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Because of the high erosional velocities anticipated for the <br />post-mining configuration, it would be advantageous to construct a <br />permanent structure in the reach of the stream that would experience <br />the greatest erosion. For this reason, a stipulation was attached to <br />the initial five-year permit (Stipulation No. 16) which required the <br />permittee to submit a plan to the Division for "the installation of a <br />structure that would demonstrably dissipate the energy of flow in the <br />channel such that erosion of the channel will not occur." The <br />permittee submitted a plan proposing the use of 3.5 ft. diameter or <br />larger stones as rip-rap in the channel to provide adequate energy <br />dissipation and preclude erosional velocity. This plan was <br />subsequently approved by the Division, thereby satisfying the <br />requirements of Stipulation No. 16. <br />Upon termination of mining, or following completion of the rail spur to <br />the central facilities area, Salt Creek Mining Company proposes to <br />return the Loma loadout facility to the land use which existed prior to <br />the coal loadout operation (storage and rail loading facility). This <br />is specified in Article 32 of the lease agreement between the applicant <br />and the D&RGW Railroad Company (see Exhibit C-VIII, Appendix C, Volume <br />IV of the application). All structures will be removed. Coal will be <br />removed form the site and deposited at the McClane Mine or Munger <br />Canyon Mine site to be covered during reclamation. The surface will be <br />graded to a smooth condition. <br />IX. Revegetation - Rule 2.04.10 <br />Baseline vegetation information for the Munger Canyon Mine can be found <br />in Section 4.8 of Volume I, Sections 3.1.1 and 4.5 of Volume VI, and on <br />Figure 4.5-1s of Volume VII of the permit application. The Division <br />has reviewed this portion of the application and determined that the <br />information is adequate. All previous concerns relating to the <br />baseline vegetation information section of the initial permanent <br />program permit application have been resolved. <br />In the initial sampling program undertaken, inadequate numbers of <br />samples were taken to provide the current desired levels of confidence <br />(p greater than or equal to .80 for non-herbaceous communities, <br />d = .10, alpha = 2) for the productivity of the greaswood shrubland, <br />shadscale shrubland, and juniper woodland vegetation types. <br />The Salt Creek Mining Company Munger Canyon Mine contains the same <br />vegetative communities (with the exception of the Big sagebrush <br />community) as, and is located contiguously to, the Salt Creek Mining <br />Company McClane Canyon Mine. Abiotic factors affecting the occurrence <br />of vegetation communities are similar. For this reason, data from the <br />two mine sites for productivity of the above communities were compared <br />to determine if the communities of McClane and Munger Canyon were from <br />differing populations. It was verified statistically that the McClane <br />and Munger respective communities were not significantly different in <br />terms of vegetative productivity within the bounds of each vegetative <br />community. Data from the McClane and Munger sites were combined <br />(within communities between sites), and it was determined that the <br />combined data met confidence level requirements. <br />-38- <br />