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Water Quality Monitoring Plan Climax Molybdenum Company <br /> Version:R4 Permit No. M-1977-493 <br /> ■ Antimony, barium, beryllium, chloride, cobalt, nickel, and total nitrate + nitrite as N: In <br /> general, no data are available for these parameters from collected mine water sources. <br /> Observed concentrations of these constituents at internal monitoring well locations are <br /> consistently well below the most stringent CBSG table values, typically at least an order <br /> of magnitude lower, indicating that these are not constituents of mine-related sources. <br /> Antimony concentrations, slightly above the CBSG value (0.006 mg/L), have been <br /> reported on two occasions in deep POC monitoring well TM-MW-002D. However, <br /> antimony has been reported as non-detect in approximately 92% of samples collected <br /> from every other groundwater monitoring well throughout the site, supporting the <br /> conclusion that antimony is not an appropriate indicator parameter. Antimony has not <br /> been detected in any samples from the shallow wells in the Tenmile Creek basin (GW#1 <br /> and GW#2) above the detection limit of 0.0004 mg/L, and the average and maximum <br /> observed concentrations in the upgradient deep well (TM-MW-001 D) are 0.0007 mg/L <br /> and 0.0032 mg/L, respectively. Ongoing monitoring of these parameters is not necessary <br /> for detecting potential mine-related effects. <br /> ■ Aluminum:As indicated in EPP Table T-E-6, aluminum has been observed in samples of <br /> collected mine water sources at concentrations above the CBSG value (5 mg/L — <br /> agricultural standard). For this reason, consideration was given to adding this metal to <br /> the indicator parameter list. Aluminum was reported as non-detect in approximately 90% <br /> of the groundwater samples in the Eagle River Watershed; with a maximum observed <br /> concentration of 0.21 mg/L in well EVMW-3D. In the Tenmile Creek Watershed, <br /> aluminum was reported as non-detect in approximately 88% of the samples in wells TM- <br /> MW-001 D, GW#2, and TM-MW-002D, with a maximum observed concentration for the <br /> watershed of 0.13 mg/L in shallow internal monitoring well GW#1. Similarly, in the <br /> Arkansas River Watershed, aluminum is detected in deep internal monitoring well AR- <br /> MW-002D, with a mean concentration of 0.24 mg/L and a maximum observed <br /> concentration of 1.25 mg/L. Aluminum in the other three wells in the Arkansas River <br /> Watershed was reported as non-detect in approximately 83% of the samples, with a <br /> maximum observed concentration of 0.05 mg/L in POC wells ARwell and ARK-MW-001 D. <br /> Based on a review of these data, although aluminum is observed in collected mine water <br /> sources, it does not appear to be a useful addition to the indicator parameter list, in <br /> comparison to iron, manganese, sulfate, and TDS. <br /> ■ Fluoride: Fluoride is observed in most of the wells within the monitoring network (with <br /> the exception of shallow POC well GW#2 in Tenmile, and EVMW-2 and EVMW-3S in the <br /> Eagle River Watershed). Higher concentrations are typically observed in the deep <br /> bedrock wells in the Arkansas and Tenmile Creek watersheds. A brief statistical <br /> summary of the fluoride data from the monitoring well network, using valid data collected <br /> through the fourth quarter of 20171, are presented in the tables below(for reference, the <br /> most stringent CBSG table value standard is the 2 mg/L agricultural standard and <br /> domestic water supply—human health standard is 4 mg/L): <br /> ' Some of the fluoride results from sampling performed in 2017 were determined to be invalid through the data validation process <br /> Non-standard laboratory procedures caused the unnecessary dilution of samples prior to fluoride analysis, resulting in reporting of <br /> estimated values or non-detect results at elevated method detection limits This issue was specific to fluoride analyses during <br /> several sampling events in 2017 and has since been corrected. <br /> EPP—Appendix C May 2018 15 <br />