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PERMFILE52059
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PERMFILE52059
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Last modified
8/24/2016 10:55:59 PM
Creation date
11/20/2007 3:11:20 PM
Metadata
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Template:
DRMS Permit Index
Permit No
C1981010
IBM Index Class Name
Permit File
Doc Date
12/11/2001
Doc Name
Analytical Comparison Between Regraded Spoils & Adjacent Overburden Drill Holes
Section_Exhibit Name
APPENDIX I Section 4.0
Media Type
D
Archive
No
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ANALYTICAL COMPARISON BETWEEN REGRADED SPOILS AND ADJACENT <br />OVERBURDEN DRILL HOLES AT TRAPPER MINE, 1985-87. <br />Introduction <br />Soil and overburden analysis is necessary in the premining phase of the coal <br />mining operation in order to predict what characteristics the spoil material <br />will exhibit after mining. Experience in overburden sampling at Trapper Mine <br />over the last ten years of operation has identified strata which have shown to <br />be indicators of potential chemical and physical problems. High clay content <br />overburden tend to be associated with high ESP or SAR values. Also, over- <br />burden up to 50 feet above the lowest mineable coal seams generally appear at <br />the surface to become part of the subsoil for supporting vegetation. The <br />replacement of these lower lithological strata on the spoil surface which may <br />have higher-than-desired mineral content may be of little concern from a <br />reclamation standpoint. The mixing of regrade surfaces during spoil regrading <br />is of primary importance to ensure adequate subsoil composition. <br />In order to focus on what Trapper considered a potential spoil problem, <br />Trapper Mine proposed and CMLRD agreed to abandon its current program for <br />sampling in-place overburden and provide yearly analysis and reports on <br />regraded spoils. The annual report will demonstrate that a surface spoil <br />layer exists with acceptable physical and chemical properties. With the addi- <br />tion of suitable topsoil, these regraded spoils provide a suitable medium to <br />promote plant growth and successful reclamation. This report is a composite <br />of three years of spoil data collection and will provide baseline information <br />for future spoil sampling reports. <br />4.1 Methods <br />Composite samples were taken on approximately 50-ft to 100-ft centers for <br />each mapping unit. Mapping units in 1985-1987 were determined by visual <br />and textural difference with no size limitation, however a minimum <br />sampling density of approximately one sample per five acres of reclaim <br />area will be performed in the future. Each sample was a composite from <br />the top four inches of spoil material. Future sampling will be composite <br />samples from one foot into the spoil material. The samples were analyzed <br />Eor pH, EC, CaC03, O.M., N03-N, P, K, Zn, Fe, Mn, Cu, Se, Ca, Mg, Na, <br />SAR, % Saturation, texture, Hg, F, Total S, and acid-base potential. If <br />a large negative acid-base potential was found, then additional analysis <br />to include pyritic Sulfur and SOq-S was run for that sample. The final <br />mapping units were then transferred to the spoil history map, I-1. Each <br />delineation on this map was identified as to year sampled, texture, and <br />lab analysis number. <br />Overburden sampling in the east panel was run concurrently with the <br />exploratory drilling program. In order [o keep the samples free from <br />drilling contamination and as representative of their natural conditions <br />as possible, the following procedures were followed. <br />1) Continuous cores if possible were taken down to the last seam of <br />mineable coal and including the lithologic strata immediately beneath <br />that coal seam. <br />. _~ <br />cont. <br />
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