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<br />Items I through 5 relate to setting up the model, and item 6 is necessary for model calibration. <br />Each of these items is described below. <br /> <br />3.2.1 Model Setup - In this section, the approach to setup of the model is described in terms of <br />model geometry, parameter distributions, boundary conditions, aquifer stress, and observation <br />data used as calibration targets. Since this model was developed as a modification to the State <br />Engineer Office (SEO) SB-74 Denver Basin MODFLOW model, particular attention will be <br />focused on the modifications to the original SB-74 model. To provide a robust tool for assessing <br />impacts of ground water development in the South Metro region, this ground water model needs <br />to extend the capabilities of the existing SB-74 model in at least two important ways: <br /> <br />. It should incorporate the best available up-to-date data and information, and <br />. It should be capable of projecting regional drawdowns and water elevations to support the <br />local (well and well-field) scale analyses for estimating the costs of adding supplemental and <br />alternate points of diversion as needed to maintain production through the aquifers' life. <br /> <br />3.2.1.1 Model Domain and Geometry - The model domain in the plan view encompasses the <br />entire areal coverage of each of the aquifer units within the Denver Basin (Figure 3.1). In the <br />plan view, the model grid is oriented parallel to the state of Colorado's township-range cadastral <br />system, with 1 mile by I mile grid cells. Each grid cell can be mapped to a section. <br /> <br />The model domain was discretized vertically to simulate each of the important water producing <br />units, or aquifers, which supply water for various uses in the basin (Figure 3.2). Those aquifers <br />are, from the top of the stratigraphic column to the bottom: the Dawson, the Denver, the <br />Arapahoe, and the Laramie-Fox Hills. Each aquifer was simulated as a separate layer except the <br />Dawson and the Arapahoe, which were further discretized into upper and lower units. The top <br />and bottom elevations of each unit were derived from the top and bottom elevations of the units <br />as inferred from well logs. Given that there was not a well in every grid cell, aquifer top and <br />bottom elevation maps were developed based on interpolation of the measured values. Our <br />model aquifer top and bottom elevation maps deviate slightly from the SB-74 model in that we <br />incorporated all data from the South Metro area available through 2001, whereas the SB-74 <br />model incorporated no data collected after 1985. To illustrate typical differences between the <br />SB-74 and the updated South Metro aquifer top and bottom elevations, Figure 3.3 shows the <br />aquifer top configuration for the Upper Arapahoe aquifer for both models. More details on this, <br />as well as on the hydrological parameter distributions discussed in the next section, can be found <br />in Appendix 3B. <br /> <br />3.2.1.2 Hydrological Parameter Distributions - To simulate aquifer behavior, hydrologic <br />parameters (e.g., transmissivity, storage coefficient, leakance, ...) must be specified for each of <br />the model units. The starting point for each parameter was the distribution specified in the SB- <br />74 model, and these values were updated based on data collected since 1985. In the calibration <br />process, some of these values were adjusted as required to improve model fit to observations. <br />Below each of the hydrologic parameters is discussed. <br /> <br />Page 3-4 <br /> <br />4 <br />t <br />t <br />t <br />t <br />t <br />t <br />t <br />t <br />. <br />. <br />t <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />I <br />