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INTRODUCTION <br />The Green River, a major tributary of the Colorado River originating in southwestern <br />Wyoming, has a drainage area of 115 770 square kilometers in Colorado, Utah and Wyoming <br />(fig. 1). Iorns et al. (1965) described the surface water and sediment yield data for the Green <br />River Basin. The headwater areas in the northern and eastern edges of the Green River Basin <br />serve as the principal areas of water source. Semiarid portions of the basin at lower elevations <br />contribute the majority of sediment. The Green River is controlled by two reservoirs, Fontenelle <br />and Flaming Gorge. Flaming Gorge Dam, downstream from Fontenelle and completed in 1962, <br />has an active capacity of 4.3 million cubic dekameters. The average annual inflow to Flaming <br />Gorge Reservoir is about 1.5 million cubic dekameters. The dam is located 660 kilometers <br />upstream from the confluence of the Green and Colorado Rivers. <br />Green River Studies Performed by Others <br />The study reported herein continues the work reported by Andrews (1986), who studied the <br />impact of Flaming Gorge Dam upon channel morphology and suspended sediment transport of <br />the Green River. Andrews described post-reservoir flow pattern changes and suspended <br />sediment transport measured at stream-gauging stations, and reported channel width trends <br />for short reaches of the river following dam closure in 1963. Andrews concluded that a condition <br />of quasi-equilibrium indicated by the absence of net aggradation or degradation existed on the <br />Green River before 1962. Construction of the dam caused changes in channel width and flow <br />and sediment patterns. <br />Andrews reported channel degradation for the Green River upstream from the Yampa River, <br />where sediment-free releases from Flaming Gorge occur and the majority of sediment load is <br />obtained from the bed. Downstream from the Yampa River to the Duchesne River, Andrews <br />noted a new quasi-equilibrium. Below the Duchesne River, he described aggrading river <br />conditions. Andrews concluded that the quasi-equilibrium in existence prior to reservoir <br />completion no longer exists along the majority of the Green River. He also stated that the <br />potential for future significant channel narrowing exists for the Green River. Using a constant <br />rate of channel narrowing calculated by comparing historical aerial photography, he estimated <br />that this narrowing may not be complete for about 30 years in a study area located about 170 <br />kilometers below Flaming Gorge Dam. <br />Andrews and Nelson (1989) studied the effects of discharge variations on a mid-channel bar <br />located about 250 kilometers below Flaming Gorge Dam in the Green River. Their comparison <br />of historical aerial photographs taken about the time of construction of Flaming Gorge (1964) to <br />those taken in 1986 demonstrated the long-term stability of this bar. They reported results of a <br />numerical model study that described evolution of bar topography over a nearly 10-fold range in <br />discharge. Their calculated rates of bar evolution indicate a rapid adjustment in bar topography <br />in response to changes in discharge. <br />These topographic changes, estimated to occur within several days to a few weeks following a <br />change in discharge, were observed for discharges of 475 cubic meters per second