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<br />2~6() <br /> <br />Discussions' with the District revealed that no attempt has been made to deter- <br />mine the irrigation requirement for any year. In addition, there is no evidence <br />that the District has limited the headgate diversion based on an irrigation <br />requirement. A comparison of 1985 headgate diversions (only year with suitable <br />irrigated acreage data) with the irrigation requirement computed using methodo- <br />logy of the 1961 Study shows that the 1985iheadgate diversion exceeded the require- <br />ment by 14,210 acre-feet.1/ <br /> <br />To gain insight into the impact of excess diversion, the previously described <br />Baseline study (lH and 1R) and variation studies 5H and 5R were modified to <br />reflect assumed increases in headgate diversion. This included established cri- <br />teria for calculating return flow from diversions in excess of ideal requirement <br />as described in the 1961 Study. Sever;al runs were made, each reflecting an <br />incrementa 1 increase in headgate di vers i on (above idea 1) . Excess di vers i on <br />increments ranged from .1 to 1 foot of addit i ona 1 water per acre. When an <br />increment resulted in a negative effect on John Martin Reservoir inflow, no <br />analysis was done of the higher increments. <br /> <br />This range of excess diversions represents an increase in headgate diversion <br />requirement of from 1,972 to 19,717 acre-feet per year(example - 19,717 acres X <br />0.1 foot per acre). In order to simulate a more realistic water management pro- <br />cedure, excess diversions were allowed, to occur only in those years of above <br />normal water supply. <br /> <br />The modified Basel ine study shows the direct effects of the excess diversions. <br />The modified 5H and 5R show the cumulative effects of excess diversions, <br />transfer of water out of the Model decree and wi nter storage under joi nt use <br />decree. <br /> <br />A few of the key results of this analysis are displayed below: <br /> <br />Effect of Excess Diversion on Baseline Study <br /> <br />Item <br />(Units 1000 Acft.) <br />Total Bypass/Spill <br />Total Return Flow <br />Total Irrigation Shortage <br />Net Effect on J .M. inflow <br />compared to historic Model <br />reservoir operation (lH) <br /> <br />Net Effect on J.M. inflow <br />compared to rehabilitated <br />Model Operation (lR) <br /> <br />1H/1R <br />Baseline <br /> <br />Foot/Acre of Excess Diversion <br />0.2 0.3' 0.4 0.5 1.0 <br /> <br />0.1 <br />13.3 <br />17.7 <br />11.8 <br /> <br />13.0 <br />18.0 <br />12.1 <br /> <br />12.6 <br />18.2 <br />12.3 <br /> <br />12.4 <br />18.6 <br />12.6 <br /> <br />12.2 <br />18.9 <br />12.9 <br /> <br />11.0 <br />20.3 <br />14.0 <br /> <br />13.6 <br />17.3 <br />11.5 <br /> <br />0.5 <br /> <br />0.3 <br /> <br />0.2 <br /> <br />-0.7 <br /> <br />0.8 <br /> <br />0.7 <br /> <br />1.0 <br /> <br />3.3 <br /> <br />3.2 <br /> <br />3.0 <br /> <br />2.8 <br /> <br />2.7 <br /> <br />2.6 <br /> <br />4/ It must be noted that 1985 is not within the study period and <br />- the first year that Model lands were back to full irrigation. <br />the example of effect of excess diversions, .it is appropriate. <br /> <br />that 1985 is <br />However, for <br /> <br />44 <br /> <br />1.7 <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />