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Last modified
7/14/2009 5:02:29 PM
Creation date
5/17/2009 11:16:05 PM
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UCREFRP
UCREFRP Catalog Number
7046
Author
Valdez, R. A., W. J. Masslich and A. Wasowicz.
Title
Final Report\
USFW Year
1992.
Copyright Material
NO
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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 />7. The percentage of Dative fish species in the Dolores River was relatively high when compared <br />to other upper basin systems; 13% in 1990, 32% in 1991, 19% for the study. <br /> <br />8. Native fish species including flaooelmouth sucker, bluehead sucker, roundtail chub and <br />speckled dace were found with evidence of successful reproduction in the Dolores River. <br /> <br />~ORECO~NDATIONS <br /> <br />1. The operation of McPhee Dam should consider enhancing the suitability of the Dolores River <br />for Colorado squawfish and protecting existing native fisheries. Flows observed in the Dolores <br />River during this study indicate that the operation of McPhee Dam has the potential to adversely <br />or beneficially impact native fisheries by altering timing and magnitude of flows. Extremely low <br />flows (20-50 cfs) released on a year round basis are potentially devastating to aquatic resources <br />as well as other aspects of the rivers corridor (i.e. productive cobble riffles, riparian vegetation). <br />Potential impacts include: 1) reduced survival and recruitment of early year classes caused by <br />unnatural temperature regimes, 2) winter kills due to inadequate water volume, 3) lack of access <br />and disruption of fish movement because of inadequate water volume, and 4) increased stress <br />associated with water quality problems at extremely low flow. Specific flow recommendations <br />include: <br /> <br />a Increase minimum base flows to 78 cfs during wet and normal years and 50 cfs (or equal to <br />reservoir inflow in less than 50 cfs) during dry years. <br /> <br />b. Spring and summer flows should simulate the shape of the natural hydrograph. Peak flow <br />should approximate peak inflow to McPhee Reservoir. Ramping up should commence as <br />soon reservoir inflow increases to avoid early warming in the Dolores River below McPhee <br />Dam. Following peak flow, a period of at least 30 days should be utilized for gradual down <br />ramping to a base flow. Ideally ramping of flows to base conditions should be done in a <br />manner to approximate relative magnitude of decreasing inflow into the reservoir. <br /> <br />c. Downstream flow releases should prioritize maintaining aquatic systems. The release of large <br />volumes of water to provide short term downstream benefits should not be allowed if it <br />results in loss of flexibility in managing flows for the system during the course of the year. <br /> <br />2. Additional research should be conducted to better understand use of the Dolores River by <br />Colorado squawfish. This should include additional sampling during spring runoff and during a <br />high flow year. <br /> <br />3. Monitoring should be continued in the Dolores River to assess biological recovery associated with <br />ongoing changes in the system. These changes include the continued clean up of the Uravan mill <br />site, Reclamation's desalinization project in Paradox Valley, and potential changes in the <br />operation of McPhee Dam. <br /> <br />4. An efficiency evaluation of Reclamation's Dolores River project should be conducted. Since <br />much of the water withdrawn for the Dolores Project is used to irrigate agricultural land in the <br />San Juan River Basin, return flows associated with overwatering and other inefficient water use <br />practices provide no benefit to aquatic resources in the Dolores River drainage. The cost of <br />inefficient irrigation practices is high for the Dolores River ecosystem and should be evaluated <br /> <br />25 <br />
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