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2008-03-21_PERMIT FILE - C1980007A (46)
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2008-03-21_PERMIT FILE - C1980007A (46)
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Last modified
8/24/2016 3:25:41 PM
Creation date
6/20/2008 3:24:27 PM
Metadata
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Template:
DRMS Permit Index
Permit No
C1980007A
IBM Index Class Name
Permit File
Doc Date
3/21/2008
Doc Name
pg 2.05-200 to 2.05-300
Section_Exhibit Name
2.05.6 Mitigation of Surface Coal Mining Operation Impacts Part 2
Media Type
D
Archive
Yes
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West Elk Mine <br />Sanitary Wastewater -West Elk Mine has apackage-type wastewater treatment plant to treat <br />sewage (primarily shower water) from the mine's facilities. The plant, constructed in 1982, has a <br />designed throughput of 10,000 gallons per day. With an aeration basin and clazifier, the plant <br />provides primazy and secondary treatment. The wastewater treatment plant is operated under <br />applicable state laws that govern wastewater treatment facilities, administrated by the CDPHE. <br />In 1996, MCC expanded the plant to increase the throughput to 20,000 gpd. The expansion <br />included a 3,000 gallon flow equalization tank, an additional clarifier and a flocculent system. <br />The clarifier is added to provide additional retention and clarification as a passive safeguard to <br />plant operation. The flocculent system will be used as a secondary safeguard that may be <br />operated to entrance solids settling in the primary clarifier. <br />Runoff from Disturbed Areas -Overland runoff, which passes over disturbed areas within the <br />permit area, is channeled to one of the sedimentation ponds. Sediment pond water may be <br />discharged to the North Fork or stored when water rights are in priority for reuse within the mine <br />azea, The quantity of effluent discharged from the sedimentation ponds is described in the <br />quarterly NPDES discharge monitoring reports and in the Annual Hydrology Reports. <br />Underground Water Management <br />Historically (prior to 1996), mine process water runoff and groundwater inflows flowed down- <br />dip in the B Seam workings, and were collected in various sized open sumps, pumped to the <br />sump at the bottom of the slopes, and then pumped to one of the sedimentation ponds on the <br />surface (MB-1 or MB-2R). After the water daylighted at the mine portals, a chemical coagulant <br />and/or flocculent was added to the flow prior to entering the sedimentation ponds. After typical <br />residence times of a few days, the pond water was dischazged in accordance with MCC's <br />NPDES permit. Prior to 1996, MCC had a strong history of NPDES permit compliance. <br />Two key events occurred in 1996 that caused MCC to alter this historic practice. The first was <br />the unprecedented inflows from the BEM fault. The second was the presence of a new colloid <br />in the mine water that would not settle out in the ponds. As a result of these events, MCC <br />changed both the way it manages water underground and the way it treats the water. <br />The current mine water management practices (as of 2004) are shown schematically in Figure <br />22. In general, the schematic represents three key components: mine inflows, mine outflows, <br />and in-mine water transfers. In order to better keep track of the quantities of water coming into <br />the mine, leaving the mine, and being stored in the various sealed sumps, MCC has installed and <br />will install numerous totalizing flow meters. These flow meters will enable a more accurate <br />computation of the mine water balance, <br />Mine Inflows -Mine inflows consist of imported water from the North Fork for mining uses, <br />various, smaller groundwater inflows, and significant groundwater inflows, such as the BEM <br />and 14HG faults. The large groundwater inflows aze shown sepazately since they require <br />special management. Estimates for the various mine inflows for 2002, for instance, are as <br />follows: <br />r1 <br />U <br />2.05-226 Revised November 2004 PRl0; Rev. March 2006; Rev. May 2006 PRl0 <br />
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