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Fishes of the San Rafael River system were <br />discussed by McAda et at (1980). Native fishes were <br />dominant in the tributary streams and middle sec- <br />tion of the San Rafael River, while introduced fishes <br />were dominant near the mouth of the river. <br />Fishes of the Upper Main-stem Colorado <br />Sub-basin <br />Joseph et at (1977) considered native and in- <br />troduced fishes of the Upper Main-stem Colorado <br />and factors affecting area streams. Introduction of <br />non-native fishes and waterflow reductions were the <br />main factors involved in declines of native species, <br />and oil shale development will surely add another <br />major obstacle to their survival. <br />The Gunnison River at one time contained all <br />threatened or endangered fishes of the Upper Col- <br />orado System except the Kendall Warm Springs <br />dace and the humpback chub. With the introduction <br />of non-native fishes, the abundance and distribution <br />of these native fishes was drastically curtailed <br />(Joseph et at 1977). Part of the Gunnison River was <br />once a world-famous trout fishery. Wiltzius (1978) <br />reviewed many studies done on the Gunnison after <br />1927 and discussed the quality and quantity of the <br />trout fisheries since the 1880's. Introduction of <br />several species, together with continued stocking <br />and other factors, played a role in changing the fish <br />fauna. Wiltzius also considered the effects of Blue <br />Mesa and Morrow Point reservoirs on the fishery of <br />the Gunnison. The fisheries in the tailwaters of <br />dams forming these and other major reservoirs in <br />the Upper Basin were discussed by Mullan et at <br />(1976). <br />Holden and Stalnaker (1975b) discussed the native <br />and introduced fishes of the Dolores, including their <br />abundance and distribution. The Dolores River <br />System appeared to have little importance regard- <br />ing preservation of rare and endangered fish species <br />and was far from its natural state due to irrigation <br />and severe pollution. <br />General notes on fishes of the Upper Main-stem <br />Colorado near Moab, Utah, were provided by Taba <br />et at (1965). Holden and Stalnaker (1975a) collected <br />near Moab, at three other sites on the Upper Main- <br />stem Colorado, and at one station on the Gunnison <br />River. <br />Fishes of the San Juan Sub-basin <br />Joseph et at (1977) stated that many of the native <br />large-river endemics of the San Juan River were <br />much reduced in distribution and abundance and <br />that some were probably extirpated. Navajo Dam <br />construction appeared to exert the major impact, <br />and competition from introduced species was <br />another significant factor. Koster (1960) and Minck- <br />ley and Carothers (1979) reported Colorado <br />squawfish captures from the San Juan River. <br />Fish encountered in the Glen Canyon area on the <br />Colorado River before construction of Glen Canyon <br />Dam included 17 species; only six were native <br />(Woodbury 1959). Major faunal collections came <br />from the tributaries as the river at this point was <br />rapid, showing much scouring and providing little <br />habitat for flora and fauna. <br />Water impoundment behind Glen Canyon Dam <br />began in January 1963. Largemouth bass were <br />stocked in the resultant Lake Powell in 1963 and <br />1964, and abundant stocks have been maintained by <br />natural reproduction (Miller and Kramer 1971). <br />Rainbow trout were also introduced in 1963; yearly <br />stocking continued but in later years was restricted <br />to the lower reservoir (May 1973). Introduction of <br />other fishes occurred in part to provide an abun- <br />dant, vulnerable food source for the four major cen- <br />trarchids (largemouth bass, black crappie, bluegill, <br />and green sunfish) in the reservoir (May and Thomp- <br />son 1974; May et at 1975). All resident species ex- <br />perienced changes in their food habits as feeding on <br />introduced threadfin shad increased. Introductions <br />of striped bass in 1974 and 1975 have provided <br />another species to the fishery. May and Gloss (1979) <br />studied depth distribution of major gamefishes in <br />Lake Powell in relation to oxygen and temperature <br />profiles. They referred to earlier, largely- <br />unpublished research on physical, chemical, and <br />biological characteristics of the reservoir. Diversity <br />of habitat in Lake Powell and of its community of <br />endemic and introduced fishes was emphasized. Pot- <br />ter (1980) provided an ecological description of Lake <br />Powell, stressing management of the resource. <br />Holden and Stalnaker (1975a) collected just below <br />Glen Canyon Dam and reported on fishes of that <br />area. Minckley and Carothers (1979) reported collec- <br />tion of razorback suckers near the mouth of the <br />Paria River. <br />ACKNOWLEDGEMENTS <br />We greatly appreciate reviews of drafts of this <br />paper by Robert Behnke, Harold Tyus, and William <br />Miller. The assistance of Darrel Snyder was par- <br />ticularly helpful. <br />5