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DESCRIPTION OF THE MODEL 5 <br />Grand Dry Fork <br />Valle PID Government <br />y MCID Highline <br />Irrigation GVWUA Canal <br />District <br />Canal <br />Grand Sulphur <br />Gulch <br />Junction Colorado River Reservoir <br />Palisade Cameo <br />15-mile or <br />Study reach <br />(Palisade to <br />Grand Junction) OMID <br />Plateau Creek <br />EXPLANATION <br />GVWUA Grand Valley Water Users Association <br />MCID Mesa County Irrigation District <br />OMID Orchard Mesa Irrigation District <br />PID Palisade Irrigation District <br />Roan <br />Creek <br />De Beque <br />Upper Colorado <br />River Basin <br />Figure 2. Primary study reach hydrologic components considered in the stochastic mixing model. <br />from Sulphur Gulch Reservoir, inflow from Plateau Creek, and <br />return flow from the Orchard Mesa powerplant. The amount <br />and quality of streamflow upstream from De Beque is a result <br />of dissolved solids transported by runoff, ground-water inflow <br />(baseflow), and reservoir releases. Daily streamflow losses over <br />the study reach include diversions, reservoir pumping, and <br />evaporation. The Government Highline and Grand Valley <br />Canals divert Colorado River water downstream from the <br />De Beque streamflow gaging station, but upstream from the <br />Palisade streamflow gaging station, for use by the Grand Valley <br />Irrigation Company, Grand Valley Water Users Association, <br />Orchard Mesa Irrigation District, Palisade Irrigation District, <br />and Mesa County Irrigation District. The quality of water that <br />will be released to the Colorado River from the Sulphur Gulch <br />Reservoir would be the result of mixing seasonally pumped <br />Colorado River water with runoff to the reservoir and concen- <br />tration of salts by reservoir evaporation. <br />In conceptualizing the stochastic mixing model, the fol- <br />lowing assumptions were made. <br />No change in reservoir operations or transmountain <br />diversions occur upstream from the city of De Beque. It is <br />assumed that the operations associated with reservoirs <br />and transmountain diversions in the headwaters of the <br />Colorado River will continue with the same (or similar) <br />pump and release schedules. The assumption of similar <br />operations is valid so long as the mean streamflow deter- <br />mined by the stochastic model does not change in time <br />(stationarity). <br />2. streamflow record at Colorado River near Cameo <br />adequately describes flow at the proposed Sulphur Gulch <br />Reservoir pump and release point. This assumption is <br />realistic because there are no anthropogenic or perennial <br />tributary sources of water between the proposed pump <br />and release point and the streamflow-gaging station <br />located about 1 mi downstream. <br />Variability in streamflow and salinity measurements <br />adequately reflects periods of extreme wet and dry <br />climatic conditions. The period of record used (1974- <br />2001)reflects wet to dry conditions; however, future <br />climate conditions may be different and result in extreme <br />wet or dry (drought) conditions. As long as climatic <br />stationarity is in effect, the minimum and maximum <br />values of the probability distribution functions describing <br />daily flow may be adjusted to incorporate extreme <br />values; for example, the probability distribution function <br />describing minimum annual (calendar year) streamflow <br />(657,210 ft3/s) at the gage near Cameo could be changed <br />to the new minimum annual streamflow (604,026 ft3/s) <br />experienced during the 2002 drought. Because of the <br />comparatively minor difference in minimum annual <br />flows (about 8 percent) and similar probability of <br />occurrence (of less than about 1-percent chance) the <br />simulations were not repeated with the new distribution. <br />4. Instantaneous routing between pump and discharge <br />points. Instantaneous routing assumes that there is no <br />time delay between water sources or sinks in the study <br />