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months of disturbance, although natural revegetation typically occurs much sooner due to the limited timeframe and <br />extent of the associated disturbance. Occasionally perforated PVC pipe may be inserted in a completed borehole, <br />and the remainder of the hole backfilled with clean gravel, as a temporary piezometer installation to measure any <br />fluctuation in water - levels. This type of piezometer installation is normally very temporary (typically used less <br />than a month) and will not impact groundwater due to the shallow depth and use of natural cuttings as backfill. <br />Any piezometer installations are reclaimed by either pulling the PVC pipe and placing additional fill, or plugging <br />the PVC pipe in -place using bagged bentonite grout, then capping the installation with a minimum 1.5 -foot surface <br />plug of natural clays or cement with a site marker. <br />Loadout Area Drainage Modifications (MR14 -284) - The drainage and sediment controls for this area were <br />approved under an SAE, as referenced in the Permit text, however, given the configuration and type and level of <br />activities in this area, the existing drainage and sediment controls were found to be marginally adequate. The site <br />conditions were reviewed and evaluated, and the following changes, as shown on Figure EX49DD -F1, were <br />implemented to modify and upgrade the site drainage controls in order to be effective under all reasonably <br />anticipated conditions. <br />The pad area on the north side of the rail spur was reduced in size by removing the accumulation of coally material, <br />and regrading and reseeding part of this area, leaving only an access road along the north side of the spur. The <br />drainage configuration of the remaining pad was modified by filling a low area and placing a berm to direct all <br />drainage to the collection sump. The sump capacity and function were expanded by constructing a second sump in <br />series, removing accumulated sediment from the existing sump, and rebuilding the rock perimeter filter. The <br />control capacity of the rail spur collection ditch was increased by excavating several sediment traps in the ditch and <br />adding additional rock check dams. As a very limited disturbance area (approximately 1.2 acres) the Loadout area <br />disturbance meets the applicable criteria for a Small Area Exemption, the proposed drainage control measures should <br />be effective in controlling runoff and sedimentation, and construction of full -scale drainage and sediment control <br />structures is neither needed nor justified. <br />(5) Topsoil. A narrative explaining the method of removal and the amount to be removed and the plan for <br />storage of topsoil, subsoil, and other material within the permit area subject to requirements of the topsoil removal <br />performance standards of 4.06.2. This narrative shall specify the depth of material to be salvaged from all disturbed <br />areas based on the soil information required by 2.04.9 and shall specify the volume of each type of material to be <br />salvaged. A map of any proposed storage structures shall accompany the narrative. The maps shall be prepared <br />according to the requirements of 2.10. <br />RESPONSE <br />See response to 2.05.4, Reclamation Plan, below for details concerning the Foidel Creek Mine. TC does not propose to <br />disturb any additional land within the Fish Creek Tipple permit area. The Fish Creek Tipple and adjoining haulroad <br />were constructed prior to the promulgation of regulations mandating topsoil salvage and storage. Thus, the best <br />plant growth medium available is a mixture of spoil and soil materials which will be substituted for topsoil. This <br />situation is further discussed within the Fish Creek Tipple/Loadout Appendix, pages 2.04 -36 through 2.04 -38 and <br />pages 2.05 -37 through 2.05 -38 of Volume VIII. <br />Eastern Minine District Dewatering Facility - The Eastern Mining District Dewatering Facility will require <br />salvaging and stockpiling approximately 13,360 CY of topsoil from the access road and the facility site. During <br />upgrading of the road, approximately 3,600 CY of topsoil will be windrowed to the side of the road. The topsoil <br />along the length of the road is approximately 30 inches deep. The facility site will require salvaging and <br />stockpiling approximately 8,300 CY of topsoil. The topsoil from the site area is approximately 30 inches deep. A <br />test pit will be dug to verify the topsoil depth obtained from previous soil mapping work. The stockpiled topsoil, <br />which is located within the pad area, will be stabilized with the topsoil stockpile stabilizing seed mixture. <br />Additionally, approximately 6,295 CY of topsoil will be salvaged from the treatment pond site. This site has been <br />relocated closer to the road to facilitate delivery of chemicals. <br />Bleeder Fan - The bleeder fan facility will require salvaging and stockpiling approximately 4,700 CY of topsoil <br />from the access road and the facility site. During the upgrading of the road, approximately 2,800 CY of topsoil will <br />be windrowed to the side of the road and left in place. The 1,200 CY that will be salvaged from the road extension <br />will be placed in the stockpile that will be established on the fan pad. In addition to the topsoil stockpiled from the <br />road extension, approximately 740 CY will be salvaged and stockpiled from the pad. The soil resources <br />MR14 -284 2.05 -84.10 12/04/14 <br />