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2014-11-04_PERMIT FILE - C2010089 (4)
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2014-11-04_PERMIT FILE - C2010089 (4)
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Last modified
8/24/2016 5:55:13 PM
Creation date
12/16/2014 12:25:44 PM
Metadata
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Template:
DRMS Permit Index
Permit No
C2010089A
IBM Index Class Name
PERMIT FILE
Doc Date
11/4/2014
Doc Name
Ponds, Impoundments and Diversions
Section_Exhibit Name
Section 2.05.3(4)
Media Type
D
Archive
Yes
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The excavated material suitable for topsoil will be salvaged in a stockpile used for <br />reclamation. The excavated material that is not suitable for a topsoil -like medium will be <br />graded into the surrounding topography within the disturbance area, topsoiled, and <br />revegetated in accordance with WFC's approved reclamation plan. Site specific <br />conditions will determine the construction methods and equipment utilized at the time of <br />excavation. Sediment removal and water discharges will be conducted consistent with <br />the approved mining permit, the Water Discharge Permit, and DRMS Regulations Section <br />4.05.6(3)(b). All sedimentation ponds will be inspected quarterly under the supervision <br />of a registered professional engineer and reported to the DRMS. The Water Discharge <br />Permit is enclosed in Appendix 2.05.3(4) -3. <br />Pit dewatering will be primarily a seasonal occurrence. The dewatering process will be a <br />sporadic, operation - controlled occurrence depending on various factors which may <br />include the location of the pit inflows, the location of standing water in the pit, or the <br />location within the pit of the overburden and coal removal operations. When pit <br />dewatering is required, the anticipated dewatering rate will be in the range of one to two <br />cubic feet per second or less. Direct pit pumping into Pond NHN -001 or NHN -002 is <br />planned for the mining south of Meehan Draw and into Pond NHN -003 for the mining <br />north of Meehan Draw. Actual water flow velocity going into ponds will be controlled with <br />adequate energy dissipaters (i.e., rock riprap, geotextiles, metal or concrete energy <br />dissipator boxes, etc.) or discharged onto non - erodible bedrock material. This will <br />minimize erosion of the pond banks. <br />Pit dewatering will have an insignificant impact on the ponds. Pit dewatering will be <br />sporadic versus continuous. The flow rate of one to two cubic feet per second or less <br />compared to the designed 10 -year, 24 -hour peak inflow rate the ponds were designed for <br />is relatively insignificant. In addition, pit water high in suspended solids will be allowed to <br />set for a period of time so the solids are allowed to settle out of the water and will remain <br />in the active pit area. Only after the pit water is clear, will it be pumped from the pit into <br />the ponds. Further more, all discharge from the ponds will be in accordance with <br />applicable discharge permits. <br />Monitoring for rills and gullies on the pond and other reclaimed slopes will be carried out <br />on a periodic basis; the monitoring being geared to those periods after spring snow melt <br />and during required quarterly pond inspections. <br />Occurrence of excessive rills and gullies will result in implementation of the following plan. <br />One of, or a combination of, the following options and corrective methods will be <br />employed: <br />If it is determined that the topography of the regraded area is such that drainage <br />is concentrated in a particular area, then this area will be improved to accept the <br />runoff. In areas where no natural armoring is present, the drainage bottom or <br />channel will be reshaped, if needed. The channel bottom will be seeded, covered <br />with erosion matting and seeded, or rip- rapped. The method used will, <br />Section 2.05.3(4) Page 5 November 2011 <br />
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