My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
2011-12-15_REVISION - M1977493 (2)
DRMS
>
Day Forward
>
Revision
>
Minerals
>
M1977493
>
2011-12-15_REVISION - M1977493 (2)
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
8/24/2016 4:46:08 PM
Creation date
4/11/2012 3:40:41 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1977493
IBM Index Class Name
REVISION
Doc Date
12/15/2011
Doc Name
ENVIRONMENTAL PROTECTION PLAN
From
CLIMAX
To
DRMS
Type & Sequence
TR18
Email Name
ECS
Media Type
D
Archive
No
Jump to thumbnail
< previous set
next set >
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
240
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
View images
View plain text
Technical Revision (TR -18) Climax Molybdenum Company <br />Environmental Protection Plan Permit No. M- 1977 -493 <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 tum, <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. As required under Rule <br />6.4.21(6), appropriate EPFs have been identified to minimize, capture and treat acid mine drainage (see <br />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 Permit Amendment Application AM -06, <br />overburden placement will consist of additional placement in the area of existing E and F dumps as well <br />as the existing McNulty OSF. The scheduling /sequencing of overburden placement is being performed <br />during the summer of 2011 as part of ongoing mine plan evaluations. This investigation and design work <br />is focused on geotechnical stability, but will also include the development of a stockpile operations and <br />monitoring plan. The operations and monitoring plan is anticipated to include recommendations and <br />guidelines for overburden placement, which will be used in the development of EPFs for the OSFs. <br />Seepage collection and run -on and run -off control facilities are identified as EPFs (see Section T- 5.3.2) at <br />these locations to minimize the impact of potential acid drainage associated with these facilities. Designs <br />for these EPFs will be submitted prior to the initiation of construction in accordance with Rule 7.3. <br />The acid - forming materials will remain in -situ at the Climax site 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) presents <br />a summary of water quality data from impacted sources, including seepage from the OSFs, TSFs and <br />other sources from around the site that are collected and treated. Samples of impacted water sources <br />will continue to be collected by Climax on an as needed basis. <br />T 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 Final Closure <br />Upon final closure and reclamation of the Climax Mine as described in the 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 />EPP: Version R2 <br />T -14 December 2011 <br />
The URL can be used to link to this page
Your browser does not support the video tag.