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Environmental Protection Plan, Schwartzwalder Mine 11-1 <br />• 11. SURFACE WATER QUALITY DATA <br />Surface water quality in Ralston Creek has been monitored by the Operator since the water treatment plant <br />began discharging in 1983. Water quality in Ralston Creek is affected by natural runoff and groundwater <br />inflow, upgradient abandoned mines, and by fill material in the valley at the Schwartzwalder mine. Prior to <br />2002, water quality in Ralston Creek was also influenced by discharge from the Schwartzwalder water <br />treatment plant. <br />This section of the EPP summarizes the water quality standards for Ralston Creek, the locations of <br />historical monitoring stations, the available surface water quality data, and trends in uranium concentrations <br />in the creek. <br />(a) Surface Water Quality Standards <br />(i) Discharge Permit Limits <br />Discharge permit limits have changed over time. The original discharge permit (#CO-000 1 -244) issued by <br />the State of Colorado listed effluent limits for water discharged from the water treatment plant operated at <br />the site. When the water treatment plant was operating during mining (and up to the time of treatment plant <br />shutdown in 2002), those limits included specific metals, uranium (0.776 mg/L), and radium 226/228 (3 <br />pCi/L), as shown in the Table 11-1. The resumption of water treatment in 2010 is subject to revised <br />effluent limits (Table 11-2) which are currently undergoing review and public comment. The most <br />significant modifications to the effluent limits include a reduction in allowable uranium concentrations <br />from 0.776 mg/L to 0.03 mg/l and the addition of monitoring requirements for arsenic, cadmium, <br />chromium VI, iron, mangangese, mercury, nickel, selenium, chloride, and sulfate (Table 11-2). <br />• Alluvial groundwater that was treated during the period from July 2 to July 30, 2010 in the interim (50 <br />gpm) water treatment system described in Section 15(b)(i) was subject to interim effluent limits. Those <br />limits were identical to the limits shown in Table 11-1 except that the daily average and maximum limits <br />for total recoverable uranium were set at 0.03 mg/L (30 µg/L). <br />Table 11-1. Existing Discharge Permit Effluent Limitations <br />• <br /> <br />Effluent Parameter Effluent Limitations <br />Maximum Concentrations <br /> 30-Da Avera a Dail Maximum <br />Flow, MGD 0.288 Re ort <br />COD, m g/1 100 200 <br />Total Suspended Solids (TSS), mg/1 20 30 <br />Potentially Dissolved Uranium, ug/1 776 1243 <br />Radium 226 +228 (total), Ci/1 3 10 <br />H, s.u. minimum-maximum NA 6.5-9 d/ <br />Oil and Grease, mg/1 NA 10 d/ <br />Total Recoverable Antimony, u g/1 6 Report <br />Boron, m g/1 0.75 Report <br />Total Recoverable Chromium, u g/1 11 16 <br />Potentially Dissolved Copper, u g/1 5.4 7.7 <br />Potentially Dissolved Silver, u g/1 0.027 0.73 <br />Potentially Dissolved Zinc, u 1 71 71 <br />Weak Acid Dissociable Cyanide, u 1 NA 5 <br />Fluoride, mg/1 NA 2 <br />Total Recoverable Thallium, u 1 0.5 NA <br />Whole Effluent Toxicity, Chronic Lethality <br />Cerioda hnia species NA IWC = 100% <br />Fathead Minnow Pime hales romelas NA IWC = 100% <br />4109C.100731 Whetstone Associates