Laserfiche WebLink
<br />3.6.4 Time of Concentration: In accordance with the USDCM, the modified CUHPF/PC <br />procedure was used for subwatersheds less than 90 acres. The modified CUHPF/PC <br />procedure produces peak flows similar to the rational method and requires a time of <br />concentration value for each subwatershed modeled. Equations 3-2, 3-3 and 3-4 from the <br />Runoff chapter of the USDCM (Volume I) were used to determine the time of concentration. <br />The velocity parameter used to determine the travel time variable in Equation 3-2 was <br />estimated from a trapezoidal channel having the geometry used for the UDSWM386 model, a <br />slope determined from the enlarged (1"=1,000') USGS quadrangle map, a Manning's 'n' of <br />0.04, and the 5-year discharge. A comparison of the results for each equation was made and <br />the shortest time of concentration was used for modeling purposes. Time of concentration <br />values generally ranged from 19 to 50 minutes. <br /> <br />3.6.5 Retention Storage Losses: Retention storage losses were determined according to Table <br />2-1 of the Runoff chapter of the USDCM. For future conditions, the retention storage losses <br />were assumed to be 0.05 inch for impervious areas (representing sloped roof areas). Retention <br />storage losses in pervious areas were assumed to be 0.4 inch. <br /> <br />3.6.6 Infiltration Losses: The infiltration parameters (initial infiltration, final infiltration, and <br />decay coefficient) were computed from Table 2-2 from the Runoff Chapter of the USDCM <br />based on an area weighted average of hydrologic soil type. The weighted average of <br />hydrologic soil type for each subwatershed was computed by superimposing the hydrologic <br />soils maps (Figures 2.IE and 2.1 W) onto the subwatershed maps (Figures 3.1E and 3.1 W). <br /> <br />3.7 UDSWM386 Modeling <br /> <br />3,8 <br /> <br />A UDSWM386 model was created to route the CUHPF/PC generated hydrographs through <br />the existing stream network. Conveyance element parameters required for the UDSWM386 <br />model include the conveyance element identifier, channel bottom width, length, invert slope, <br />side slopes, hydraulic roughness, and routing connectivity. A summary of these <br />characteristics is shown in Table 3.5 (located in Appendix A) and the methods for estimating <br />these characteristics are described in the following sections. <br /> <br />3.7.1 Conveyance Element Identification Number: Conveyance elements were numbered <br />from downstream to upstream for each stream as shown in Figures 3.2E and 3.2W. All <br />conveyance elements were identified according to the upstream design point. Design points <br />were located at the outfall of each tributary subwatershed and numbered according to the <br />highest subwatershed ID tributary at that point. <br /> <br />3.7.2 Stream Geometry: All streams were modeled as trapezoidal cross-sections. Bottom <br />widths, lengths, invert slopes, and side slopes were estimated from either detailed mapping at <br />a scale of 1"=100' or the enlarged USGS quadrangle map at a scale of 1"=1,000', depending <br />on availability. In some cases, streams were represented by a base flow channel and an <br />overflow floodplain channel. <br /> <br />3.7.3 Roughness: The roughness or Manning's "n" value for each conveyance element was <br />determined using Equation 2 from the UDSWM386 Users Manual (UD&FCD 1985b), which <br />is shown below: <br /> <br />n = 0.303 . (S)038 . (R) .016 <br /> <br />where: <br /> <br />n = Manning's roughness coefficient <br />S = Friction slope (feet/feet) <br />R = Hydraulic radius (feet) <br /> <br />This equation is the result of research work by Robert D. Jarrett of the USGS (Jarrett, 1984) <br />and is recommended for hydrologic routing in natural channels. For this study, the friction <br />slope was approximated using the invert slope and the hydraulic radius was approximated for <br />100-year flood conditions. The Manning's "n" value for the conveyance elements generally <br />ranged from 0.067 to 0.133. <br /> <br />3.7.4 Routing Connectivity: The routing connectivity of the conveyance elements, design <br />points, and subwatershed hydrographs were incorporated into the UDSWM386 models <br />according to the SWMM Routing Schematic diagram provided in Figure 3.3. <br /> <br />3.7.5 Existing Ponds: The existing dam and reservoir in the upper reaches of the Willow <br />Creek Watershed was ignored because it is privately owned. However, Little Willow Creek <br />was routed through the existing detention pond in the Roxborough Village Subdivision, as <br />well as the Platte Canyon Reservoir. <br /> <br />Results <br /> <br />Table 3.6 (located in Appendix A) presents the peak discharges from the UDSWM386 model <br />at various design points along the main channels for the 10-, 50-, 100-, and SOD-year storm <br />events. Figures 3.4, 3.5, 3.6 (located in Appendix A) present discharge profiles along the <br />main channels for the 10-, 50-, 100-, and SOD-year storm events. Figure 3.7 shows typical <br />hydro graphs at selected locations. <br /> <br />The following information is also provided in the separately submitted Technical Addendum <br />to this report. <br /> <br />1. Summary output tables from the UDSWM386 model for the 10-,50-, 100-, and 500- <br />year storm events for future development conditions. <br />2. Discharge profiles along the main channels for the 10-, 50-, 100-, and 500-year storm <br />events. <br />3. The routed hydrographs at roadway and canal crossings, as well as existing detention <br />facilities for the 10-, 50-, and 100-year storm events. <br /> <br />14 <br />