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<br />are great uncertainties concerning the magnitude of the pumping stresses. These stresses have a <br />direct impact on the resulting head distribution: the drawdown is linearly proportional to the <br />quantity of water pumped. <br /> <br />Historical (1880 - 1995) pumping locations and magnitudes were obtained from those used in <br />the SB-74 model. These pumping stresses were applied to our historical model runs used in <br />model calibration. Future pumping estimates were obtained from two sources. For the South <br />Metro region, current and future (2000 and beyond) pumping estimates were derived from <br />current demand information and projected growth provided by each of the then twelve (l2) <br />participating water providers (parker Water and Sanitation has since withdrawn from the study). <br />Given the uncertainty as to where future wells would be installed, the projected pumping for each <br />of the water providers was uniformly distributed across all the gridblocks that lie within each of <br />their respective service areas. For areas outside the South Metro water provider service <br />boundaries, the current and future pumping conditions (locations and magnitudes) associated <br />with the BASE scenario for the SB-74 model were applied with minor adjustments associated <br />with new demand patterns in the South Metro area. For all future development scenarios <br />considered (see Section 3.2.3), Figure 3.4 shows the future pumping demands specified for the <br />entire basin from the historical period through 2050. Table 3.1 presents the future pumping <br />estimates for the three ground water scenarios modeled for key South Metro water providers. <br />The pumping volumes presented in this table have been refmed in the study process and do not <br />match exactly the volumes modeled. However, these minor revisions which are less than ot 5% <br />have little effect on the study results. <br /> <br />3.2.2 Model Calibration - Model calibration involves adjusting one or more of the model <br />parameters described in Section 3.2.1 to minimize the differences between model predictions and <br />historical observations of aquifer response. "Aquifer response" refers to some history of how the <br />ground water system responds to stress, and these historical data are referred to as calibration <br />targets. <br /> <br />After providing a broad discussion of model calibration targets, error measures, and general <br />considerations related to steady-state and transient conditions, a chronological summl!rY of the <br />calibration process is provided. <br /> <br />3.2.2.1 Calibration Targets - In our calibration process, there were five data sets used as <br />calibration targets: <br /> <br />. Pre-development heads, reflecting steady-state conditions in the bedrock aquifers prior to <br />installation of wells in the basin, <br />. Historical heads in 1991, <br />. Historical drawdown rates from pre-development through 1991, <br />. Historical heads in 2000, and <br />· Drawdown rates between 1991 and 2000. <br /> <br />It is generally recognized that calibration of a steady-state model is more likely to converge on a <br />unique solution if flow targets are used in addition to head targets (see for example, Reference <br />3.1). Unfortunately, there is essentially no available high quality data that characterizes <br />interactions between the bedrock aquifers and streams and/or the alluvial that could be used for <br />flow targets during calibration of the steady-state model. <br /> <br />Page 3-10 <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 />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />. <br />