<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,
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