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methodologies were utilized. First, the monitoring data from the old Peabody Nucla Mine were <br />analyzed to determine the annual volume of flow into the pit from actual observations and to also <br />determine the distance of drawdown (cone of depression) observed as the old Peabody Nucla <br />Mine advanced to the north (see Map 2.04.7-1, "Old Peabody Nucla Mine Highwall"). The <br />second method involved the determination of pit inflow rates and drawdown in the adjacent <br />overburden and coal zones as a result of groundwater drainage from the bedrock zones into the <br />pit utilizing a version of the groundwater flow model MODFLOW. A description of the <br />modeling procedures and the assumptions used are provided in Appendix 2.05.6(3)-2. <br />Observation and Analysis Flow from the old mine backfill (SS#1, #2, and #3, see New <br />Horizon 1 Mine Permit) indicate that total seepage from that high -wall varied from a low of <br />about 17 gpm (during periods of no irrigation) to a high of about 52 gpm during irrigation <br />season. The high flow rates average about 42 gpm and the irrigation season is about 165 days <br />long. The low flow rates average about 17 gpm and represent no irrigation for about 200 days per <br />year. The average annual flow rate is therefore on the order of about 28 gpm or about 5390 <br />ft3/day. This flow rate compares well with the flow rate of about 27 gpm calculated by <br />subtracting the flow in Nygren Draw (SW -N6) from the flow rate at NPDES 001, (see Table <br />2.04.7-5 in Section 2.04.7). This further suggests that once the irrigation water is diverted into <br />the HDPE pipeline that highwall seepage should be more on the order of about 17gpm (< 3300 <br />ft3/day) and then decrease as the bedrock zones dry out. <br />The bedrock zones are tight, with low transmissivity (measured OB and Coal Zone <br />transmissivity and hydraulic conductivity at 58 ft2/day and 2.1 ft/day respectively at GW -N9) <br />which results in limited but steep cones of depression. The old Peabody Nucla Mine (New <br />Horizon #1 Area) is again instructive as the hydrograph of GW -N8 (see pg. 7-1-75 of New <br />Horizon 1 Mine Area Permit) shows the water level was first affected by the mining in <br />November 1980. At that time the coal face was about 760 ft from hole GW -N8. Total draw down <br />at GW -N8 after 2 years and 9 months was 12.24 ft. Monitor hole GW -N9 at a distance of 854 ft <br />from the final high -wall has never been affected, (see GW -N8 and GW -N9 hydrographs in <br />Appendix 2.05.6(3)-2; Figures 2.05.6(3)-2a and 2.05.6(3)-2b). Based on the evaluation of these <br />observations, water level drawdown in the bedrock zones is expected to only extend about 590 <br />feet beyond the permit boundary. NHN's hydrologic consultant, Bishop -Brogden Associates, <br />Inc. (BBA), prepared Figures 2.05.6(3)-2f and 2.05.6(3)-2g in order to illustrate the observations <br />at GW's N8 and N9. These two figures are contained in Appendix 2.05.6(3)-2. Figure 2.05.6(3)- <br />2c in Appendix 2.05.6(3)-2, is an illustration of the projected draw down from an ideal pit in a <br />stationary position based on the evaluation of the GW -8 and GW -9 hydrographs. Water level <br />measurements were suspended at GW's-N8 and N9 from 1987 through 2007 and the "old" <br />highwall was reclaimed in 1992. Water level monitoring at these two holes was resumed during <br />2008 and 2009 as part of the 2 year "close out" monitoring for New Horizon #1 Area Permit. <br />Water levels in GW -N8 have recovered about 80% of the maximum draw down since the <br />Section 2.05.6(3) Page 12 April 2016 (PR -01) <br />