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George V. Patterson, Energy Fuels Coal, Inc. <br />Page 9 <br />February 12, 2015 <br />c) Impacts to Groundwater Quantity <br />The PHC section of the PAP predicts the following impacts to groundwater quantity: <br />• Minor reductions in down - gradient groundwater flows <br />• Possible dewatering of abandoned mines in the Vento seam <br />• Localized reductions in the piezometric surface <br />• Localized alteration of groundwater flow patterns <br />• Possible increases in recharge as a result of mine dewatering <br />hi the letter of October 24, 2014, that accompanied the TR43 application, EFCI referenced these <br />five predicted impacts and discussed each of them in qualitative terms. EFCI also provided <br />historical water level data from MW 16, MW23 and MW65. <br />The Division agrees with the general assertion made by EFCI, that the monitoring data that has <br />been presented supports the predictions, however this is not sufficient for approval of TR43. As was <br />laid out in the opening paragraph of this letter, the operator should provide a detailed analysis <br />showing, among other things, that onsite impacts have been minimized and offsite impacts <br />prevented, and should include... an evaluation of any impact trends which may exist in the <br />available data. In the context of impacts to groundwater quantity, this will require that EFCI <br />collect monitoring data from MWNW. <br />There is no doubt that the Southfield Mine has had an impact on groundwater quantity within the <br />coal seam and mine workings areas, but the extent of the impact is not well characterized. EFCI <br />have previously submitted several reports from Bishop - Brogden Associates, Inc (BBA) pertinent <br />to the discussion of groundwater quantity at the site, these reports are dated February 3, 1987,8 <br />July 19, 2013,9 and November 11, 2014.10 In the opinion of the Division, a misconception is <br />evident in the earliest of these reports. It has persisted and has led to confusion in the ongoing <br />discussion of groundwater at the site. In the 1987 report BBA characterized the hydrogeology of <br />the site based on water levels measured in five monitoring wells (MW8, MW 10, MW16, MW23 <br />and MW65) on May 20, 1986. These five points were plotted on a map and contour lines were <br />interpolated between them to produce figure 5 (1987 BBA report). This figure has the title <br />"Ground Water Elevations" which is misleading. The individual points on the figure are more <br />accurately labeled as "Elevation of potentiometric surface ". BBA used the contour lines of the <br />projected potentiometric surface to infer a head gradient (and consequent groundwater flow <br />direction) to the north east, parallel to Newlin Creek. Based on this analysis BBA characterized <br />the groundwater in the Vermejo formation as "tributary to the surface stream system ", with a <br />recharge zone to the west of the Chandler syncline, in the Wet Mountains; discharge where the <br />formation outcrops to the east; and with a continuous potentiometric surface in between. This <br />same conceptual model underlies the figure on page 2 of the 2014 report, which has red arrows <br />pointing upwards from the mined area labeled "Expected Water Level Recovery ". <br />The Division feels that a more accurate conceptual model is employed in section 2.04.7 of the <br />PAP ( "Hydrology Description "). The model is described in a 4 page section of the permit text, <br />pages 2.04.7 -8 through -11. The key points are summarized below: <br />