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• the disturbance area .will be taken <br /> entirely out of production at any given time, the <br /> remainder either in an undisturbed, ~re+mining condition, <br /> or in a stage of reclamation, <br /> Using regional range exclosures as a guide, within <br /> one year following establishment of the study area, there <br /> is expected to be a significant increase in plant vigor <br /> and cover, probably reaching a peak in 3 - 4 years. <br /> Thereafter, improvement in the plant community will be <br /> measured in terms of a change in composition, with <br /> more palatable grasses, forbs and shrubs increasing in <br /> percentage of biomass. <br /> Conditions within the sanctuary are expected to <br /> benefit livestock in the long term, since the carrying <br /> capacity of the site is expected to increase substantially. <br /> When returned to grazing in the post-mining phase, forage <br /> conditions, therefore weight gains, should more than <br />. compensate for short-term reductions in stocking rates. <br /> This method is deemed preferable to other management <br /> options, e.g. fertilization, because of distinct <br /> advantages to the fauna in dry years. L. Carpenter <br /> (in litt.) reported that plans on an experimental area <br /> northwest of the lease area failed to respond to <br /> fertilization following the dry winter/spring of 1977. <br /> His findings correspond with those of others who have <br /> attempted fertilization in arid areas and have found <br /> that an absence of moisture can negate the anticipated <br /> results (Nagy and Haufler 1980). <br /> It has been shown that the lease area is primarily <br /> a spring-summer use area for featured species. Therefore <br /> it is in dry years that benefits from livestock exclusion <br /> are expected to be the greatest, since a forage/cover <br /> reserve will be maintained, and increased litter will <br /> tend to retain moisture and delay the site dessication <br />• characteristic of heavy livestock use. <br />-15- <br />