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The pattern of the Yampa River through Dinosaur National Monument is <br />controlled by the local geology, but the character of the river, its local bed <br />and bank conditions, and the distribution of riparian vegetation are deter- <br />mined by the prevailing streamflow and sediment transport regime. Biological <br />and physical characteristics of this river system are affected by seasonally <br />controlled streamflows and intermittent transport and storage of sediment. <br />Much of the sand- and silt-size material introduced into the canyon reach from <br />Deerlodge Park is mobile at the lowest discharges; however, high discharges, <br />though relatively infrequent and of short duration, transport a large part of <br />the total annual sediment load (fig.. 7). <br />Reduced flood peaks and sediment transport through a river reach can <br />result in changes in channel geometry, bed-material size, and bank stability. <br />Schumm (1977, p. 159} summarized the metamorphoses of several rivers in <br />response to changes in mean annual flood, mean annual discharge, and type of <br />sediment load. Regulation of flood peaks can have pronounced effects on the <br />distribution of riparian vegetation as observed on the Green River above the <br />Yampa River (Potter and others, 1983). Dense vegetation encroaching on a <br />channel can promote accumulation of sediment and result in channel width <br />reduction. A reduction in annual streamflow can have a similar effect on <br />channel geometry, sediment transport, and riparian conditions. <br />The quantity and composition of sediment carried by a river also are <br />significant factors affecting river morphology. When the transport of sedi- <br />ment through a river reach is equal to the amount of sediment supplied to it, <br />the river is said to be in equilibrium, or graded. Changes in the amount of <br />sediment supplied to a reach can disrupt equilibrium and lead to aggradation <br />or degradation of the channel. Sediment surplus (or deficit) equals the <br />difference between supply to the reach and transport through the reach. <br />Sediment supply may be reduced progressively because of changes in climate or <br />land management that result in lower sediment yield, or because sediment is <br />being stored upstream in the channel or flood plain. More abrupt reductions <br />in sediment supply occur when sediment is trapped in manmade impoundments. <br />Depletion of annual streamflow due to transbasin diversions may be accompanied <br />by a reduction in transport capacity below a diversion structure, resulting in <br />diminished sediment supplied to downstream reaches. <br />The annual total sediment load can be reduced significantly if the <br />magnitude and duration of the highest increments of streamflow are altered, <br />even though the volume of annual streamflow remains unchanged. Since con- <br />struction of Flaming Gorge Reservoir on the Green River in Wyoming, the <br />magnitude and duration of high flows have been reduced, while the duration of <br />low flows has increased. Annual streamflow below the dam is equal to pre-dam <br />annual streamflow; but, the annual sediment load measured at a gaging station <br />located 106 mi downstream has declined by 54 percent (E. D. Andrews, U. S. <br />Geological Survey, oral common., 1983). <br />The potential effects of altering the distribution of discharges on sed- <br />iment transport through Deerlodge Park have been examined for several assumed <br />flow durations of the Yampa River. The historic duration of streamflows <br />(curve A, fig. 8) was decreased or increased by percentages equivalent to the <br />changes observed in the Green River near Jensen, Utah (station 09261000), flow <br />duration following the construction of Flaming Gorge Reservoir. The assumed <br />23 <br />