishes, particularly flannel- <br />mouth sucker (Catostomus latipinnis), roundtail <br />chub, green sunfish (Lepomis cyanellus), red <br />shiner (Cyprinella lutrensis), sand shiner (Notro- <br />pis stramineus), and channel catfish (Ictalurus <br />punctatus), that compete with the endangered <br />fishes for available food resources or prey on them <br />directly (Valdez and Wick 1983; Karp and Tyus <br />1990). Adult squawfish also prefer areas of the <br />channel that are braided and complex, where low <br />velocity habitats (e.g., eddies, pools, and slow <br />runs) are abundant. Like razorback sucker, adult <br />squawfish tend to move in and out of large back- <br />waters that form on downstream ends of backbar <br />channels and terrace- or wall-based channels <br />(Fig. 2), which remain connected to the main <br />500 <br />so z 400 <br /> M <br />60 E 300 <br />., 3 <br />40 O, L6 200 <br />20 P* <br /> 100 <br />140 260 <br />Deerbdge <br />120 <br />Z 220 <br />1001 <br />q M 180 <br />3 140 <br />? <br /> <br />80 o <br />60 <br />b <br />100 . <br /> <br />Maybell <br /> 60 <br /> <br />40 <br />20 r <br />20 20 25 30 5 10 15 <br />JUN JUL <br />so z <br />3 <br />60 <br />400, <br />20 ? <br />50 <br />1986 <br />40 e <br />3 <br />30 <br />0 <br />20' <br />10 <br />5 10 <br />AUG <br />Fig. 3. Relationships of Colorado River squawfish spawning dates (vertical bars, data derived from larval drift rates <br />adjusted for hatching time) to Yampa River flows measured at the Deerlodge and Maybell gauges in 4 years. <br />Number of fish represents number of larval fish sampled and distributed according to estimated spawning date <br />(from Nesler et al. 1988). <br />20 25 30 5 10 15 20 25 30 5 10 <br />JUN JUL AUG <br />20 25 30 5 10 15 20 25 30 5 10 <br />JUN JUL AUG