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Mining related dewatering impacts were noted for the Fish Creek sandstone wells 91M001 and 91M004 (Figure <br />26), and the Ashley well (Figure 27). Wells 91M001 and 91M004 were undermined in 1995 and exhibited <br />historic water level declines corresponding to mining activity. Water levels in these wells subsequently stabilized, <br />exhibiting only seasonal fluctuations. Two springs (SW -1 and SW -2) are monitored in the same vicinity as <br />91M001 and 91M004. Minor flow was detected in SW -1 during May 2011. SW -2 exhibited no flow in 2011. <br />The Ashley well was undermined in 1999 and exhibited water level declines corresponding to mining activity. <br />This well appeared to be recovering in 2000, continuing through 2011. <br />No unusual observations are noted with respect to Foidel Creek alluvium groundwater levels. The historical <br />increasing conductivity trend in well 001 -S -5 (Figure 32) stabilized in 2004, and appears to be increasing again <br />through the end of 2011. <br />No unusual observations are noted with respect to Fish Creek alluvium groundwater levels. The general water <br />level decline noted in well 006 -AY -1 (Figure 34) since 1995, appears to continue in 2011. Overall, fluctuations <br />at this well are insignificant. No other notable water level observations are apparent based upon review of the <br />2011 data. Field conductivity readings at this well appear stable over the last few years. <br />Surface Water: Recorded surface water flows for Foidel Creek, Fish Creek, and Trout Creek were generally <br />high in comparison to TC's historic record because of a heavy snow year. Flooding of Fish Creek, Middle Creek, <br />and Trout Creek was observed in areas from late March through May. A stream gage study was initiated by TC <br />with the aid of a consultant in the fall of 2007, continuing through 2011. This study will continue in the spring, <br />summer and fall of 2012. A discussion of this study, including results for re- evaluating stream rating curves will <br />be included in the 2012 AHR. <br />Conductivity concentrations at site 301, 69, and 1005 on Trout Creek appeared elevated during the spring runoff <br />season in April. This may be the result of upgradient spring runoff flushing through the old P & M mine area. <br />No other water quality impacts of concern were evident at any surface water sites monitored during 2011. <br />Spoil Springs: Recorded 2011 spoil spring discharges remain minimal and, therefore, did not constitute a <br />significant portion of discharge from the TC mine area with the potential to impact off -site areas. Discharges <br />from sedimentation ponds predominately occurred in conformance with applicable CDPS permit limitations and <br />therefore did not constitute significant impacts to receiving waters. <br />Mine Discharge: Mine water discharge site 109 did not discharge to Foidel in 2011. In 2005, TC began <br />redirecting electro - coagulation treated mine water pumped from the Fish Creek Borehole well, underground <br />locations for dust control. Mine water from the Fish Creek Borehole well (which is treated by electro- <br />coagulation) inadvertently discharged to Fish Creek over two days in January 2011 because of a cracked pipeline <br />valve. No other discharge occurred in 2011. <br />The mine pump at TORT began discharging to Foidel in September 2008 under an emergency discharge permit <br />issued by CDPHE. In early 2009, TC experienced difficulties in consistently meeting WET and iron standards at <br />the pipeline discharge source. In the second quarter of 2009, TC halted all discharge at the discharge source <br />18 <br />