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<br />FINAL REPORT, November 2()03 <br />High-flow Requirements for the Duchesne River <br /> <br />matched the total energy head in the main channel at the chute's upstream junction. Downstream <br />boundary conditions for modeling higher discharge were derived by fitting a curve to stages <br />measured at the downstream cross section over the observed range of discharges. <br />Input data for the Green River backwater model consisted of an estimate for Manning's n <br />for the Duchesne River and a downstream boundary condition comprising a stage-discharge <br />relationship for the Green River at the mouth of the Duchesne River. Cross sections of the <br />Duchesne River were assigned Manning's n values of 0.025. The lack of rigorous calibration of <br />this model is justified on the grounds that it is intended to predict only the spatial extent of <br />backwater effects extending up the Duchesne River from the Green River. River stage within <br />this backwater zone is primarily a function of stage at the downstream boundary such that local <br />channel roughness has little or no effect on local hydraulic conditions. This model is not <br />intended to accurately predict flow velocity or depth, and has no validity beyond assessment of <br />the influence of the Green River backwater. A stage-discharge relationship was previously <br />developed for Old Charlie Wash I, a site on the Green River approximately 500 m upstream <br />from the mouth of the Duchesne, as part of the US Fish and Wildlife Recovery Program for <br />Endangered Fishes of the Upper Colorado River (FLO Engineering 1997). We adjusted the <br />datum used at Old Charlie Wash to better match the elevation at the mouth of the Duchesne <br />River, and this relationship was applied as a downstream boundary condition to our model. As <br />geographic data in our model were derived from the work of LC Headwaters, Inc., the water <br />surface elevation at the mouth of the Duchesne River reported by LC Headwaters was used for <br />datum adjustment. LC Headwaters reported a water surface elevation of 1,425.2 m at a time <br />when the Green River discharge was approximately 18,000 ft3/S. <br /> <br />Sediment Sampling <br />Two standard pebble counts were conducted on each of two riffles at each detail study <br />site. Surface layer size distributions produced from these data allowed determination of mean <br />gravel size for use in critical shear stress analysis at each site. Bulk subsurface bed material <br />samples were also collected from riffles exposed at low flow at each site according to the 2- <br />percent criterion of Church et al. (1987). These samples were sieved through 8 mm screens in <br />the field, and the remainder was dry sieved through finer screens in the laboratory. Samples of <br />fine sediment were collected from several locations in pools and backwaters on occasions before <br /> <br />28 <br />