Laserfiche WebLink
Total Basin 87,449 79,649 9 % 86,215 1 % <br />Difference = (StateCU Results- StateMod Results)/StateCU Results <br />Wet-Year Crop Consumptive Use Comparison <br />Table 5 shows the total basin consumptive use estimates and the consumptive use estimates for <br />the explicit and aggregate structures for the representative wet year 1984. Focusing on explicit <br />structures, the current StateMod estimates consumptive use of explicit structures in wet years <br />that is much closer to the StateCU results than the CRDSS StateMod estimates. Although not as <br />intuitive as the dry year analysis, the wet year analysis recognizes that when more water is <br />available, efficiencies are generally lower and more of the diverted water returns to the river. <br />Therefore, there is more water for subsequent diversions and basin-wide consumptive use is <br />higher. <br />Table 5 <br />Crop Consumptive Use Comparison Representative Wet Year - 1984 <br /> StateCU Previous CRDSS StateMod Enhanced StateMod <br />Comparison Results Results % Difference Results % Difference <br />Explicit Structures 41,862 40,381 4 % 41,139 1 <br />A re ate Structures 20,249 23,967 -18 % 23,966 -18 <br />Total Basin 62,111 64,348 -4 % 65,335 -5 <br />Difference = (StateCU Results- StateMod Results)/StateCU Results <br />Conclusions <br />The following summarizes the main conclusions discussed during the Results Section: <br />• The Previous CRDSS analysis and the Enhanced analysis, using the variable efficiency <br />and soil moisture accounting options, result in streamgage, diversion, and reservoir <br />calibration that is considered good. <br />• Both simulations result in predicted streamflows, diversions, and reservoir end-of--month <br />contents that match gaged data well on both an annual and monthly basis. <br />• The Previous CRDSS analysis predicts streamflows during the representative dry-year <br />(1977) that average 2 percent higher than gaged streamflows, while the Enhanced <br />analysis predicts streamflows that average 6 percent lower than measured. <br />• The Previous CRDSS analysis predicts diversions during the representative dry-year <br />(1977) that average 3 percent lower than measured diversions, while the Enhanced <br />analysis predicts diversions that average 11 percent lower than measured. Most of the <br />shortages in the current analysis occur in Water District 54 on Slater Creek and Little <br />Snake River, where the four aggregate diversion structures are shorted by an average of <br />30 percent. These aggregate structures account for more than 50 percent of the demand <br />in this water district. Because the aggregate diversions are "estimated" based on average <br />efficiencies, the Previous CRDSS analysis, which used average efficiencies during <br />simulation, was more likely to meet those demands. <br />VariableEff Taskl-5 15 of 17 November 5, 2001 <br />