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Technical Revision (TR-28) Climax Molybdenum Company <br /> Environmental Protection Plan Permit No. M-1977-493 <br /> of the system of EPFs in-place in the Eagle River Watershed is demonstrated by water quality observed <br /> at water quality monitoring locations described in the Water Quality Monitoring Plan (Appendix T-C) and <br /> in water quality within Eagle Park Reservoir. <br /> Robinson Lake functions as a process water and seepage containment, storage and return system. The <br /> Robinson Lake Pump Station returns process waters directly to the process water tank for the mill. <br /> Because the integrity of this collection and return system is essential to production of molybdenum <br /> concentrates, close observation of its operation and maintenance of the systems is a priority. The <br /> development of the Robinson Lake Operating Plan (Appendix T-D) provides additional operational <br /> safeguards to prevent an overflow condition from Robinson Lake. <br /> The 4 Dam and Robinson Dam seepage collection and pump systems will remain in place and fully <br /> functional until such time as seepage from the dam meets water quality standards for this segment of the <br /> Eagle River. The seepage collected in the 4 Dam Seepage Collection System averages only <br /> approximately 10 gallons per minute, and the system has a redundant design to provide secondary <br /> containment, as described in Section T-5.2.2. The effectiveness of this system has been provided <br /> through monitoring water quality in the East Fork Eagle River at sites described in the Water Quality <br /> Monitoring Plan (Appendix T-C). <br /> The 1 Dam EPF has been effective in controlling the release of tailing material from the TSF. The <br /> regrading, capping, and reclamation of this dam (Section T-5.2.2) have increased its present and future <br /> effectiveness. <br /> T-5.4.3 Tenmile Creek Watershed <br /> EPFs in the critical Tenmile Creek Watershed have been, and continue to be, extremely effective in <br /> containing and controlling contaminants and preventing contaminant release into the environment. As the <br /> EPFs essentially function in series from the top of the watershed, the effectiveness of the system is <br /> increased through the redundancy or secondary containment afforded by this arrangement. Each EPF <br /> serves as a protective layer for up-gradient EPFs. However, it must again be emphasized that the upper <br /> Tenmile Creek Watershed has been significantly impacted by historic placer and lode mining, milling and <br /> smelting activities, which peaked in the 1880s. Prior to construction of the Mayflower TSF and the <br /> Interceptor System, impacted waters and significant loads of contaminated sediments from these non- <br /> Climax historic operations entered Tenmile Creek and were transported downstream. <br /> The Climax water treatment system successfully treats large volumes of water. The treated discharge at <br /> Outfall 001A has consistently met all effluent limitations contained in Climax's CDPS permit. Utilizing the <br /> first and second stage treatment processes of the SDP and PDWTP with lime addition for pH adjustment <br /> is an effective and time-proven means of treatment. <br /> The EPFs that control and contain the water treatment chemicals, as with the process water and tailing <br /> circuit, have a proven track record for effectiveness at the Climax Mine. As discussed in Section T-5.3.2, <br /> water treatment chemicals have primary and secondary containment. <br /> The ETDL and TDL generally have good records for effectiveness. However, leaks/spillage can and have <br /> occurred in the past. As described in TR-20 and TR-23, there is containment in the designs and, if leaks <br /> occur, any needed repairs to the line will be made promptly. As stated previously, other EPFs (East Side <br /> Channel and TSFs) adjacent to and downgradient of the ETDL and TDL also provide containment, <br /> preventing a release outside of the water management and treatment system. <br /> The effectiveness of the Robinson, Tenmile (TR-20), and Mayflower TSFs (TR-23) is self-evident. The <br /> Robinson TSF has been used since the mid-1930s, the Tenmile TSF since the mid-1950s, and the <br /> Mayflower TSF since the mid-1970s without failure. Each TSF will contain any major point and non-point <br /> source releases of potential contaminants from upstream areas including impacted seepages from the <br /> McNulty and North 40 OSFs, spillage/leaks from the ETDL and TDL, and potentially contaminated <br /> surficial run-off from haul roads, the pit area, and the yard areas around the mill facilities. The <br /> effectiveness of the Mayflower TSF (including the 5 Dam Seepwater Collection and Return System) in the <br /> Climax water treatment and discharge system has been discussed at length. <br /> Designated chemical storage EPFs within the mill all include secondary containment as described in <br /> EPP: Version R4 T-32 August 2018 <br />