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<br />For Coal Creek SLA used the Environmental Protection Agency SWMM (Reference 12) in <br />determining discharges for the original report. SLA assumed that all irrigation ditches and <br />canals would already be full from upstream runoff and would not have the capacity to <br />intercept additional runoff. The Natural Resources Conservation Service (NRCS) found <br />that one exception to this assumption is Windsor Ditch, which crosses the basin upstream <br />of the Town of Wellington. The NRCS determined that 200 cfs would be diverted from <br />Coal Creek by Windsor Ditch. <br /> <br />Discharges for Dry Creek were computed using the SWMM (Reference 12). The drainage <br />basin was divided into 190 subbasins that drained into 139 channel sections. Basins were <br />selected so that hydrographs would be available at critical design points, particularly at <br />irrigation canal crossings and at onstream reservoirs (Reference 1). Precipitation <br />information was obtained from the NOAA Atlas (Reference 18). The 0.2-percent annual <br />chance rainfall, not available from the atlas, was extrapolated assuming a Gumbel <br />probability distribution (Reference 1). <br /> <br />Discharges for Fish Creek and the Fall River were computed based upon records of stream <br />gages located on the two streams. The Fish Creek gage has 30 years of record, and the Fall <br />River gage has 9 years of record. These records were analyzed using a log-Pearson Type <br />III distribution as recommended in U.S. Water Resources Council Bulletin 17 (Reference <br />11). These discharges were weighted with those obtained using regression equations from <br />the Colorado Water Conservation Board's Technical Manual No.1 (Reference 10). <br /> <br />The hydrologic study for Spring Creek completed by Anderson Consulting Engineers, Inc., <br />was conducted in 2003 (Reference 72). MODSWMM was used to determine peak <br />discharges for the 10- and I-percent annual chance floods. The study was updated to <br />reflect current drainage patterns, revise detention pond routing parameters, and improve <br />modeling techniques, if applicable. <br /> <br />Peak discharge-drainage area relationships for streams studied in detail are shown in Table <br />1. <br /> <br />3.2 Hydraulic Analyses <br /> <br />Analyses of the hydraulic characteristics of flooding from the sources studied were carried <br />out to provide estimates of the elevations of floods of the selected recurrence intervals. <br />Users should be aware that flood elevations shown on the Flood Insurance Rate Map <br />(FIRM) represent rounded whole-foot elevations and may not exactly reflect the elevations <br />shown on the Flood Profiles or in the Floodway Data table in the FIS report. Flood <br />elevations shown on the FIRM are primarily intended for flood insurance rating purposes. <br />For construction and/or floodplain management purposes, users are cautioned to use the <br />flood elevation data presented in this PIS report in conjunction with the data shown on the <br />FIRM. <br /> <br />Cross sections for the Big Thompson River and its tributaries were taken from topographic <br />maps at a scale of 1 :2,400, with a contour interval of 2 feet (References 19, 20, and 21) and <br />field surveys. These tributaries include the North Fork Big Thompson River, Big <br />Thompson River Tributaries 1, 2, 3, and 4, Long Gulch, Rabbit Gulch, Quillan Gulch, <br /> <br />21 <br />