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<br />Reservoir Operating Studies <br />An important limitation imposed by the use of monthly hydrology is the inability to <br />examine effects on peak flows and on flows during periods of rapid change. For example, an <br />average July flow of 900 cfs might in reality be a flow of 2,000 cfs at the beginning of the <br />month and 200 cfs at the end of the month. <br />Water Demands <br />Existing basin water uses are generally represented in the model through the use of <br />gaged flow hydrology rather than virgin flow hydrology. Implicit in this method is the <br />assumption that those historical water use patterns imbedded in the gaged hydrology will <br />continue in the future as they have in the past, unaffected by any additional water development <br />or management simulated explicitly in the basin model. <br />Exceptions to this generality include major municipal and industrial uses relying on water <br />' rights junior to the Juniper Project rights and longstanding agricultural uses that, by virtue of <br /> late adjudication, have water right priorities that are junior to the 1954 Juniper Project rights. <br /> Depletions associated with these existing junior uses were explicitly represented in the model <br /> rather than implicitly represented by the gaged (depleted) hydrology in order to the evaluate the <br /> effect of the Juniper Project water rights on other basin demands and to estimate the project's <br /> contemplated draft. In the predecessor study, approximately 13,000 of of agricultural <br /> depletions with junior water rights were thus explicitly represented; these depletions were <br /> derived from data provided by Division 6 but did not include diversions with estimated annual <br /> depletions less than 5 of or reservoirs with estimated depletions of less than 700 af. In the <br /> present study the model was modified to include an additional 4,000 of of junior depletion <br /> attributable to these smaller agricultural uses. The resulting total of roughly 17,000 of includes <br /> all junior agricultural depletions estimated by Division 6. <br /> Three basic demand data sets were defined for use in the basin model, representing three <br /> levels of water demands. These demand levels were defined during the predecessor study as <br /> representative of current (1989) potential demands and demands associated with population and <br /> industrial growth projected for the years 2015 and 2040. <br /> Current Potential Demands <br /> The current potential demand level was defined by making certain adjustments to <br /> recently observed water diversions and depletions. These adjustments were of two general <br /> types: 1) adjustments to "level out" historical demands over the entire 53-year study period, <br /> and 2) adjustments to account for the fact that observed historical water deliveries do not <br /> completely describe water demands. The former adjustment is made in recognition of the fact <br />' that water demands in certain sectors, notably municipal and industrial, have grown and <br /> changed significantly over the 1930-82 study period. The second adjustment is made in <br /> recognition of the fact that, even under current development conditions, there is potential for <br /> increased water use due to climatic factors, greater utilization of generating capacity at power <br /> plants, repair of washed out headgates, etc. Accordingly, the current potential demand level <br /> reflects the maximum estimated water requirement associated with current basin development <br />imposed uniformly upon the hydrology of the 1930-82 study period. Table 2-1 below <br /> summarizes the current (1989) observed and potential water demands in various sectors of the <br />' basin economy. <br /> 2-3