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<br />-,. <br /> <br />" <br /> <br />,---'-'-'----- ---,---------- -- <br />, The method chosen to calibrate the model was to run the model from 1920 <br />'to 1980 and to try to match the water-table contours in 1947 and 1978 and fit, <br />water-level hydrographs with at least 20 years of record. The initial water, <br />table for the model run was assumed to be the preirrigation steady-state con-, <br />dition--before any pumping occurred. This water-table configuration was com-: <br />puted by running the model with the computed boundary fluxes and no pumping" <br />and solving for the position and flow of Beaver Creek. The simulation was, <br />:run to steady-state so that the constant flux out of the north end of the, <br />modeled area plus the streamflow in Beaver Creek equaled the boundary-flux: <br />, inflo",. <br /> <br />The model was run for the GO-year period starting at this initial, no- <br />pumping condition. Estimating the distribution of pumping both spatially and <br />temporally \."as a part of the calibration process. The model allo\'led pumping <br />to occur only in those nodes where wells occur, as del ineated from the well- <br />permit list. In the first calibration attempt, the total pumping was evenly <br />'distributed to each of these nodes. However, it is known that historic irri- <br />gation was more concentrated at the southern end of the valley and increased <br />,in the northern end at a later time. Thus, a function was built into the <br />model which weighted the distribution of the total pumping to the southern <br />end prior to 1953 and toward the northern end after that date. Also programed <br />into the model was the feature to decrease pumping at a node proportionately <br />as the saturated thickness decreased from its initial value. 'Finally, a <br />driving function for total annual pumpage from all wells in the entire valley <br />was input to the model. This driving function was generated to correspond to <br />the curve in figure 23 until 1955. An abrupt change in pumping was attributed <br />to excessive drawdowns caused in part by the extreme drought conditions from <br />1953 to 1956. Since that time irrigation and pumping reportedly have de- <br />cl ined steadily (Robert Samples, Water Commissioner, oral commun., 1978). The <br />pumping rates computed by the model as a result of these different functions <br />are shown on figure 24. The driving function assumed average precipitation <br />every year to smooth out the vagaries in pumping estimates due to fluctuating <br />precipitation (fig. 22). <br /> <br />Other than the adjustments to the pumping functions and values, the only' <br />'significant change made to the input data during calibration was the distri-, <br />bution of hydraulic conductivity. The 1947 water-table simulation closely <br />matched actual conditions, but the 1978 water-table simulation was too high <br />'in the western part of the model where the sand dunes occur. Because there: <br />was no evidence to suggest an unidentified \1ithdrawal in that area, and the: <br />area in question was too far from the boundary for modifications in the <br />:boundary flux to help, the only useful modification to the data was to in-; <br />:crease the hydraulic-conductivity values in that area to about 400 ft/d. <br />I <br /> <br />. I <br /> <br />, <br />I <br />I -' <br /> <br />47 <br />