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at a range of flows, and 300 cfs provides minimum to adequate depths for fish movement. The <br />300 cfs is necessary to maintain approximately 1 foot -of depth through the critical shallow areas <br />of the river downstream from the Redlands Diversion Dam. A portion of the same water will <br />be used to operate the fish passageway. The Service and the State of Colorado will study and <br />evaluate the effects of the releases on occupied habitat of endangered fish in the Gunnison River. <br />Recommendations will be made, based on these studies, on development of a long-term water <br />supply contract. In addition, the effects of the interim water agreement on other water uses in <br />the basin will be monitored, thus providing important data for use in developing a long-term <br />contract. Appendix B highlights provisions of the drift agreement. <br />Three alternatives were considered for how the water agreement will address historic water use <br />patterns that have developed since the completion of the Aspinall Unit and these are discussed <br />below. Alternative A, which provides fish flows of 300 cfs from July through October and <br />historic levels of protection to water users based on water supplies and existing contracts as <br />discussed below, is the preferred alternative. Under all alternatives, including No Action, water <br />would be available for sale from the Aspinall Unit for municipal, industrial, irrigation, or other <br />purposes. <br />Alternatives <br />No Action <br />On any program, the "No Action" alternative exists. Under this alternative, a fish passageway <br />would not be constructed under the Recovery Program and the interim water agreement would <br />not be executed. There would be no special effort to maintain a flow of 300 cfs below the <br />Redlands Diversion Dam at this time, nor would there be special efforts to protect senior water <br />users downstream of the Aspinall Unit; however, water users would be expected to continue to <br />utilize Blue Mesa releases dependent on water supplies. The need for a fish passageway would <br />remain and a passageway could be constructed under other programs. Under No Action, the <br />endangered fish studies on the Gunnison River would still continue, leading to recommendations <br />for changing Aspinall Unit operations to protect the fish. However, the absence of a fish <br />passageway at the Redlands Diversion could impair the Recovery Program's ability to act as the <br />"reasonable and prudent alternative" to offset the impacts of water use and development, and as <br />a result both existing and future water use could be adversely affected under the Endangered <br />Species Act either economically or in ability to use water. <br />Fish Pa ew <br />Alternative designs for the fish passageway were also considered, and several different types of <br />passage structures were appraised. All but one of the alternatives had a vertical slot and orifice <br />in each baffle. The primary variable of the different alternatives was the location of the <br />passageway in relation to the diversion dam. Several alternatives were considered which <br />involved building the passageway over the Redlands Diversion Dam in different locations. These <br />9