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• DRAFT February 25, 1998 <br />Thus, flow-habitat relationships regarding nursery habitat availability for Colorado <br />squawfish include both antecedent-condition and flood magnitude components. The <br />recommended flood cycle over a period of years should include both occasional large <br />floods that rebuild channel topography and more frequent lower magnitude floods. The <br />current practice of extending the duration of low-peak floods should be re-evaluated. If <br />the prolonged peak's stage is greater than the bar tops but less than bankfull, then neither <br />the habitats associated with the bars or with the floodplain are available, a condition that <br />was typically of very short duration for the Green River prior to dam closure. The target <br />summer flow should be dependent on existing channel morphology and hence will need to <br />be evaluated annually, although the conceptual model presented could be useful in <br />advance planning of flow needs. Winter flows and their impact on overwinter habitat <br />availability and degradation must be evaluated. <br />Model simulations indicate that shear stress, and hence sediment transport, is a function of <br />depth, so that the discharge necessary to build bars in this sediment abundant system are a <br />function of depth of flow over the bar rather than absolute discharge. Consequently, when <br />antecedent topographies are lower, it is expected that a lower discharge would be <br />necessary to build bars. The flow conditions during this study were insufficient to test this <br />hypothesis but future work could address this issue. <br />• <br />Schmidt, J.C. 1994. Annual Report: Compilation of historic hydrologic and geomorphic <br />data for the upper Colorado River basin. Flaming Gorge Research Program, Study #37, <br />Department of Geography and Earth Resources, Utah State University, Logan, Utah. 5p. <br />Preliminary results of ongoing investigations of the geomorphology and hydrology records <br />of the Green River Basin are: <br />1. The magnitude of the annual peak discharge of the Green River upstream from the <br />Yampa River has decreased about 60 percent from the 1923-1962 period to the period <br />following closure of Flaming Gorge Dam. At Jensen and Green River, LIT, the changes <br />have been about 25 percent, depending on the recurrence of the flood being evaluated. <br />Floods on the Yampa River have been unchanged during the same periods. <br />2. The highest floods of this century occurred between in the early part of this century. <br />Instantaneous peak discharge at Green River, UT, exceeded 60,000 ft3/s in 1897, 1909, <br />1917, and 1921. Peak flows at Greendale are estimated to have exceeded 20,000 ft /s in <br />1899, 7918, and 1921 (Figure 2). These floods are unprecedented; the fact that floods of <br />this magnitude do not occur at present may be related to climatic change and be unrelated <br />to the existence of dams. The effects of these floods -on habitat availability have not been <br />evaluated. <br />• <br />25