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George V. Patterson, Energy Fuels Coal, Inc. <br />Page 6 <br />April 23, 2015 <br />2013 Memo (page 13), wherein it states `Additional monitoring of the coal zone is not <br />warranted. - - - since groundwater is already known to be of degraded quality and unlikely <br />that it would be put to beneficial use, this would provide little additional information - - - ". <br />DRMS: ii) Please clarify the lowest elevation that could be measured if MWNW were <br />clear, and whether or not this is the floor of the mine, (5855' was the elevation <br />discussed in TR35 adequacy correspondence and given on page 2.05.6 -53 of the PAP; <br />5860.5' was used in the 2013 Summary Report by BBA) <br />EFCL- As previously stated, the elevation of the floor of the mine workings is 5855 feet. The <br />mine workings were 5.5 feet in height in the vicinity ofMW -NW, the referenced elevation of <br />5860.5 feet stated in the BBA 2013 Summary Report is the elevation of the roof of the <br />workings where the steel casing was cut off during mining operations. <br />DRMS: iii) Please provide a discussion of well MW16 explaining the fact that the <br />recorded water level dropped below 120' below ground surface (bgs) numerous times <br />between 1979 and 2000, but that since 2000 the well has often been reported as dry <br />with the depth to water indicated as 110' bgs (according to Exhibit 25, the depth of <br />MW16 is 136' and the screened interval is from 106' -136') <br />EFCI: Regarding MW -16 although it is uncertain as to why water levels fluctuated in MW- <br />16 during 1979 -2000, potential water sources for MW -16 are the abandoned Peacock Mine <br />and the abandoned Pine Gulch Mine, both being in the Red Arrow seam and situated up- <br />dip from MW -16. Both mines are located at the outcrop and are recharged by <br />precipitation. Given that the flooded Peacock Mine in particular, flowed into the Southfield <br />Main Entries (Peacock Inflow 2), and that the Peacock is recharged by precipitation, it is <br />conceivable that static water pressures in the abandoned mines (draining /recharging) were <br />influencing the water levels in MW -16. <br />The Division's statement that MW -16 was "often reported as dry at 110 ft with depth to <br />water indicated as 110 ft" is contradictory. Various AHR's reported "mud" at 110 ft bgs <br />which does not imply that that was the water level, i.e. the well had no water at 110 ft as <br />reported in the respective AHR's. More importantly, the "'average' water level in MW -16 <br />during the 1979 -2000 time period was 104.1 ft bgs approximately 2 ft above the screened <br />interval of the well. <br />Concerning MW -16 being reported as dry, the above referenced abandoned mines are <br />located parallel to the Southfield Moose Panel and the Pine Gulch Panel 113 workings and <br />being up -dip from MW -16, it is conceivable that the workings influenced water levels in <br />MW -16. Further, as is referenced in the Division's February 12, 2015 Adequacy Review <br />letter, (National Drought Mitigation Center (http: / /droughtmonitor. unl. edu)) the region has <br />been in drought conditions for several years during which MW -16 has been dry. <br />Nonetheless, according to well completion data, 4 vertical feet of the screened interval is <br />available to accept water if it was present. <br />