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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 />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 />3.6.4 Time of Concentration <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 />For future development conditions, Equation 3-4 from the Runoff chapter of the USDCM <br />was used to determine the time.9f concentration, since it yielded shorter concentration <br />times than Equation 3-2 and 3-3 and Figure 3-1 (UDFCD, 1969). Time of concentration <br />values generally ranged from 30 to 120 minutes for existing development conditions. For <br />future development conditions, the time of concentration values ranged from 17 to <br />48 minutes. <br /> <br />3.6.5 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 />3.6.6 Inrdtration Losses <br /> <br />The infiltration parameters (initial infiltration, final infiltration, and decay coefficient) <br />were computed from Table 2-2 of the Runoff chapter of the USDCM based on a <br />weighted average of hydrologic soil type (UDFCD, 1969). The weighted average of <br />hydrologic soil type for each subwatershed was computed based on superimposing the <br />hydrologic soils maps (Appendix B) onto the subwatershed maps. <br /> <br />DENlOOISI86.WPS <br /> <br />3-6 <br />