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<br />I <br /> <br />I <br /> <br />Open Space <br /> <br />2 <br /> <br />I <br /> <br />U.S. Army Corps of Engineers in Omaha, Nebraska, based on their hydrologic <br /> <br /> <br />analysis experience along the front range. Depression and detention storage <br /> <br />was selected to be consistent with the Fossil Creek and Dry Creek studies. <br /> <br /> <br />Subcatchment roughness characteristics were based on field investigation and <br /> <br /> <br />selected to be similar to the previous studies. Channel unit lengths, slopes, <br /> <br /> <br />and geometries were defined from field surveys and from 1:1200 scale <br /> <br /> <br />topographic maps from Larimer County, Colorado, where available (reference 14) <br /> <br />or U.S. Geological Survey 1:24000 scale topographic maps (reference 13). <br /> <br /> <br />Manning's roughness coefficients were based on field investigation. Table 6 <br /> <br /> <br />lists the parameters used and the range of values selected. Storage discharge <br /> <br /> <br />curves for ponding behind channel crossings were defined from topographic <br /> <br /> <br />mapping and weir flow equations. The ponded areas along Cooper Slough were <br /> <br /> <br />upstream of the crossings at State Highway 14, Colorado and Southern Railroad <br /> <br /> <br />and Vine Prive. The ponded areas along Boxelder Creek were upstream of 1-25 <br /> <br /> <br />near Fort Collins and Wellington, State Highway 14, abandoned Colorado and <br /> <br />Southern Railroad, Vine Drive, Larimer-Weld Canal and Willox Lane. Stage- <br /> <br /> <br />discharge curves were presented in the "Technical Addendum" (reference 10). <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />Table 5. Percent Impervious for Fully Developed Zoning Conditions. <br /> <br />I <br /> <br />I <br /> <br />Land Use <br /> <br />Density <br /> <br />Percent Impervious <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />Industrial <br />Commercial <br /> <br />80 <br />90 <br /> <br />I <br /> <br />I <br /> <br />Residential <br />(inside Urban Growth Area) <br /> <br />4.0 dwelling units <br />per acre <br /> <br />40 <br /> <br />I <br /> <br />I <br /> <br />Residential/Agricultural <br />(outside Urban Growth Area) <br /> <br />0.43 dwelling units <br />per acre <br /> <br />6 <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />Results <br /> <br />Rainfall-runoff data were not available for the Cooper Slough or Boxe1der <br /> <br /> <br />Creek basins. For this reason, the results of the Fossil creek and Dry Creek <br /> <br /> <br />studies were used to evaluate and justify the results of this study. The peak <br /> <br /> <br />discharges per square mile from Dry Creek and Cooper Slough are very similar. <br /> <br />The Fossil Creek basin produces higher peak flows per square mile because of <br /> <br /> <br />steeper slopes and lower infiltration rates than the Boxelder Creek and Cooper <br /> <br /> <br />Slough basins. The Boxelder Creek drainage basin is longer and flatter than <br /> <br /> <br />Dry Creek and has lower unit area peak discharges. A comparison of the study <br /> <br /> <br />results with the previous studies was presented in the Technical Addendum. <br /> <br /> <br />A summary of the peak flows for existing and developed conditions in the <br /> <br /> <br />Cooper Slough basin is given in Table 7. A summary of peak flows for the com- <br /> <br /> <br />bined Boxelder Creek-cooper Slough basins is given in Table 8. The discharge <br /> <br />profiles which show the change in flow rate along the study reach for Boxe1der <br /> <br /> <br />Creek are given in Figure 5. Figures 6 and 7 present the discharge profiles <br /> <br /> <br />for Cooper Slough for existing and developed basin conditions, respectively. <br /> <br /> <br />The flood hydrographs at State Highway 14 are given in Figure 8, for Boxe1der <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />11 <br />I <br />, <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />20 <br /> <br />I <br /> <br />21 <br /> <br />I <br /> <br />II <br />