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� 1n <br /> ' o Transit Mix Concrete Co. <br /> slope is maintained while the stockpile is constructed, and then the stockpile is regraded to <br /> 3H:1V for reclamation. The stockpile design includes benching to minimize the regrading <br /> volumes. The only additional work will be the drainage channel and placing material in the <br /> pit area between F2 and the highwall. Therefore, volumes and costs have not been provided <br /> as this work is to be completed during Phase III. Exhibit D has been revised to more clearly <br /> discuss the stockpile slope gradients and grading. <br /> 124) On page 5 of the Waste Stockpile Stability Analyses, the Applicant states that seeps are <br /> known to be present in the vicinity downstream of stockpile TSI, but they are located <br /> below the toe of the stockpile near the creek. However, information provided in Exhibit G <br /> shows an upward vertical hydraulic gradient component at groundwater monitoring wells <br /> GW-1, GW-3, and GW-4, indicating areas of potential groundwater discharge to Little <br /> Turkey Creek surface water flow or to ground surface within the Little Turkey Creek valley <br /> in the form of seeps. Monitoring wells GW-3 and GW-4 are located upgradient from <br /> stockpile TS1. This is particularly well shown in Figure 3-2 —Potentiometric Elevations for <br /> Groundwater in the Hydrogeology and Impact Analysis by Hydro-Logic Solutions, Inc., <br /> where locations of the monitoring wells are plotted along with mine features. Figure 3-2 <br /> shows GW-3 (7,072 feet potentiometric elevation) located within the F2 backfill area, <br /> approximately 375 feet from the northern quarry edge. Figure 3-2 shows GW-4 (7,024 feet <br /> potentiometric elevation) located within the plant area, approximately 300-375 feet from <br /> the northern quarry edge. This means that potential seeps are present upgradient from the <br /> proposed TS 1 stockpile. Please provide clarification on these seep areas, including any <br /> potential impacts they might have on stability of stockpiles/backfill areas. Additionally, <br /> because the plant area is to be mined down to an elevation of approximately 6,950 feet, <br /> which is well below the potentiometric elevation of GW-4, please discuss whether the <br /> Applicant anticipates this having any effects on plant operations. <br /> Response: No seeps have been identified upgradient from the locations presented on the <br /> various maps in Exhibit C and G, and seepage into the stockpile is not expected. <br /> Regardless, seepage is not expected to have an adverse impact on stockpile stability. The <br /> Waste Stockpile Stability Analyses specifies that the fines material is considered to be a <br /> well-drained material that will sufficiently convey any seepage waters to Little Turkey <br /> Creek without the phreatic surface rising beyond the contact between bedrock and the fines <br /> material. <br /> Seepage is also not expected to have any impact plant operations. The groundwater <br /> assessment demonstrates that seepage flows during Phases I and II of mining are less than 5 <br /> gallons per minute. These flows will be diverted into Little Turkey Creek through the <br /> stormwater management system without impacting <br /> 125) In the Waste Stockpile Stability Analyses, Figures G1.1 through G2.2 for Section G (across <br /> F2 backfill area) do not appear to correlate with the G-G' section line shown in Figure 1 — <br /> General Arrangement with Section Lines, particularly at the G' end of the sections. The G <br /> end (left side) of the sections appear to line up with the G-G' section line shown on Figure <br /> 1, as they start at about the elevation of the pit floor, 6,950 feet. However, the elevations of <br /> the ground surface at the G' end (right side) of the sections is not consistent with the <br /> Hitch Rack Ranch Quarry(M-2017-049) <br /> Response to Comments—March 9,2018 <br />