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Page 4 of 5 <br />dissolved sulfate (mg /1), and total dissolved solids (mg /1). All <br />required parameters were analyzed. <br />18. Basic Standards for <br />CWQCC regulations 41.4 <br />The Seneca II Mine did not generate significant amount of <br />Ground Water <br />and 41.5 <br />Ieachates in 2012. Both groundwater wells exceeded the <br />manganese standard (0.2 mg /1) in 2012. As mentioned in the <br />above item number 8 above, in soils with a high pH a <br />standard of 10 mg /l would be more appropriate than the .2 <br />mg /1. In 2012 neither of the Seneca II wells displayed a value <br />higher than 3.5 mg /1. The TDS trend at well SBAL68 is stable <br />and do to the recent addition of well SFAL72 to the <br />monitoring program, a trend cannot be determined at this <br />time. <br />19. Restoration of ground <br />CDRMS regulation <br />For the 2012 water year, water levels at all wells fell within <br />recharge to approximate <br />4.05.12(3) <br />their historic ranges. All alluvial wells displayed seasonal <br />pre- mining rate <br />water level fluctuations in response to periods of <br />precipitation recharge. <br />20. Prevention of adverse <br />CDRMS regulation <br />Compliance with the Basic Standards for ground water, as in <br />impacts to ground water <br />4.05.11(1) <br />item 10, indicates the permittee is preventing adverse <br />systems outside permit area <br />impacts to ground water quality outside the permit area. <br />Monitoring data indicate the permittee is preventing impacts <br />to water quantity outside the permit area. Hydrology reports <br />indicate that a water level at all wells fell within their historic <br />ranges, with the exception of well SFAL72. SFAL72 is new to <br />the monitoring program so long term data is not available. <br />All alluvial wells showed seasonal water level fluctuations in <br />response to periods of precipitation or lack thereof. <br />Overburden and coal well water levels are fluctuating in <br />response to the precipitation recharge and ground water flow <br />from the reclaimed mine pits. <br />21. Prevention of impacts to <br />CDRMS regulation <br />No material damage has occurred, as discussed in item 20, <br />ground water that adversely <br />4.05.11(2) <br />above. <br />impact post- mining land use <br />22. Minimize disturbance to <br />CDRMS regulation <br />The disturbance to the hydrologic balance within and <br />hydrologic balance within <br />4.05.1(1) <br />adjacent to the permit area caused by mining and <br />and adjacent to the permit <br />reclamation at the Seneca II Mine is the minimum that can be <br />area <br />expected from a reclaimed surface mine at this location. Use <br />of best management practices indicates minimization of <br />disturbance to the hydrologic balance. <br />23. Prevention of material <br />CDRMS regulation <br />Surface water — Predictions were made for the TDS increases <br />damage to the hydrologic <br />4.05.1(1) <br />to be observed on Fish Creek during the months of June and <br />balance outside the permit <br />July due to discharges from the Seneca II Mine. In June, an 76 <br />area <br />mg /l increase was predicted between SSF11 and SSF13. In <br />July, a 74 mg /l increase was predicted between SSF11 and <br />SSF13. Based on the information provided there was a 50 <br />mg /l increase in TDS in June and a 40 mg /l increase in July. It <br />appears that the run -off from Seneca II has little impact on <br />Fish Creek. <br />