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2 <br />reproducing. The bottom fauna changed from large warmwater species to <br />small coldwater species and algae dominated the plant community. <br />Some changes in the Gunnison River have been recorded as a result <br />of earlier impoundment. Williams (1951) indicated that Taylor Reservoir, <br />approximately 60 miles upstream from the Curecanti Project, decreased <br />silt loads and lowered summer water temperatures. Wiltzius (1966), <br />after analyzing willow fly (Pteronarcys californica) emergence dates, <br />suggested that Taylor Reservoir has a warming effect on the Gunnison <br />River during early spring. <br />In anticipation of changes in aquatic fauna within the Monument, <br />determination of water temperature regimen, flow characteristics, river <br />habitats, fish species present, condition factor, and fish distribution <br />before, and during upstream impoundment was sought. <br />The objective of this study is to provide a base for detection of <br />subsequent changes in the fish fauna within the Monument. This study <br />is qualitative due to the severe physical nature of the study area that <br />limited access and types of gear used. <br />LOCATION AND DESCRIPTION OF BLACK CANYON OF THE GUNNISON NATIONAL MONU- <br />MENT - - <br />Black Canyon of the Gunnison River is in southwestern Colorado be- <br />tween Sapinero and Montrose, Colorado. Most of the Canyon is in Gunni- <br />O <br />son and Montrose counties. The region, topographically, is a transition <br />zone between the Southern Rocky Mountains to the east and Colorado Pla- <br />teau to the west. <br />Black Canyon of the Gunnison National Monument (Figure 1) comprises <br />0 <br />approximately 10 miles of the narrowest, deepest, and most spectacular <br />portion of the 50 mile canyon. Canyon walls range in height from 1,700 <br />to 2,400 feet. Width at the rim is as narrow as 1,300 feet while the