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<br />2 <br /> <br />endangered species. These studies indicated that proper operation of <br />Flaming Gorge Dam was critical to the survival of various life stages of <br />endangered species. Therefore, an environmental study involving Reclamation <br />and FWS was initiated in 1986 in response to a FWS request and the pending <br />Section 7 Consultation for the Biological Opinion concerning the operation <br />of Flaming Gorge Dam and the proposed upgrade of Flaming Gorge Dam <br />generators increased hydropower production. The Endangered Species Act of <br />1973 (Public Law 93-205) charges Federal agencies to consider the needs of <br />listed species and produce biological opinions relative to the impacts of <br />planned and operating projects. <br /> <br />Studies conducted by the FWS and others have concluded that backwaters in <br />the Green River serve as important nursery habitat for young-of-the-year <br />Colorado squawfish (Tyus et al. 1987, Tyus and McAda 1984). Colorado <br />squawfish spawn during mid to late summer, and their larvae become <br />distributed in shallow backwater habitat that reduces predation and adverse <br />flow events (Tyus et al. 1987). Therefore, it is assumed that maximizing <br />backwater habitat during summer will increase the survival rate of young <br />Colorado squawfish. <br /> <br />In response to a request from Mr. Reed Harris and Mr. Bob Williams of the <br />Upper Colorado Regional Office (Reclamation), the feasibility of using <br />remote sensing techniques to study backwater habitat availability in the <br />Green River below Flaming Gorge Dam was examined. A pilot study was <br />developed in 1986 using color infrared (CIR) photography and Geographic <br />Information Systems (GIS) techniques to examine backwater availability in <br />response to different Green River flows. The pilot study proved successful, <br />and in 1987 an expanded study was initiated which examined the relationships <br />between seven different flows and backwater area and number at five sites on <br />the Green River in Utah. The objective of the 1987 study was to establish a <br />data base that would allow optimization of Green River flows for backwater <br />availability during late summer when young-of-the-year Colorado squawfish <br />would be present. During 1988 the Green River backwater study was <br />continued. The 1988 study was originally designed to test fluctuating flow <br />conditions and their effect on backwater habitat development. However, <br />extremely low-flow conditions produced by the drought preempted the <br />scheduled study. These stable low flows presented a unique situation to <br />establish a relative baseline condition for riverine habitat. Approximately <br />320 miles of the Green River from about Island Park to the Colorado River <br />confluence were photographed during the low flows that occurred during the <br />summer. The objective of the 1988 study was to establish baseline <br />conditions for backwater availability at extremely low flows, or a "normal" <br />summer hydrograph, for this portion of the river. <br /> <br />Aerial photography is currently thought to be the optimum method for mapping <br />and determining various riverine habitat availability. Future monitoring of <br />the Colorado River and its tributaries will be necessary to observe long- <br />term habitat trends vital for the survival and enhancement of endangered <br />fish populations. However, monitoring several hundred river-miles (rm) for <br />many years may prove prohibitively expensive. Therefore, in a related <br />project, a more cost-effective alternative for mapping backwater <br />availability using videography was investigated during 1988. This study <br />