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2018-08-22_REVISION - M1977493A
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2018-08-22_REVISION - M1977493A
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Entry Properties
Last modified
3/6/2021 12:44:25 AM
Creation date
8/22/2018 4:39:03 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1977493A
IBM Index Class Name
REVISION
Doc Date
8/22/2018
Doc Name
Request for Technical Revision
From
Climax Molybdenum
To
DRMS
Type & Sequence
TR28
Email Name
ECS
MAC
Media Type
D
Archive
Yes
Tags
DRMS Re-OCR
Description:
Signifies Re-OCR Process Performed
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Technical Revision (TR-28) Climax Molybdenum Company <br /> Environmental Protection Plan Permit No. M-1977-493 <br /> flocculent used in the water treatment process will remain at the site until no longer required in the water <br /> treatment process. Removal and disposal of water treatment chemicals will occur as discussed for mill <br /> process chemicals during periods of temporary cessation or prolonged lack of mineral production. <br /> T-4 Acid-Forming Materials and Acid Mine Drainage <br /> The Climax ore body beneath Bartlett Mountain contains unoxidized sulfides that, in the presence of <br /> oxygen, water, and bacteria, have the potential to become an acid-forming material as defined in Rule 1, <br /> Section 1.1(1). Likewise, waste rock materials deposited in McNulty OSF, North 40 OSF, and tailing <br /> material deposited in the TSFs also contain material with acid-forming potential. Climax concurred with <br /> this fact in its response to the DRMS (August 31, 1994) when it accepted the DRMS determination that <br /> Climax was a DMO under the amended rules. In addition, water that percolates through the open pit area <br /> and accumulates in the pit or closed underground workings contacts sulfide bearing material and, in turn, <br /> has the potential to become acidified, thus, meeting the definition of "Acid Mine Drainage" in Rule 1, <br /> Section 1.1(2). <br /> Overburden material will be handled during operations, to the extent practicable, to minimize the <br /> generation and impact of acid drainage as well as the volume of water requiring treatment during and <br /> after mining. As overburden material is placed as part of ongoing operations, Climax will continually look <br /> for and identify opportunities to manage overburden materials to minimize acid rock drainage and the <br /> volume of water requiring treatment. Techniques will include, but may not be limited to, material <br /> segregation (based on acid generating potential), upgradient diversion of unimpacted water, and Climax's <br /> election to implement concurrent reclamation to minimize future acid drainage and the quantity of water <br /> requiring treatment. Concurrent reclamation of OSFs is described in Exhibit E of AM-06. As required <br /> under Rule 6.4.21(6), appropriate EPFs have been identified to minimize, capture and treat acid mine <br /> drainage (see Section T-5.3). <br /> The locations of OSFs have been developed with consideration of existing conditions as well as overall <br /> technical and economic feasibility. As described in Exhibit D of AM-06, overburden placement will consist <br /> of additional placement in the area of existing E and F dumps as well as the existing McNulty OSF. TR- <br /> 25 includes OSF design, stability analyses, and an operations and monitoring plan. TR-25 also includes <br /> final designs for seepage collection and run-on and run-off control facilities to minimize the impact of <br /> potential acid drainage associated with these facilities. <br /> The acid-forming materials will remain in-situ at Climax following final termination of mining and <br /> processing activities. As discussed herein, as long as acidic drainage with the potential to affect the <br /> environment is released from these sources, such drainage will be managed according to the stipulations <br /> and requirements of the appropriate regulatory permits in place at the time. <br /> The geochemical processes at the site are well understood to ensure the effectiveness of the water <br /> management and treatment system. Table T-E-6, included in Appendix T-E (Geochemical Data) is from <br /> EPP R3 (TR-24) and presents a summary of water quality data from impacted sources, including seepage <br /> from the OSFs, TSFs and other sources from around the site that are collected and treated. Samples of <br /> impacted water sources will continue to be collected by Climax on an as needed basis. <br /> T-4.1 Temporary Cessation/Prolonged Lack of Mineral Production <br /> Surface water discharge at Climax is regulated under the CDPS Permit as discussed in Section T-2.2. <br /> Under temporary cessation or a prolonged lack of mineral production scenario, mine waters, storm water, <br /> and seepage waters would continue to be managed, treated and discharged according to the conditions <br /> of this permit. <br /> T-4.2 Final Closure <br /> Upon final closure and reclamation of Climaxas described in the Reclamation Permit, Technical Revisions <br /> and Amendments, impacted waters from the mine, ponded water on the TSFs, seepwater from TSFs and <br /> OSFs, and storm water will be managed according to conditions of the CDPS Permit. This permit <br /> acknowledges that surface water from Climax must meet effluent limitations prior to discharge. <br /> EPP: Version R4 T-15 August 2018 <br />
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