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Permanent sealing of holes, wells or other exposed underground openings not completed to <br />aquifers will be sealed by replacing cuttings or other suitable media in the hole. A suitable plug <br />will be placed ten feet below the ground surface to support a cement plug or other media to <br />within three feet of the ground surface. Permanent sealing of holes, wells, etc. completed in <br />aquifers will be sealed using cement or other suitable sealant. The sealant will be placed in the <br />hole from the bottom to within ten feet of the surface. Surface plugs used to complete the <br />permanent sealing of holes, wells, etc. will be selected and used only if DRMS gives prior <br />approval. All associated surface sites will be reclaimed following the cessation of mining. NHN <br />will submit to the DRMS a proof of compliance report containing pertinent information on <br />permanent sealing of any hole, well, etc. within 60 days of completion of such activities. <br />Ground Water Ouantity The backfilling and grading of spoil materials is accomplished by <br />dozers and trucks (see Section 2.05.4(2)(c), Backfilling and Grading). As described in Section <br />2.04.7 Hydrologic Description, the NHN permit area is hydrologically isolated from adjacent <br />areas of Dakota coal strata by stream incision. Further, the hydrologic regime at NHN is the sole <br />product of seasonal irrigation by way of the Colorado Cooperative Company's 2nd Park Lateral <br />irrigation ditch. This ditch was completed in about 1905 and delivers approximately 19.2 cubic <br />feet per second (cfs) of water to the 2nd Park area. About 10.8 cfs enters the permit area in the 2nd <br />Park Lateral (see Map 2.04.7-1 of Section 2.04.7) where about 2.5 cfs is used on the permit area <br />and the remaining water goes to water shareholders located downstream. The 2nd Park Lateral is <br />to be diverted into a high density poly ethylene (HDPE) pipeline around the mining area. After <br />the mine has advanced far enough north and overburden backfilling and top soil spreading has <br />progressed past the original ditch location, the HDPE pipeline will be rerouted to approximately <br />the original ditch location. Infiltration and percolation of irrigation water from the banks and bed <br />of the 2nd Park ditch will for the most part be eliminated. This will also eliminate the primary <br />source of recharge to the overburden, coal and under -burden zones. The structure of the strata <br />(see Map 2.04.6-2 in Section 2.04.6) will prevent any major saturation of the backfilled <br />overburden material as any percolating excessive irrigation water or water from intense <br />precipitation events will drain to the south along the contact of backfill material and the <br />relatively tight under -burden. In addition to backfilling methods, top soiling and reclamation <br />plans outlined in Section 2.05.4(2)(d), Overburden and Topsoil Handling, and Section <br />2.05.4(2)(e), Revegetation, will enhance the potential for establishing reclaimed areas that <br />exhibit similar infiltration rates to pre -mining conditions. Seeding and mulching of redistributed <br />topsoil will augment moisture retention and infiltration rates of the reclaimed areas. Mechanical <br />manipulation of the regraded spoil and topsoil (chisel plowing, disking and ripping) will further <br />aid the percolation of soil moisture downward. <br />Any accumulated ground water inflow to the pit will be removed by pumping the water into a <br />sediment pond (NHN-001 through NHN-003). Design criteria for such sediment ponds are <br />presented in Section 2.05.3(4), Ponds, Impoundments, Other Treatment Facilities and <br />Section 2.05.6(3)(b)(v) Page 2 December 2016 (RN -01) <br />