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<br />Development of Ground-Water Models <br /> <br />'. <br /> <br />To predict the effects of artificial recharge on the aquifer system, a <br />ground-water model of each of the two alluvial valley aquifers was construct- <br />ed. These models consist of a unique set of input parameters describing the <br />j~spective aquifer systems and a digital computer program which approximates <br />the solution to the ground-water flow equation. The program used is a modi- <br />fication of the standard U.S. Geological Survey two-dimensional, finite-dif- <br />ference model using the iterative, alternating direction, impl icit solution <br />techn i que (Trescot t and others, 1976). <br /> <br />,: <br /> <br />To model the aquifers, maps of the areas of interest were fir~t subdi- <br />'vided into a rectangular network of nodes'. Beaver Creek valley was subdivided <br />into 37 rows by 27 columns with the largest node representing an area of' <br />0.5 mi2 and the smallest node an area of 0.08 mi2. Badger Creek valley was <br />subdivided into 33 rows by 24 columns with the largest node representing an <br />area of 0.3 mi2 and the smallest node an area of 0.04 mi2. The input param-' <br />eters to these models included the hydraulic head, hydraul ic conductivity" <br />specific yield of the aquifer, altitude of bedrock surface, and altitude of, <br />land surface at each node. In addition, al I the stresses to the aquifer were, <br />specified. These stresses included boundary fluxes, pumping, recharge, and' <br />discharge to the stream. <br /> <br />All of these stresses are input to the model except discharge to the' <br />stream, which is computed by the model. Discharge to a stream was simulated' <br />by defining a node to be constant head if the water level at a stream node <br />rose above the bottom of the streambed (as defined by the altitude of land <br />surface). The discharge to all constant head stream nodes was accumulated and, <br />accounted for as the surface streamflow leaving the modeled area. If the <br />flow to a stream node reversed directions as water l~vels in the aquifer de-' <br />clined, thus making the stream a source of water, the designation of a con-, <br />stant head node was discontinued and that node would no longer be considered <br />a part of the flowing stream. <br /> <br />Data Availabi lity <br /> <br />. ! <br />i <br />i. <br /> <br />The most abundant data available for ground-water modeling are water, <br />levels. In Beaver Creek valley, south of Brush, water-level data for at least <br />15 years were available for 24 wells (fig. 14). The hydrographs of these, <br />wells (fig. 15) illustrate some interesting trends. Little change in water, <br />'levels is noted in the southern end of the valley (higher alti tudes) since <br />about 1955-60. The date of the initial water-level declines cannot be deter-: <br />mined from the avai lable data for that part of the valley. In the northern i <br />end of the valley (lower altitudes) the date when water levels began declin-: <br />jng moved steadily forward in time. Thirteen wells within the modeled area of i <br />Badger Creek valley have at least 10 years of data (fig. 16). Unfortunately, I <br />most of these wells are considered part of the South Platte River alluvial: <br />~quifer and are in areas that are irrigated by surface-water supplies. The I <br /> <br />I i <br /> <br />i <br />, <br />I' <br />j <br />'j <br /> <br />33 <br />