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Freshwater and Siltation ponds would be filled in with overburden at the site which would lower their horizontal hydraulic <br /> conductivity to be similar to the Eolian deposits in the area. The horizontal hydraulic conductivity in these areas was set <br /> to 65 feet per day.The additional impacts from adding this site to the model are presented in Table 3a below and a <br /> layout of the site is shown on Figure 5 and 5A. <br /> Table 3a <br /> Mi ing Groundwater Level Table With Monarch DENM Site(Slurry Walls In-Place <br /> After Slurry Surface <br /> Basement Wall Difference(FT Groundwater Depth Elevation <br /> Location /n Baseline Construction Rise or Fall) Below Surface Goo le Earth Cell IJK <br /> Patrnd a House n 47363 47455 9.2 185 4764 161 1351 <br /> Cline House n 47368 47477 10.9 183 4766 162,1321 <br /> Hardinq House y 1 47366 4748.8 12.2 162 4765 161 1291 <br /> Wiedeman House <br /> 13434 n 4738.2 4750.8 126 172 4768 163,121,1 <br /> Wiedman House 13218 n 4738.5 47512 127 10.8 4762 163 1151 <br /> Sharp House y 4738.4 47509 125 9.1 4760 163 111,1 <br /> HS Land and Cattle n 4732.6 4744.7 121 103 4755 1551071 <br /> Karbowski Brave House n 47255 47315 60 20.5 4752 1451081 <br /> Schmidt Well NA 47144 4710.4 -4.0 226 4733 1321121 <br /> United Well NA 47120 47070 -5.0 41.0 4748 132,1261 <br /> Owens Well NA 47142 47117 -2 5 343 4746 132,1331 <br /> Wright House y 47174 47128 -4 6 39.2 4752 1351321 <br /> Schmidt House n 47184 47177 -0 7 30.3 4748 1351351 <br /> Smit House y 4718.8 47192 04 288 4748 135,1361 <br /> Kissler House y 47295 47348 5.3 20.2 4755 148,137,1 <br /> Woolverton House y 47308 4736.5 5.7 25.5 4762 150 1361 <br /> Shimon House y 4733.0 47397 67 193 4759 154 1361 <br /> Kern House y 47338 47409 71 191 4760 156,1371 <br /> Rainbolt House y 4735.9 4744.4 85 206 4765 161,1371 <br /> Gilcrest Valle HS NA 47370 47425 5.5 35 4746 170 1551 <br /> The addition of the full build out of the Monarch DENM Site increases mounding on the southern side of the Section 20 <br /> Site by limiting groundwater flow to the west. Slurry Walls along Highway 60 and the addition of the Monarch DENM <br /> Siltation and Freshwater ponds creates a groundwater corridor along Highway 60 north to the South Platte River,which <br /> causes the groundwater at the HS Land and Cattle building to rise approximately twelve(12)feet from baseline <br /> conditions. <br /> 6.3 Miti ation <br /> This section describes potential mitigation actions to decrease the mounding affect of slurry wall construction on the <br /> surrounding properties and the Town. The Monarch DENM Gravel Mine timeline submitted to the DRMS was utilized in <br /> conjunction with the Section 20 expected timeline to determine the phasing of mitigation construction. These timelines <br /> are approximate and are subject to change which may necessitate early construction of mitigation structures depending <br /> on measured groundwater conditions at the Site. <br /> The shadow affect to the north will likely be minimized by the proximity to the unnamed slough and the infiltration ponds <br /> to the northeast of the Site. During mining at the Site, an unlined siltation pond will be present in the northwest comer of <br /> the Site which will also mitigate some of the shadow affect. At this time no mitigation is recommended to address <br /> shadowing to the north unless groundwater monitoring demonstrates that the drop in groundwater head elevations is <br /> larger than anticipated. Mitigation would be warranted if any of the three well owners to the north complain about <br /> Groundwater Model Report-Section 20 Gravel Mine Site -9- August 2022 <br />