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n <br />b. In the interim period until consultation is completed, Reclamation has <br />committed to assist in meeting a 2,000 cfs minimum flow below the <br />confluence of the Gunnison and Colorado Rivers an average of 9 out of <br />10 years. Preliminary studies have been done to attempt to assess the <br />impact of Blue Mesa on the rare fish habitat and to determine Blue <br />Mesa's ability to offset these impacts and to contribute to the <br />recovery program. Any preliminary flow regime necessarily will be <br />' subject to refinement as additional scientific information is <br />accumulated but provides a basis for determining whether Blue Mesa <br />could assist in meeting flow needs in the interim period. <br />c. Reclamation and the Service will cooperate with the Implementation <br />Committee in establishing an instream flow right, pursuant to State <br />laws, to guarantee the delivery of any flow releases through fish <br />' habitat (see Section 4.1.3). <br />4.2 HABITAT DEVELOPMENT AND MAINTENANCE <br />Alteration and loss of habitat have contributed to the decline of the four <br />Colorado River fishes. Recovery of these species may be aided by assessing <br />the quantity and quality of habitat needed for recovery and by developing or <br />enhancing habitat through management techniques, such as instream flows, <br />creation of backwaters, or other nonflow activities, etc. The use of any of <br />these management techniques will also be considered in relation to the <br />1 successful implementation of other habitat management techniques to provide a <br />balanced contribution from each. Initially, the habitat development and <br />enhancement techniques described in this chapter will be applied <br />experimentally to determine if the rare fishes will use developed habitat and <br />' if such techniques contribute to recovery. Appropriate permits and NEPA <br />compliance will be required. <br />Habitat management techniques will be tested in a variety of habitat types, <br />including backwaters, spawning habitat, grow-out (rearing) areas (see <br />Section 4.3.2), or will be used to open new habitat through the construction <br />of fish passages and jetties. Testing should address the questions of <br />' quantity of specific habitats needed and the problems associated with habitat <br />quality. For instance, if lack of backwater habitat is contributing to the <br />low numbers of young-of-the-year squawfish, then increasing the quantity of <br />backwaters may increase the abundance of young squawfish. Likewise, if lack <br />of habitat quality is the problem, the focus should be on improving, in <br />selected locations, the quality of existing backwaters and spawning habitat by <br />improving flows, water temperature, water chemistry and turbidity, decreasing <br />the numbers of predatory.fish, etc. The role of changing flows in creating <br />important ephemeral backwater habitat must also be determined. <br />4.2.1 Backwaters <br />Young-of-the-year Colorado squawfish are most often found in backwaters, since <br />backwaters provide nursery and feeding habitat. Backwaters can be created by <br />manipulating river flow to retain the characteristics typical of the river <br />system. Regulation structures such as Flaming Gorge can be operated to <br />' control river flow and temperature to maximize the quantity and quality of <br />backwaters in certain river reaches during periods when they are most critical <br /> <br />4-11