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site=s ability to adapt to these changes. One must keep in mind that as productivity and cover <br />increase diversity usually decreases. Therefore, a balance needs to be established between the <br />criteria which provides optimum value for the postmining land use and that which provides adequate <br />ecological resiliency. <br />When selecting appropriate diversity criteria one must considerthe nature of the site and the ability of <br />species and life forms to colonize from adjacent sites. Greater emphasis should be placed on diversity <br />for large unbroken tracts of land than for smaller sites with extensive influence from undisturbed native <br />vegetation. Therefore, diversity standards should be greater on large concentrated disturbances from <br />strip mined lands than for smaller diffuse disturbances from linear features such as light use roads. <br />The most appropriate approach to developing revegetation criteria is the combined use of reference <br />areas and data on site potentials. Some of the information relating to the vegetative communities are <br />available from studies of reference areas. The remaining data have been collected from the mine <br />permit site as a whole. Reference areas have also been established in areas where disturbance has <br />been less prevalent. Complimentary information has been produced from regional data. Table V-14 <br />compares baseline samples of various plant communities to the NRCS (p.k.a. SCS) Range Site <br />descriptions. <br />V.E.2 Revegetation Success Criteria Historic, current, and probable future land use all involve the <br />use of the permit area as sheep and wildlife habitat winter range. As a result, revegetated sites must <br />not only meet those specifications set forth by the DMG, but must compliment the values of <br />surrounding lands. The application of the latter category of criteria is particularly important on sites that <br />receive the greatest utilization by sheep during the winter and early spring. These are exposed sites <br />on south and west-facing slopes, and ridge and hill tops. <br />Fencing of reference areas 110, 140 and 150 was necessary to prevent continued depletion of the <br />herb layer as a result of sheep winter use and to improve the existing range condition. However, <br />Section 4.15.7(3)(d) of the regulations requires the reference areas to be managed in a manner that is <br />in accordance with the approved postmining land use. Therefore, before sampling for comparative <br />purposes, the reference areas must be made available for grazing. <br />Semi-arid sites characterized by harsh and limiting environmental conditions have been successfully <br />reclaimed in this region using the techniques around which this plan has been constructed. <br />Understanding the special treatments and well-coordinated maintenance programs is important. The <br />site-specific plans and evaluations provided for by this plan and the presence of a resident reclamation <br />specialist is integral to the success of the plan. Criteria used to evaluate revegetation success for <br />purposes of final bond release are as follows: (Table V-15 summarizes these criteria). <br />(a) Vegetative cover of the revegetated area must be at least 90% of the vegetative cover <br />ExhibitE-Reclamation Plan Rio Blanco Special Use Permit#81.1 September2000 <br />V-33 <br />