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Water Quality Monitoring Plan Climax Molybdenum Company <br /> Version:R4 Permit No. M-1977-493 <br /> 4.1.4 Surface Water Monitoring Baseline Data Evaluation <br /> Analytical data collected from the internal surface water monitoring locations CC-SW1, and EI-SW1 during <br /> the extended baseline monitoring period is presented in Appendix B-4. Tables included in Appendix B-5, <br /> present available surface water data from the East Fort Arkansas River, East Fork Eagle River and the <br /> EPR outlet. Monitoring using the full baseline parameter list began in the fourth quarter of 2011 for the <br /> Eagle River and EPR Outlet locations, and the first quarter of 2012 for the Arkansas River locations. The <br /> data for each location are presented in individual tables. The data in these tables have been summarized <br /> with descriptive statistics, including the calculation of the minimum, maximum, and mean concentrations, <br /> the standard deviation, the number of data records, or analyses for each analyte, and the number of <br /> observations below the method detection limit. <br /> In accordance with the approach described in TR-18, river and EPR Outlet data are presented along with <br /> applicable surface water standards for the East Fork Arkansas and East Fork Eagle Rivers. As described <br /> in Section 3.1.6, Arkansas River monitoring location Arkansas#1 is upstream of former and present mine <br /> facilities in the upper reach of the Arkansas River basin. Arkansas River monitoring location Arkansas#2 <br /> is located at the property boundary on the south side of Highway 91. In evaluating the full period of record <br /> at these locations, concentrations of several water quality constituents have decreased since monitoring <br /> began in 1993, most notably are decreases in manganese and zinc, although there is a seasonal pattern <br /> with higher concentrations typically observed in the early spring. <br /> Consistent with the groundwater monitoring program, cadmium, copper, iron, manganese, molybdenum, <br /> zinc, pH, sulfate, and TDS are included in the indicator parameter list for long term surface water monitoring. <br /> Lead is not included due to its absence in collected mine water sources, the predominance of results below <br /> the detection limit, and the fact that recent data indicate concentrations well below surface water standards <br /> at all monitored locations. Because standards are in place for both dissolved and total recoverable iron, <br /> total recoverable iron will be added to the indicator parameter list. Similarly, although dissolved <br /> molybdenum has been monitored through the baseline period, total recoverable molybdenum has been <br /> added to the indicator parameter list since the surface water standard is expressed as total recoverable. <br /> Aluminum, calcium, and magnesium are not included as indicator parameters for the long-term monitoring <br /> at surface water monitoring locations. There are no surface water standards for these three parameters in <br /> any of the stream segments identified in Section 3 for the three river basins. Aluminum is not included as <br /> an appropriate indicator parameter, based primarily on recent data that are typically reported as non-detect. <br /> Calcium and magnesium are excluded because they are not considered indicators for the identification of <br /> impacts from mine-related sources. Hardness is retained in the indicator parameter list since it is a useful <br /> parameter for monitoring the East Fork Eagle and Arkansas Rivers, since many surface water standards <br /> are hardness based. Of the remaining additional baseline monitoring parameters, only arsenic and silver <br /> warrant significant discussion. Both dissolved arsenic and silver are reported as non-detect in nearly all of <br /> the samples obtained from the river and EPR surface water monitoring locations and, as discussed in the <br /> groundwater data evaluation (Section 4.1.1.1), neither arsenic nor silver are associated with mine-related <br /> sources at Climax. Therefore, arsenic and silver are not included in the indicator parameter list. <br /> The data collected at the internal surface water monitoring locations (CC-SW1 and EI-SW1, located above <br /> Clinton Reservoir), represent natural, un-impacted conditions. To simplify the monitoring program the same <br /> surface water indicator parameter list is recommended. For consistency, relevant surface water standards <br /> are also presented for comparison purposes with the data for the internal surface water monitoring location <br /> data in Appendix B-4. <br /> EPP—Appendix C May 2018 20 <br />