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EMD (Panels 2 -Right through 6 -Right, PR97-04) <br />As with the initial EMD panels (9 -Right through 7 -Right), the proposed operations will not impact areas of <br />unusually high value for fish and wildlife. The prior database survey, which is present in Exhibit 19A, indicates no <br />nesting activity is occurring within the Middle Creek drainage. The recovery rooms for the southern longwall <br />panels in the EMD will be sufficiently removed from the Twentymile Sandstone outcrop to prevent complete <br />failure of the face. Therefore, the nests located in this section of the Twentymile Sandstone will not be impacted by <br />the continuing operations in the EMD. <br />NMD and WMD (Panels 17 -Right through 24 -Right, 12 -Left through 20 -Left, and 14- and 15 -Left Inby, PR <br />03-06, PR06-07, PR09-08, TR07-63, TR08-64, TR09-68, TR09-71) <br />TC's continued expansion into these areas of the North and West Mining Districts, will not impact areas of <br />unusually high value for fish and wildlife. There are no cliffs in the area that will be subsided, so there is no <br />potential for subsidence impacts to raptors. The Fish Creek valley will be subsided, as shown on Map 23, resulting <br />in the potential for seasonal flooding of low-lying areas and an increase in groundwater levels, relative to the <br />subsided surface along the margins of drainages channels. Both of these subsidence effects have the potential to <br />result in beneficial increases in riparian vegetation and habitat along the margins of affected drainages. The <br />flooded area will be dictated by surface flows in Fish Creek. During spring runoff, more of the valley will be <br />flooded, with flows and water levels declining, as the runoff abates. Rough approximations of flooded area <br />acreages are presented in the AVF report prepared by SUbTerra for these revisions. <br />Wolf Creek Reserve (Panels WC-5RT through 9RT, TR13-83, PR14-10, PR15-11) <br />The planned development and mining of the Wolf Creek Reserve will not impact areas of unusually high value for <br />fish and wildlife. There are no cliffs in the area that will be subsided, so there is no potential for subsidence <br />impacts to raptors. The Fish Creek valley will be subsided, as shown on Map 23, resulting in the potential for <br />seasonal flooding of low-lying areas and an increase in groundwater levels, relative to the subsided surface along <br />the margins of drainages channels. Both of these subsidence effects have the potential to result in beneficial <br />increases in riparian vegetation and habitat along the margins of affected drainages. The flooded area will be <br />dictated by surface flows in Fish Creek. During spring runoff, more of the valley will be flooded, with flows and <br />water levels declining, as the runoff abates. Roughm <br />approxiations of flooded area acreages are presented in the <br />AVF report prepared by SubTerra for these revisions. <br />In those areas where ancillary facility installations such as ventilation installations, utility boreholes, and <br />dewatering facilities are necessary to support mining and related activities, plans for surface disturbance and <br />ongoing activities will be reviewed with Colorado Parks and Wildlife (CPW) to identify any potential wildlife <br />impacts and incorporate any appropriate mitigation measures. In general, TC will incorporate any appropriate CPW <br />mitigation recommendations in the proposed development, mining, and reclamation plans. Dependent on the <br />specific location and circumstances, this may involve relocation of proposed roads and surface installations, <br />seasonal or daily timing restrictions, measures to control activities and noise (ie: shielding, noise reduction <br />measures, facility enclosures. limitations on site lighting or automatic sensors, fencing, etc.). <br />3 Protection of the hydrologic balance. <br />MR16-296 2.05-127.1 05/03/16 <br />