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3.7 Mine Water Discharge Sites <br />Four mine water discharge sites are currently associated with the TC operations are monitored. Site 109 requires <br />quarterly monitoring for flows, field parameters, and water quality samples (when flowing), and site 115 is <br />monitored as a CDPS discharge point in accordance with the requirements set forth under CDPS Permit No. CO- <br />0042161. <br />Two other mine water discharge sites are discussed in greater detail under a subsection to Section 3.6 above. To <br />dewater the old WMD and EMD, pumps and piping were installed to direct mine water from the Fish Creek Vent <br />Shaft (FCVS) and IORT #1, to the Area # 1 Pit. Overflow from the Pit passes through site 7 to Pond D, and <br />subsequently through CDPS Outfall 005A to Foidel Creek. Site 7 requires quarterly analyses when flowing per <br />DRMS Permit No. C -82 -056. Site 7 discharged during the second and third quarters of 2014. Outfall 005A <br />requires weekly, twice monthly, monthly, and quarterly water quality sampling when flowing, under CDPS <br />Permit CO- 0027154. <br />There has been no flow from site 109 to Foidel Creek for several years, and none in 2014. Site 115 had not <br />discharged to Fish Creek since early 2005, but was reactivated in 2008 and 2009, both for a limited times (i.e. <br />approx. one to three months) with low flows (25 — 500 gpm). Site 115 did not discharge in 2014. <br />Note that mine water is pumped from underground to the surface (from the old WMD), and was treated via an <br />electro - coagulation process at the surface, where water enters the 3 former treatment ponds that can be directed <br />through site 115. Treatment was not conducted in 2014. This water is pumped directly back into the mine for <br />underground dust suppression. Additional overflow piping was added so the treatments ponds cannot overflow. <br />Overflow water is directed back into the mine via a former pump well. <br />Historically, when pumping mine water from the Fish Creek Borehole (mine discharge site 115) the flow <br />becomes a contributor to sulfate levels in Fish Creek. Fish Creek in turn contributes to the sulfate levels in Trout <br />Creek. Trout Creek currently had a secondary drinking water standard limiting sulfate concentrations above 250 <br />mg/l. Table 53a provides historical water quality data. <br />3.8 2014 Inflow Survey <br />An inflow study was conducted underground in the winter. Flow rates and field parameters were recorded for <br />measurable inflows from the accessible areas of the underground mine. Results of this survey are presented on <br />Figure 117, 2014 Inflow Study Mined Area (in map pouch at back of report). Note that this map also includes <br />historic data for older underground areas, the majority of which have subsequently dried up. <br />Background <br />The old WMD was closed in 1996. At that time inflows were 52 gpm. Note that water elevations for the old <br />WMD were monitored periodically at the Fish Creek Borehole. Our best estimate is that inflows for the old <br />15 <br />