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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />The resulting sediment transport values for the chosen stable design discharges were also <br />used to generate tables of stable channel dimensions for the channel improvements. The <br />improved channel models were similarly used to generate new sediment transport rating curves. <br /> <br />Sediment yields for the existing conditions are not presented in this report. Annual yields <br />are typically calculated by integrating the sediment transport rating curve with the flow-duration <br />curve for the area. Because of the deterioration in channel capacity within the problem areas, <br />reliable sediment transport curves for the existing conditions could not be obtained. The limited <br />range of flows modeled hydraulically (up to 1,000 cfs) does not provide an adequate <br />representation of the river hydrology. Based on the discharge frequency peaks presented in Table <br />3.2, 1,000 cfs does not cover enough of a range of flows to provide meaningful yield <br />calculations. <br /> <br />Stable channel geometry "templates" were generated for the three problem areas. These <br />are conceptual floodway cross-sectional configurations designed to balance sediment inflow and <br />outflow. The target values for inflowing bed sediment load were estimated from the most <br />efficient channel segments with at least 1,000 cfs capacity and other data sources. The channel <br />configurations are compound. That is, they have more than one prism. The sediment transport <br />values for the chosen stable design discharges were used to generate tables of stable channel <br />dimensions for the channel improvements. A low-flow trapezoid was designed to convey the <br />current channel capacity, estimated to be about 800 cfs. A second trapezoid with a capacity of <br />2,500 cfs was included to carry higher flows. The 100 to 1,000 cfs sediment transport rating <br />curve was extended through extrapolation and integrated with the flow-duration curve for the <br />pre-dam condition from the Lower Arkansas River Planning Assistance to States Study (1999a). <br />This indicated an effective discharge of around 2,500 cfs. These two channel sizes were <br />combined together, with the low-flow (800 cfs) channel cut within the 2,500 cfs channel. Both of <br />the channels used 1 V:2.5H sideslopes. The widths varied with each problem area. The channel <br />template dimensions are discussed below under the specific Problem Areas. The resulting <br />compound channels were inset into a simple, lO-point cross-section, idealized as a 700-foot <br />wide, lO-foot deep floodplain. A 400-foot length segment of this idealized configuration for each <br />problem area was modeled in HEC-2 and the improved channel models were used to generate <br />new sediment transport rating curves and calculate sediment yield and average concentrations. <br />The results are listed in Table 3.7 and shown graphically in Figure 5. The variables listed in <br />Table 3.7 are reasonably uniform, with a generally increasing trend in the downstream direction. <br />This promotes transport through the study reach, transporting sediment to John Martin Reservoir, <br />and allows for some increase in load from tributaries. <br /> <br />Table 3.7. Improved channel template sedimentation results. <br /> <br />Sediment Variable Problem Area 3 Problem Area 2 Prob. Area 1 <br />Mean Daily Load (ton/day) 2584 2673 2164 <br />Mean Daily Concentration (mg/L) 1717 1776 1438 <br />Annual Sediment Yield (ton) 942,902 975,619 789,624 <br />Annual Sediment Yield (cu. yds.) 751,017 777,076 628,932 <br /> <br />33 <br />