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Strricvr - 2.05.6 <br />In general, depression of the water table near the mine is expected to be both minor and 1«alized due <br />• to the re]atively low permeabihty of the ass«iated stntigraphic units. Additionally, ground water <br />flow patterns in the overlying perched aquifer system may also be affected by downward leakage <br />through subsidence fractures. This may result in partial or full drainage of the perched aquifers and <br />may affect the discharge of springs and seeps. Impacts on perched aquifers and azs«iated springs <br />and seeps due to secondary subsidence effects are not expected to be significant since the perched <br />aquifers are very limited in areal extent, potential subsidence areas represent a relative small pottion of <br />the total permit area, and there are no known adjudicated or other beneficial rues from the perched <br />aquifer system <br />Upon completion of operations and final mine reclamation and closure, ponions of the underground <br />workings will gradually fill with water resulting in reestablishment of the water table at approximately <br />the same level which existed prior to mining. Any minor changes in water levek which may «cur are <br />not expected to be significant since the overall hydrologic balance within the ground water bazin will <br />not be effected. Reductions in the quantity and availability of ground water az a result of alterations <br />to the ground water flow patterns are expected to represent a minor percentage of total ground water <br />flows within the bazin, will be limited in areal extent, and should be temporary in nature. In addition, <br />reductions in groundwater flows are not expected to adversely impact ground water users since <br />beneficial ground water rue in the general area u limited to the North Fork alluvium/colluvium which <br />is stratigraphically below and effectively hydraulically isolated from the sequence to be affected by <br />mining by low pem~eabiliry bedr«k. Potential impacts to springs and seeps discharging from the <br />perched aquifer system are discussed below. <br />OMI's mining activities may result in some drainage and dewaering of overlying perched ground <br />water aquifers az a result of vertical seepage through subsidence fractrtres. Consequently, springs and <br />seeps discharging from the stratigraphic units containing the perched ground water maybe effected. <br />• OMI will attempt to m,~,mnr subsidence to the extent possible while m~~rimning recovery of <br />available coal resources. Subsidence will be controlled through the use of longwall mining methods, <br />maintenance of bamer pillars, limiting extraction in critical areas, and proper mining and roof control <br />design and operations practices. Effective control of subsidence will limit fracturing of overlying <br />strata and the consequent potential for drainage through subsidence fractures. Additional discussion <br />of potential subsidence effects is presented in Section 2.05.6, Subsidence Survey, Subsidence Control, <br />and Subsidence Monitoring Plan <br />Although subsidence fracturing may result in limited discharge from ass«iated perched ground water <br />aquifers, changes in the general potentiometric surface are not anticipated since the perched aquifer <br />system u isolated from the water table aquifer by the low pemreabiliry interbedded silutones and <br />shales of the underlying formations, storage volumes in the isolated perched aquifer «currences are <br />minor compared to the regional system, and any subsidence fractures are expected to gradually fill-in <br />with natural consolidation and mineral deposition. L«alized changes in the potentiometric surface <br />for the perched aquifers within mine subsidence areaz may have some effect on ground water levels <br />and flow rates in those ground water aquifers which supply surface springs and seeps. <br />A total of eleven springs were I«ated and monitored by Western Slope Carbon from 1983 through <br />1987. Seven of the springs (Nos. 1 - ~ are ephemeral and four (Nos. 8 - 11) are peremiaL The <br />perennial springs have an average combined total recorded flow of only 23 gpm or 0.05 cfs and az <br />such do not represent a significant ground water resource. If, however, discharge from any seeps or <br />springs which are beneficially utilized is documented az having decreased below bazeline conditions az <br />- a result of mining-related activities, OMI will mitigate these impacts through augmentation of any <br />affected water rights, monetarycompettsa[ion, development of alternative watering facilities such az <br />guzzlers, or other appropriate mitigation meazures. <br />• As ground water encounters freshly exposed subsurface materials in the mine, oxidation and <br />weathering will cause changes in ground water chemistry including increases in TDS and the <br />concentrations of individual chemical constituents. Over time these increases will stabilize and start <br />PR04 2.05-95 Revised August 2000 <br />