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<br /> <br />3.6.3 Slope <br /> <br />For area adjustment 1, 2-hour duration hyetographs were created by distributing the I-hour <br />rainfall depths according to Table 3-1 of the Rainfall chapter of the USDCM (UDFCD, <br />1969). No area adjustments were applied. <br /> <br />The slopes for each subwatershed were estimated according to the weighted slope method <br />documented in the USDCM. The length.of each sJlbwa.t~rshed was broken up into small <br />segments. The slope of each of the segments was computed and corrected according to <br />Figure 4-1 of the Runoff chapter of the USDCM (UDFCD, 1969). The segment lengths <br />and corrected slopes were entered into Equation 4-5 of the Runoff chapter of the USDCM <br />(UDFCD, 1969) to determine the weighted subwatershed slope. Weighted subwatershed <br />slopes varied from 0.2 percent to 4.9 percent in the study area. <br /> <br />For area adjustment 2, 3-hour duration hyetographs were created by adding rainfall <br />exceeding the 2-hour storm depth uniformly over the extended duration. The 3-hour <br />hyetographs were then adjusted according to the 10 to 20 square mile area adjustments <br />shown in Table 4-2 of the Rainfall chapter of the USDCM (UDFCD, 1969). <br /> <br />In accordance with the USDCM, the modified CUHP procedure was used for subwater- <br />sheds less than 90 acres (UDFCD, 1969). The modified CUHP procedure produces peak <br />flows similar to the rational method and requires a time of concentration value for each <br />subwatershed modelled (for example, subwatersheds less than 90 acres). For existing <br />development conditions, Equations 3-2 and 3-3 from the Runoff chapter of the USDCM <br />were used to determine the time of concentration (UDFCD, 1969). The velocity <br />parameter used to determine the travel time variable in Equation 3-2 was estimated from <br />Figure 3-1 of the Runoff chapter of the USDCM using the curve for short grass pasture <br />and lawns (UDFCD, 1969). <br /> <br />Time of Concentration <br /> <br />3.6.4 <br /> <br />For area adjustment 3, 6-hour duration hyetographs were created by adding rainfall <br />exceeding the 2-hour storm depth uniformly over the extended duration. The 6-hour <br />hyetographs were then adjusted according to the 20 to 30 square mile area adjustments <br />shown in Table 4-2 of the Rainfall chapter of the USDCM (UDFCD, 1969). <br /> <br />For area adjustment 4, 6-hour duration hyetographs were created as described for area <br />adjustment 3 and adjusted according to the 50 to 75 square mile area adjustments shown <br />in Table 4-2 of the Rainfall chapter of the USDCM (UDFCD, 1969). <br /> <br />I <br />I <br /> <br />I <br />I <br />I <br />I <br />I <br /> <br />Hyetographs for the 500-year event were based on the same temporal distribution as the <br />l00-year event. <br /> <br />I <br /> <br />For future development conditions, Equation 3-4 from the Runoff chapter of the USDCM <br />was used to determine the time of concentration, since it yielded shorter concentration <br />times than Equation 3-2 and 3-3 and Figure 3-1 of the USDCM (UDFCD, 1969). Time of <br />concentration values generally ranged from 30 to 120 !!linutes for existLng development <br />conditions. For future development conditions, the time of concentration values ranged <br />from 17 to 48 minutes. <br /> <br />Retention Storage Losses <br /> <br />Retention storage losses were determined according to Table 2-1 of the Runoff chapter of <br />the USDCM (UDFCD, 1969). For existing conditions, the retention storage losses were <br />assumed to be 0.05 inch for impervious areas (representing sloped roof areas) and 0.40 <br />inch for pervious areas (representing wooded areas and open fields). For future <br />development conditions, the retention storage losses were assumed to be 0.05 inch for <br />impervious areas (representing sloped roof areas) and 0.35 inch for pervious area <br />(representing lawn grass). <br /> <br />3.6.5 <br /> <br />CUHP Modelling <br /> <br />CUHP models for existing and future development conditions were developed for each <br />watershed (total of twelve base models). The 24 storms described in ta~e previous section <br />were modelled in each of the twelve base CUHP models. The subwatershed characteris- <br />tics required for the CUHP models included the identification number, area, length, <br />centroid length, slope, impervious percentage, retention storage losses, and infiltration <br />losses. The methods for estimating the subwatershed characteristics are described below <br />and a summary table of the characteristics is shown in Appendix H. <br /> <br />Subwatersheds were delineated on 1 :24,000 scale digitized USGS quadrangle maps. The <br />boundaries were determined based on the topography of the maps, existing roadways! <br />bridges, and existing culverts. The subwatershed areas, lengths, and centroid lengths were <br />estimated from the digitized 1 :24,000 scale USGS quadrangle maps. <br /> <br />3.6 <br /> <br />Delineation of Subwatersheds <br /> <br />3.6.1 <br /> <br />InfIltration Losses <br /> <br />The infIltration parameters (initial infIltration, fmal infIltration, and decay coefficient) <br />were computed from Table 2-2 of the Runoff chapter of the USDCM based on a weighted <br />average of hydrologic soil type (UDFCD, 1969). The weighted average of hydrologic soil <br />type for each subwatershed was computed based on superimposing the hydrologic soils <br />maps (Appendix A) onto the subwatershed maps. <br /> <br />3-3 <br /> <br />3.6.6 <br /> <br />Imperviousness <br /> <br />The imperviousness of each subwatershed was determined based on superimposing the <br />maps of existing and future development condition imperviousness (Appendices B and C) <br />onto the subwatershed maps. Based on the assumed impervious values for each land use <br />area, a weighted impervious percentage for each subwatershed was calculated. For exist- <br />ing conditions, imperviousness was typically 1 percent. For future conditions, the imper- <br />viousness ranged from 2 to 85 percent. <br /> <br />DENlOO15186.WP5 <br /> <br />3.6.2 <br /> <br />I <br />I <br /> <br />I <br />I <br /> <br />I <br />I <br />I) <br />I <br />I <br />II <br />I <br />