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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 />the colloidal particles. The colloids are clay particles with 95 percent of the particles smaller <br />than five microns and 35 percent smaller than two microns. The chemical flocculents/polymers <br />that had historically been effective did not work on this colloid. After extensive testing by MCC, <br />consultants and chemical suppliers, MCC determined that conventional alum in heavy doses <br />would be the most practical means for meeting the necessary TSS limits. There are significant <br />drawbacks to alum applications in this situation. First, substantial quantities of alum aze <br />required. For example, with MB-1 and MB-2R at capacity, approximately 4,000 pounds of alum <br />per week per pond were necessary. The chemical is corrosive and applying it to the <br />sedimentation ponds is difficult and costly (MCC has rented a "hydroseeder" truck to spray on <br />liquid alum). An even larger concern is the enormous quantity of "floc" that is generated by the <br />alum additions. MCC recognizes that it will be necessary to remove the alum floc that has <br />accumulated in the sedimentation ponds, on a more frequent basis, and this will require a major <br />expenditure each time. Continuing to apply alum in the current manner on a long-term basis is <br />not feasible. <br />MCC investigated and evaluated numerous water treatment systems to identify effective, <br />reliable, long-term alternatives for the reduction of TSS. Four technology categories were <br />evaluated; gravity sepazation of solids, batch treating of ponds, chemical treatment, and physical <br />treatment. The technology categories evaluated aze summarized below: <br />Gravity Seaaration of Solids <br />• Because an extremely long detention time was required to treat mine water to achieve <br />compliance dischazges (up to several weeks), this treatment technology was determined to be <br />infeasible. <br />Batch Treating of Ponds <br />This TSS treatment technology was determined to be infeasible for the following reasons: <br />Runoff from precipitation events cannot be prevented from entering an already treated pond, so <br />adding chemicals to treat the runoff could increase the potential for chemically overdosing the <br />pond. Also, due to the more frequent filling of the ponds, and thus constant settling of solids, the <br />sediment storage volumes would be filled faster, displacing water storage volumes. As a result, <br />expensive sediment clean-out of lined ponds would be more frequent, increasing the potential for <br />damage to the liners and creating high repair and/or replacement costs. <br />Chemical Treatment <br />Two options were evaluated for chemical treatment; both temporary and permanent treatment <br />systems. A temporary treatment system was determined to be infeasible, because gravity feeding <br />chemicals caused dosages to be irregular and difficult to maintain. To ensure proper treatment, <br />constant attention would be required for chemical adjustment. Also, chemicals aze often cold <br />temperature sensitive and would not flow properly from the dispenser during the winter. Surface <br />applications of alum worked well, however, the applications were expensive and would not work <br />. if the ponds were frozen. A permanent chemical treatment system was evaluated and was not <br />successful alone, as the system required a mechanical feed of chemical into a constant flow. <br />2.05-114 Revised November 1004 PRl 0; Rev. March 2006; Rev. May 1006 PRlO <br />
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