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<br />THE SOUTHWESTERN NATURALIST 30(1):129-140 MARCH 27, 1985 <br />EFFECT OF INCUBATION TEMPERATURE ON <br />SURVIVAL OF EMBRYOS OF <br />NATIVE COLORADO RIVER FISHES <br />PAUL C. MARSH <br />ABSTRACT.-Razorback sucker (Xyrauchen texanus [Abbott]), bonytail (Gila elegans Baird and <br />Girard) and humpback (G. cypha Miller) chubs, and Colorado squawfish (Ptychocheilus lucius) <br />Girard) comprise the endemic "big river" fish fauna of the Colorado River, western North Amer- <br />ica. All are near extirpation in the wild. Effects of incubation temperature upon embryo hatch <br />success were experimentally examined to evaluate potential impacts of cold hypolimnetic reservoir <br />releases upon species reproductive success. Eggs were spawned and fertilized at 18°C, and embryos <br />incubated at 5, 10, 15, 20, 25, and 301C. Total mortality of embryos of all species occurred in 12.96 <br />hours at 5, 10, and 30°C; and in 48-60 hours at 15°C for P. Lucius only. Survival and percentage <br />hatch were highest at 15 and 20°C (G. elegans) or 20°C (all others). Hatched prolarvae were 0.2-1.3 <br />mm TL longer at 20°C than at 15 or 251C. Spinal or other anomalies were more frequent at 15 <br />and 251C than at 20°C. Development rates (V) were similar for all species, 4.4-61 (15°C), 8.4-9.9 <br />(20°C), and 12.4-18.8 (25°C). Because of lower survival and higher incidence of anomalies at 15 <br />and 25°C, optimal temperatures for development and hatching are probably near 20°C. Reproduc- <br />tion may thus be limited in the wild by low water temperatures, although successful hatching is <br />certainly riot precluded. Other hypotheses to explain the demise of these fishes in thermally suita- <br />ble portions of the Colorado River, such as predation upon young, should be examined. <br />Razorback sucker (Xyrauahen texanus [Abbott]), bonytail (Gila elegans <br />Baird and Girard) and humpback (G. cypha Miller) chubs, and Colorado <br />squawfish (Ptychocheilus luci.us Girard) comprise the unique, endemic "big <br />river" fish fauna of the Colorado River of western North America. All are in <br />danger of extinction and are listed as threatened or endangered by one or <br />more of six western states (Deacon et al., 1979), and all but razorback sucker <br />are considered endangered by the U.S. Fish and Wildlife Service (USDI, <br />1980). <br />Historic ranges included larger rivers throughout the Colorado River <br />basin (razorback sucker, bonytail chub, Colorado squawfish) or middle and <br />upper Colorado and Green Rivers (humpback chub). Present distributions <br />are severely limited. Razorback suckers are found only above Grand Canyon <br />and in lakes Mead, Mohave, and Havasu on the lower Colorado River (Fig. <br />1); bonytail chub currently persist in Green River and Lake Mohave; hump- <br />back chub populations persist in the mouth of the Little Colorado River <br />and in Desolation Canyon of the Green River; and Colorado squawfish are <br />restricted to the upper river in Colorado, Utah, and Wyoming (Lee et al., <br />1980). <br />Declines of these and other native southwestern fishes have been attributed <br />to dewatering; mainstream dams and impoundments; altered stream flow, <br />channel morphology, and water quality; and introduction of exotic fishes <br />(Miller, 1961; Minckley and Deacon, 1968; Seethaler, 1978; Johnson and <br />Rinne, 1982). In particular it has been suggested that lowered water temper- <br />atures associated with hypolimnetic reservoir releases may curtail reproduc- <br />tion (Vanicek, 1967; Vanicek et al., 1970; Holden, 1973; Seethaler et al., 1976; <br />Joseph et al., 1977; Kaeding and Zimmerman, 1983).