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<br />SECTION 3.0 - HYDROLOGIC ANALYSIS <br /> <br />3.1 Background <br /> <br />This study and report were conceived in order to convert the hydrologic model for the Ralston Creek <br />watershed from MITCA T to CUHP-SWMM and to account for reductions to the 100-year floodplain as a <br />result of the construction of and/or enlargement of various reservoirs, Because results from previous studies <br />were used in development of the published Flood Insurance Study (PIS) and associated floodplain mapping, <br />it was necessary to perform a calibration procedure to insure that results from this study compared well with <br />those previously published, <br /> <br />The Arvada/Blunn Reservoir was not included in previous hydrologic models, Leyden Lake was omitted <br />from the Phase A report, but was considered as a separate model for the Phase B report, However, Leyden <br />Lake was improved in 2001, and no longer operates as represented in the Phase B modeling, For these <br />reasons, in order to determine consistency between the models, it was first necessary to model the Ralston <br />Creek basin without considering effects from Arvada/Blunn Reservoir and Leyden Lake, Ralston <br />Reservoir, which was in place before the Phase A report was published and has not been modified since. <br />remained in the model. <br /> <br />Once the new CUHP-SWMM model was sufficiently calibrated to previously published results, effects of <br />the new reservoirs were added to the model in order to determine an updated hydrologic response for the <br />watershed, These results will be used to determine the extent of the 100- year floodplain, as well as the <br />magnitude of flooding for other events, for the future developed condition, <br /> <br />3.2 Methodology <br /> <br />Although this study is essentially an update of previous studies, it utilized a new modeling application, In <br />addition, mapping and computer-generated data files were unavailable from the previous studies, For this <br />reason, other than the calibration procedure to insure consistency, this study essentially resulted in the <br />development of a completely new model. <br /> <br />Because there is no comprehensive, single-datum mapping for the entire Ralston Creek watershed, USGS <br />7,5' quadrangle maps were used, Arvada, Golden, Ralston Buttes and Black Hawk were the maps used for <br />this study, Available electronically, these maps could be combined with computer aided drafting to develop <br />accurate watershed runoff characteristics, <br /> <br />Design rainfall was then prepared for various points in the watershed, Design events considered include the <br />10-,50-, 100-, and 500-year events, Rainfall patterns for a number of various areal corrections were <br />developed and used in the analysis, To more accurately represent rainfall, the entire basin was developed <br />into upper, central, and lower regions, with separate rainfall patterns developed for each, <br /> <br />Using this information, CUHP models were prepared and run for the various design frequencies and <br />correction scenarios, Output hydrographs from these models were then run through the stream network <br />using UDSWMM in order to determine peak flow rates at critical design points, <br /> <br />3.3 Subwatershed Delineation <br /> <br />The first step in the procedure was to delineate the entire Ralston Creek basin and separate the Ralston, <br />Leyden, and Van Bibber subbasins, These basins were then delineated into subwatersheds, For areas <br />upstream of Arvada/Blunn Reservoir and Leyden Lake, subwatersheds were delineated with a maximum <br />basin area of five square miles, For areas below these reservoirs, a detailed delineation was performed with <br />maximum basin areas of 130 acres, Because the Van Bibber basin was only included in this study to <br />determine its effects on the Ralston Creek basin (an analysis of the Van Bibber floodplain was not included <br />in this study), it was not subject to the same areal criteria as the Ralston and Leyden basins, The Van <br />Bibber Creek basin was delineated based on previous studies where the sub watershed maximum area limits <br />did not apply, <br /> <br />Once delineated, a number of geographic variables for each subwatershed were calculated for input into the <br />CUHP model. These variables include the following: <br /> <br />. Contributing Drainage Area (sq, mi,) <br />. Catchment Length (mi,) <br />. Centroid Distance (mi,) <br />. Catchment Slope (ftlft) <br /> <br />These variables were determined graphically using computer aided drafting, and this electronic map is <br />included on the attached CD-ROM, The watershed characteristics are shown in Tables 1,2, and 3 of <br />Appendix A for the Ralston, Leyden, and Van Bibber basins, respectively, <br /> <br />The subwatershed delineations are shown in Figures 1 through 5 of Appendix A, Figures 6 through 9 of <br />Appendix A portray a routing schematic for the basin, <br /> <br />3.4 Watershed Imperviousness <br /> <br />A critical variable for development of subwatershed hydrographs is the percentage of impervious surfaces in <br />each subbasin, Impervious surfaces increase the hydrologic response of a subbasin, and the hydro graphs <br />generated for each subbasin are particularly sensitive to this value, <br /> <br />It was understood that any changes to planned development relative to the Master Plan were local rather <br />than regional in nature, For this reason, aggregate impervious percentages developed in previous studies <br />(which utilized much larger subbasin areas) were kept the same, However, a zoning map provide by the <br />City of Arvada was utilized to determine actual impervious percentages for each individual subwatershed, <br />For each large subwatershed in the previous study that was subdivided into smaller watersheds for the <br />present study, a weighted average was computed to maintain consistency over larger regions, <br /> <br />The values determined for watershed imperviousness are included in Tables 1,2, and 3 of Appendix B, <br /> <br />4 <br />