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Section 7 <br />Availability of Existing Water Supplies <br />estimating available supply in these basins. For those <br />basins without developed DSS datasets - Arkansas, <br />South Platte, and North Platte - information for physically <br />and legally available flows were gathered from existing <br />sources and studies. For example, USGS flow gages <br />were used to help quantify physically available flows for <br />all three of these basins. The Republican River basin <br />was not studied in SWSI because of ongoing interstate <br />litigation concerns. Additionally, legally available flows <br />were quantified in the SECWCD Hydrologic Analysis <br />Study (2000) for the Arkansas Basin, and in the Denver <br />Water Chatfield Reservoir Reallocation PACSM modeling <br />effort, the CWCB Lower South Platte Water Management <br />and Storage Sites Reconnaissance Study, and the <br />NCWCD NISP for the South Platte Basin. <br />Table 7-1 Summary of SWSI Sources of Data: Supply <br />Availability <br /> . . ~, <br />Arkansas SECWCD Hydrologic Analysis (2000), <br />USGS flow gages <br />Colorado DSS/StateMod <br />Dolores/San Juan/ <br />San Mi uel DSS/StateMod <br />Gunnison DSS/StateMod <br />North Platte USGS flow a es <br />Rio Grande DSS/StateMod <br />South Platte PACSM model (Denver Water), NISP <br />study (NCWCD), Lower S. Platte Water <br />Management and Storage Sites <br />Reconnaissance Study (CWCB) <br />Yampa/VVhite/Green DSS/StateMod <br />* Republican not studied <br />For each basin where DSS StateMod runs were <br />available, modeled flows were summarized at 4 to 10 key <br />locations. Locations were chosen to provide a good <br />spatial coverage across a given basin. These locations <br />also generally correspond to downstream ends of <br />delineated subbasins (counties and water districts). The <br />simulated flows at these locations are therefore <br />representative of total subbasin available flows and <br />provide useful information for analyzing options at a <br />subbasin level (Section 10). <br />7.1.3 Firm Yield Analysis <br />The concept of "firm yield" is a common term used in <br />water supply planning. The firm yield, as defined below, <br />is analyzed for several locations to illustrate the storage <br />to yield ratios under certain planning criteria. For these <br />analyses, firm yield is defined as the maximum annual <br />~~ <br />supply that can be reliably provided every year for the <br />period of record with no monthly shortages. <br />This firm yield definition is based on no monthly <br />shortages for the period of record. The appropriate <br />period of record to be used for firm yield analysis as well <br />as the willingness to accept some shortages can <br />significantly affect the firm yield analysis. Individual water <br />planning agencies may have different criteria for the <br />critical period of record that should be used. In addition, <br />the planning agencies may determine that it is more cost- <br />effective to manage infrequent shortages with demand <br />modifications than to design the water system to deliver <br />full supplies with no shortages over the critical period or <br />period of record. <br />As part of the supply availability summaries presented in <br />this section, curves of firm yield versus total storage <br />("yield curves") are provided for one location in most <br />basins. These curves were generated using Water <br />Supply Investigation Tool (WatSIT), a screening-level <br />reservoir and water supply model developed for this <br />project. The model simulates the filling of a reservoir by a <br />time series of monthly available river flows and the <br />simultaneous emptying of the reservoir according to a <br />user-defined monthly demand pattern. For a given <br />reservoir size, firm yield is therefore calculated as the <br />maximum total annual demand that can be met without <br />shortages over the full period of record of river flows. A <br />detailed description of WatSIT is provided in Appendix F. <br />Firm yield calculations can be inaccurate for short <br />periods of record, because assumed starting reservoir <br />conditions affect calculated firm yields (Lester and Couch <br />2000). Starting reservoir conditions affect firm yields <br />when the reservoir simulation fails to include at least one <br />period of partial depletion followed by full recovery (to full <br />capacity) before entering the critical hydrologic period <br />(Zarriello 2002). Firm yields presented in this section <br />were not affected by assumed starting conditions for any <br />of the basins except the Rio Grande and the South Platte <br />Basins (which had shorter periods of record than the <br />others). As described below, for the Rio Grande Basin <br />analysis, starting reservoir conditions were set equal to <br />the maximum wet-weather predicted storage volume. For <br />the South Platte Basin, the analysis was terminated at <br />the point at which yields showed a dependence on <br />starting conditions (at high total storage values). <br />~~ <br />Sfvtewide Woter Supoly Initiofive <br />7-Z S:\REPORT\WORD PROCESSING\REPORT\S7 11-10.04.DOC <br />