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Appendices 6-3 and 6-4 of Tab 6. Analytical data associated with Wolf Creek <br />and Sage Creek overburden and underburden is presented in Tables 6-7A <br />through 6-7D, and Appendix 6-3 of Tab 6. Summary tables and text <br />delineating unsuitable zones and addressing mitigative measures for unsuitable <br />zones within Wadge, Wolf Creek and Sage Creek overburden and <br />underburden are included in Appendix 6-5. <br />Wadge Overburden/Underburden Assessment <br />In 4% or less of the samples analyzed, pH, acid/base potential, boron, manganese, <br />cadmium and zinc exceeded suspect levels. In general, the Division concurs with <br />the applicant's determination that normal mixing of overburden will mitigate the <br />toxic effects of these materials. D.J. Dollhopf in "Selective Placement of Strip <br />Mine Overburden in Montana" (Chapter 5, Summary Report, 1981) suggests that <br />if the volume of toxic material is less than 15% of the total volume of material to <br />be replaced, dilution of the toxic material can be successful. <br />Two primary concerns identified by the Division as a part of the PR-1 review were <br />in regard to potentially acid forming materials associated with the Lennox coal <br />seam and excessive clay contents associated with shale strata overlying the Lennox. <br />The Division requested Seneca to prepare a spoil sampling plan and mitigation <br />plan for areas where the Lennox would be spoiled, and for areas where the Lennox <br />would potentially be exposed by highwall reduction. Amore detailed mitigation <br />plan for areas of excessive clay content was also requested. <br />Seneca submitted an acceptable sampling plan to be employed in areas potentially <br />affected by Lennox spoil or outcrop within the original permit area. The same <br />sampling plan will be applied to all regraded spoil areas and graded fmal <br />highwalls in the south extension mining block. The plan calls for samples to be <br />taken on 500 foot centers within the designated area, and analyzed for clay content, <br />pH, and acid-base potential. Mitigation will include additional sampling to define <br />the area of concern, deep ripping of areas of unsuitable clay content and <br />amendment or burial of acid forming material with a minimum of four feet of <br />suitable material as cover. <br />Nitrate-nitrogen levels were excessive in 14 % of the overburden core samples taken <br />at the Seneca II-W Mine. The locations of the holes which exhibited elevated <br />levels were distant from one another. Furthermore, the stratigraphic location of the <br />elevated nitrate-nitrogen samples are not correlative. Due to the vertical and <br />horizontal distances between locations containing elevated nitrate-nitrogen levels, <br />percolating ground water will not be adversely affected. The dilutional effects of a <br />predicted spoils aquifer should buffer the concentration of nitrate as nitrogen by the <br />time the aquifer discharges to the surface system. <br />Seneca II-W Findings Document 27 November 17, 2004 <br />Permit Revision No. 4 <br />