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<br />3.4.3 Hyetographs <br /> <br /> Table 3-3 <br />Composite Future Imperviousness Values <br />Watershed Composite Future Imperviousness <br /> (percent) <br />Oak Gulch 33 <br />Unnamed Tributary 42 <br />Lemon Gulch 24 <br /> <br />A total of 8 hyetographs were developed for the four recurrence intervals (10" 50" I 00" and <br />SOO,year), and two storm types (2,hour with no area adjustment and 2,hour with an area <br />adjustment). The derivation of the hyetographs is described below. <br /> <br />The 2,hour duration hyetographs with no area adjustments were developed by inputting the <br />one,hour depths and letting the CUHP program automatically develop the 2-hour <br />distribution. <br /> <br />The 2-hour duration hyetographs with the area adjustment were taken directly from the <br />Douglas County Drainage Criteria Manual (1986). The hyetographs used were adjusted <br />according to the 5 to 10 square mile area adjustments shown in Table 4-2 of the Rainfall <br />chapter of the USDCM (UDFCD, 1969). <br /> <br />3.5.3 Slope <br /> <br />Hyetographs for the SOO,year event were based on the same temporal distribution as the 100, <br />year event <br /> <br />The slopes for each sub watershed were estimated according to the weighted slope method <br />documented in the USDCM. The length of each subwatershed 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 and <br />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 1.2 percent to 5.6 percent in the study area. <br /> <br />3.5 CUHP Modeling <br /> <br />3.5.4 Time of Concentration <br /> <br />CUHP models were developed for the 8 storms described in the previous section. The <br />subwatershed characteristics required for the CUHP models included the identification <br />number, area, length, centroid length, slope, impervious percentage, retention storage losses, <br />and infiltration losses. The methods for estimating the subwatershed characteristics are <br />described below and a summary table of the characteristics is shown in Appendix E. <br /> <br />In accordance with the USDCM, the modified CUHP procedure was used for subwatersheds <br />less than 90 acres (UDFCD, 1969). The modified CUHP procedure produces peak flows <br />similar to the rational method and requires a time of concentration value for each <br />sub watershed modeled. <br /> <br />3.5.1 Delineation of Subwatersheds <br /> <br />For rural land use conditions (future imperviousness less than 20%), Equations 3,2 and 3-3 <br />from the Runoff chapter of the USDCM were used to determine the time of concentration <br />(UDFCD, 1969). The velocity parameter used to determine the travel time variable in <br />Equation 3-2 was estimated from Figure 3,1 of the Runoff chapter of the USDCM using the <br />curve for short grass pasture and lawns (UDFCD, 1969). Time of concentration values <br />generally ranged from 36 to 124 minutes. <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 <br />roadways/bridges, and existing culverts. The subwatershed areas, lengths, and centroid <br />lengths were estimated from the digitized 1 :24,000 scale USGS quadrangle maps. <br /> <br />3.5.2 Imperviousness <br /> <br />Under urban conditions (future imperviousness greater than 20%), Equation 3,4 from the <br />Runoff chapter of the USDCM was used to determine the time of concentration, since it <br />yielded shorter concentration times than Equation 3-2 and 3,3 and Figure 3-1 from the <br />USDCM (UDFCD, 1969), For urban development conditions, the time of concentration <br />values for individual subwatersheds ranged from 19 to 40 minutes, <br /> <br />The imperviousness of each subwatershed was determined by superimposing the map of <br />future development condition imperviousness onto the subwatershed maps. Based on the <br />assumed imperviousness values for each land use area, a weighted impervious percentage for <br />each sub watershed was calculated. The composite future imperviousness values for the Oak <br />Gulch watershed, Unnamed Tributary watershed, and the Lemon Gulch watershed are shown <br />in Table 3,3. <br /> <br />4 <br /> <br />Oak Gulch and Lemon Gulch FHAD.DOC <br />