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RULE Z PE _ITS <br />Another topsoil distribution technique that may be used in areas targeting Sagebrush Steppe would be the <br />development of low berms using emplaced topsoil with the aid of equipment such as a road grader (see <br />Figure 2.05 -7). For ease of discussion, such berms could be termed "soil fences ". These berms would act <br />as natural snowfences trapping wind blown snow to aid sagebrush emergence and development. In this <br />circumstance, a designed amount of topsoil (e.g. 9 inches) would be redistributed over a target area, <br />however, berms would be developed utilizing only the topsoil resource. Where upper layers of topsoil <br />have been pushed aside, a depth of remaining topsoil may be in the 2 -4 inch range that should then help to <br />encourage sagebrush emergence while discouraging vigorous grass growth. Where topsoil is bermed, a <br />peak depth up to 30 inches may result. In these thicker topsoil areas, other taxa within the seed mix (or <br />alternate mix) should provide additional competitive advantage. It is critical that berms be constructed on <br />the contour to preclude development of preferential erosion pathways. It is also necessary that berms <br />only be constructed where they will be approximately perpendicular to the prevailing winds, otherwise <br />there is little benefit to be gained. Furthermore, berms would have to exhibit low and rounded shoulders <br />to allow seeding equipment to operate properly. Implementation of techniques such as this must <br />necessarily occur as a result of site - specific opportunity (as opposed to plan) given a variety of factors, <br />not the least of which is availability of equipment and personnel. <br />As indicated on Figure 2.05 -7, the dimensions (in cross - section) would need to be based on the width of <br />seeding equipment to facilitate proper seeding operations, although the widths indicated may be changed <br />in the field, especially given aspect differences. In this regard, sagebrush conducive seed mixes would be <br />applied to the shallow soil areas as well as the uphill- facing side of the berm (west- facing slopes). This is <br />the area that will receive maximum benefit from entrapped snow. The downhill- facing side of the berm <br />would ideally receive the grassland conducive mix owing to the steeper slope (4:1). For easterly aspects, <br />the grassland conducive mix would still need to be applied to the downhill 4:1 slope. As this technique is <br />developed and "proven ", modifications to seed mix placement can and should be made as necessary. <br />This additional level of complexity should not be problematic for maintaining an overall topsoil balance. <br />It will simply add an additional layer of "bookkeeping" (Section 12 of the Annual Report) beyond that <br />which has already occurred at Colowyo over the past three decades. <br />Revegetation Plan <br />Following the retopsoiling of an area, any necessary fertilization, surface preparation, berm <br />development, construction of contour furrows, and seeding of the reclamation will take place. <br />The reclamation seed mixture for areas targeting grassland (grazingland land use and erosion <br />control), as shown in Table 2.05 -7, Reclamation Seed Mixture, contains sufficient diversity for <br />ecological stability. The seed mixture contains a variety of grasses, forbs and shrub species well <br />adapted to the soil and moisture conditions found at Colowyo. The diverse seed mixture is capable <br />of self - selection for each reclaimed micro - habitat encountered in the reclaimed areas. The diverse <br />seed mixture is required to ensure quick erosion control for the first few years of reclamation as well <br />as obtaining the desired post- mining vegetative community with the same seasonal variety and <br />lifeform of the pre -mined area. <br />The species and seeding rates indicated on this "grassland" mix resulted from in -depth analyses of <br />past mixes and the resulting emergence and dominance within revegetated areas. A total of eleven <br />different measurement events on Colowyo reclamation coupled with a performance evaluation for <br />each taxon in the 2002 mix resulted in development of the mix indicated on Table 2.05 -7 as well as <br />Table 2.05 -9. Examples of changes resulting from this analysis include: elimination of streambank <br />Rule 2 Permits 2.05 -28 Revision Date: 10/23/12 <br />Revision No.: RN -06 <br />