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HABITAT AND GEOPHYSICAL CHARACTER, UPPER COLORADO RIVER <br />The width, depth and physical characteristics of the Upper Colorado <br />River vary greatly by geographic area and also vary with quantity of <br />flow. Some of the deeper areas recorded in the study were Cataract <br />Canyon with a maximum depth of 92 ft and Black Rocks and Westwater <br />Canyons with maximum depths of about b0 ft. In the Green River a maximum <br />depth of about 60 ft was recorded for Gray Canyon and up to 28-ft depths <br />were recorded for the lower Green River in Labyrinth Canyon. Average <br />depths for cross sections of the different river strata varied from <br />about 2 ft to over 60 ft. <br />Various habitats in the upper Colorado River were quantified at key <br />locations using computer modeling developed by the FWS Instream Flow <br />L <br />Group (IFG) methodology (3~a appendix G ). Three hydraulic stations on <br />the Green River were modeled;~Mineral Bottom (RM 56), Ouray (RM 248), <br />and Gray Canyon (RM 141); and three stations were modeled on the Colorado <br />River at Black Rocks (RM 136), Potash (RM 53) and Moab (RM 73). Analyses <br />were made to evaluate potential habitats suitable for young a~-3s~a~ `- <br />a.~ squawfish and j::~e~il~e-~ adult humpback chub at these sites. <br />Flow changes experienced in the Upper Colorado River were analyzed <br />by looking at hydrologic time series at the six hydraulic stations <br />mentioned above. Actual USGS gaging station flows for 1960-1980 were <br />compared to modeled flaws depicting: (1) virgin flow conditions without <br />any development in place, and (2) developed flow conditions with 1980 <br />development projected from historic conditions. Temperature modeling <br />was also done to determine effect of flow changes on river temperatures <br />at the key hydraulic stations. <br />Generally, the IFG hydrologic time series analysis shows that <br />there have been significant peak flow reductions on both the Green and <br />Colorado Rivers. The Colorado under present-day conditions has had the <br />average monthly peak flow reduced by about 407 while the Green River has <br />experienced an average peak monthly flow reduction of abaut 25 to 40x. <br />Changes in instantaneous peaks or daily maximum flows has changed by <br />even a greater degree. These changes in peak flow have correspondingly <br />resulted in higher low flows during the fall and winter through the <br />release of reservoir storage waters. <br />River morphology and habitat is primarily determined by peak flow <br />levels, magnitude and duration. What has occured in both the Colorado <br />and Green River with reduced peak flows is that these rivers no longer <br />move the volume of sediment material through the system that they once <br />did. This has resulted in mare silt/sand areas, braided channels and <br />aggradation of the main river channel. The result has been fewer deep <br />r ns, fewer clean gravel-rubble areas and a reduction in the frequency <br />duration of overbank flows, especially on an annual basis. v <br />With reduced peak flows, water temperatures are wa~ming more <br />quickly during the spring runoff period in the Coloradgft~'The opposite `-" <br />occurs in the Jensen area of the Green River with the cold water released <br />from Flaming Gorge Reservoir depressing temperature during the summer. <br />G <br />