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RULE 2 PERMITS <br /> thereby theoretically increasing the mass of dissolved solids entering the groundwater. These dissolved <br /> solids in groundwater will eventually enter the surface water system, with a theoretical increase in <br /> dissolved solids in the surface water. This increase is calculated to be small enough to have no impact on <br /> the current or projected surface water uses in Wilson, Taylor, or Good Spring creek drainages. <br /> Groundwater <br /> Groundwater in the vicinity of the Lower Wilson and South Taylor mining areas is restricted to perched <br /> aquifers of limited extent within bedrock of the Williams Fork Formation, the Trout Creek aquifer (a <br /> bedrock aquifer of regional extent), and valley fill deposits as described in Section 2.04.7. The Williams <br /> Fork Formation aquifers have no beneficial use owing to their limited extent and minimal production. <br /> The Trout Creek Sandstone is a sandstone unit underlying most of the permit area and extending across <br /> much of northwestern Colorado. It contains water of useable quantity and quality as demonstrated by <br /> beneficial wells near the permit area. The Trout Creek Sandstone is beneath the mining impact areas and <br /> is separated from these impacts by clay and claystone layers within the Williams Fork Formation (see <br /> Section 2.04.5 and 2.04.6). A borehole intersecting the Trout Creek (84-B-TC - NW'/4, NE'/4, Sec. 19, <br /> T3N, R93W) was installed between the Lower Wilson and South Taylor mining areas. The Trout Creek <br /> formation was dry at this location, since the sandstone in this area outcrops to the west and is above any <br /> recharge source. With the dip of the strata to the north and east, the Trout Creek Sandstone, and <br /> overlying strata, do not become saturated until (1) the strata dips below the valley floor and (2) the <br /> elevation of the appropriate strata equals the elevation of surface water in Wilson and Good Spring Creek. <br /> Based on this information, mining is anticipated to have no impact on the Trout Creek aquifer. <br /> Groundwater in the shallow valley fill of Good Spring Creek is calculated to be marginally impacted by <br /> surface mining activities at South Taylor as described in the Probable Hydrologic Consequences. There <br /> are no registered beneficial-use wells in the Colorado Division of Water Resources well database within <br /> several miles, down gradient of the mining impact areas (Map I IB). <br /> 2.05.6 (3)(b)(i &ii) Hydrologic Controls <br /> Surface water and groundwater drainage from the mining areas will be controlled as described in Section <br /> 2.05.3(4) and Section 4.05.Surface water flow will be diverted around the mining operations and into <br /> sediment ponds. Stormwater that enters the mining operations and water that occurs on the mining <br /> operations will be allowed to evaporate or infiltrate, or will be routed into these surface structures. <br /> 2.05.6 (3)(b)(iii) Probable Hydrologic Consequences <br /> Rule 2.05.6(3)(b)(111) requires determination of probable hydrologic consequences for the mining <br /> operations. This rule indicates that these consequences must be defined for both the permit area and <br /> adjacent areas, for quantity and quality of surface and ground waters. Baseline conditions must be <br /> established,and possible impacts from the activities must be anticipated. <br /> Summary of'the Probable Hydrologic Consequences—South Taylor Pit <br /> The anticipated probable hydrologic consequences of mining coal in the South Taylor area are: <br /> Springs near the South Taylor Pit might experience increased and/or decreased flow. <br /> The South Taylor pit will eliminate several seeps and springs. <br /> • Dewatering of the pit is not anticipated. <br /> • Hydraulic transmissivity within the backfilled pit will be higher than the adjacent unmined areas. <br /> South Taylor/Lower Wilson—Rule 2,Page 77 Revision Date: 6/22/20 <br /> Revision No.: MR-220 <br />