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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />elevation the bottomland could be inundated by flows measured at Jensen as low as 14,000 cfs (Figure 3, <br /> <br />flow data provided by George Smith, USFWS). This is 3,000 to 6,000 cfs lower than estimated by Cooper <br /> <br /> <br />and Severn (1994) in the absence of contour elevation data. The elevation of the inlet to Old Charley Wash, <br /> <br /> <br />4,651 fas!. The estimated minimum water discharge required to enter Old Charley is estimated to be 8,500 <br /> <br /> <br />cfs. Little historic data exists on the length of time water is retained in Old Charley Wash, however, last year <br /> <br /> <br />following a relative high flow year (spring peak exceeding 20,000 cfs) water was retained in the bottomland <br /> <br /> <br />through September. Cooper and Severn (1994) suggested the water elevation of Old Charley Wash is <br /> <br /> <br />closely correlated with water elevation in the Green River. Evaporation rates of the wetland are estimated <br /> <br />to be 2.5 feet between July and October. <br /> <br /> <br />Cooper and Severn (1994) described Old Charley Wash as a sodium-calcium sulfate-bicarbonate <br /> <br /> <br />type water (chloride occurs in low concentrations compared with sulfate and bicarbonate). Water <br /> <br /> <br />conductivity was relatively low compared to other waters sampled on the Ouray National Wildlife Refuge with <br /> <br /> <br />most open water measurements ranging between approximately 300 and 600 umhosjcentimeter. Dissolved <br /> <br /> <br />oxygen ranged between 2 and 11 ppm in July and August. Several other chemical variables were measured <br /> <br /> <br />by Cooper and Severn (1994) and none appeared to be of biological concern. Water samples were tested <br /> <br /> <br />for selenium but concentrations were not detectable. Currently, Old Charley Wash has a water control <br /> <br />structure on both the inlet (elevation 4,651 fasl) and the outlet (4,646 fasl). A fish access control structure <br /> <br /> <br />was built into the outlet structure last fall. This spring, grading will be completed in Old Charley Wash to <br /> <br /> <br />allow contour draining of the bottomland. The water control structure at the inlet is currently operable, but, <br /> <br /> <br />needs to be repaired if it is to be used on a regular basis in the future. <br /> <br /> <br />Because Old Charley Wash is connected to the Green River at flows exceeding 14,000 cfs, the fishes <br /> <br /> <br />found in this wetland are identical to those occupying the Green River. In 1986, Tyus and Karp (1990) <br /> <br /> <br />reported 20 razorback sucker were collected from the outlets of Stewart lake and Old Charley Wash. <br /> <br /> <br />Colorado River Fish Project data records indicate that 42 adult razorback sucker have been collected <br /> <br /> <br />between Green River miles 251 and 248 between 1980 and 1992. Colorado squawfish adults implanted with <br /> <br /> <br />radio transmitters have also been observed occupying Old Charley Wash (Tyus and Karp 1991). In addition, <br /> <br />3 <br />