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Mining activities are presently ongoing ai the Site directly between the Parker Property and Dersham Property and at the <br />Brighton Pit directly east of the Site as seen in Figure 7. An active settling pond is located as shown and a perimeter <br />bentonite-soil slurry wall has been constructed around the Brighton Pit. The aggregate has been removed from the <br />Brighton Pit and activities in the middle of the Site consist of dewatering and mining. To the south of the Site, Aggregate <br />Industries' Tucson Pit has installed a perimeter slurry wall and this site is now moving towards reclamation as observed <br />during a site visit. Another gravel mine to the west of Tucson Road just south of WCR 2 is actively dewatering (no slurry <br />wall has been constructed) and through this dewatering, mitigation of a Sakata Farms irrigation well is occurring. The <br />mitigation consists of the dewatering water being conveyed to the north side of WCR 2 through a pipe to a small 2-3 foot <br />deep holding pond where water percolates back to the ground to create a mounded groundwater table. These Site <br />conditions and surrounding conditions were all observed during a Site visit and through discussions with the Brighton Pit <br />manager. The existing conditions discussed above are reflected in the model in order to calibrate to the most current <br />and accurate Site conditions. <br />Figure 7 shows the modeled groundwater contours. Table 7 below reports the steady-state modeled water levels and <br />the measured water levels ai the Site. Figure 6a shows a graph of the location versus site groundwater level. Overall, <br />the model matched the existing groundwater gradient to a good degree of accuracy. <br />Table 7 <br />Measured and Modeled Site Groundwater Levels <br /> <br />Well <br />Observed <br />Modeled Difference <br />fl <br />MW01 4929. 32 4928. 61 0.71 <br />MW02 4933. 35 4933. 56 -0.21 <br />MW03 4933. 85 4933. 71 0.14 <br />MW04 4935. 81 4935. 36 0.45 <br />MW05 4933. 38 4933. 86 -0.48 <br />MW06 4938. 05 4938 .01 -0.56 <br />Notes: <br />1.Observed values are average measured water levels from the <br />2005 and January -March 2006. <br />4.1.1 Baseline Conditions <br />A modeling run was performed considering a "Baseline Condition" in order to compare the changed groundwater levels <br />to a more representative case than the existing conditions. The existing conditions case was modeled in order to <br />calibrate the model to known water levels as described above in Section 4.1. The baseline condition was run using the <br />same parameters as the existing conditions and removing the active dewatering occurring on the parcel between the <br />Parker Site and Dersham Site and removing the ongoing dewatering and recharge ai the gravel pit to the southwest. <br />The Brighton Pit slurry wall remained as well as the Tucson Pit slurry wall. The water levels during the baseline <br />simulations were used to compare mining phases and most importantly are a more representative comparison to the <br />reclamation water levels because the existing condition takes into account too many stresses on the system. <br />4.2 Mining Simulation <br />Mining conditions were modeled to show the potential impacts that dewatering could have on surrounding wells. The <br />mining conditions model was run to match the proposed mining phases as presented in Table 8 and Figure 8. A model <br />run was done for each phase of mining to evaluate the effects of dewatering. Constant head nodes approximately equal <br />to the bedrock elevation within the mined area were applied to each phase to reflect dewatering. Surrounding ponds and <br />Groundwater Model Report -Hall-Irvin Parker-Dersham Site - 7 • April 2006 <br />