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• It is anticipated that the full extent of <br /> impacts on sage grouse will be assessed in the course <br /> on the on-going study, which entails the use of radio- <br /> telemetered birds (T. Schoenberg, misc. unpubl. reports). <br /> Meanwhile, for the purposes of this application, <br /> it is appropriate to summarize existing data and to <br /> provide a generalized statement of sage grouse habitat <br /> requirements and probable impacts. <br /> Studies of sage grouse in North Park have been <br /> reported by Rogers (1964) and Beck (1977). Summaries <br /> of the sage grouse literature have been provided by <br /> Johnsgard (1973) and Braun et al. (1977). <br /> Studies have found that sage grouse require a <br /> diversity of habitat types falling within or adjacent <br /> to ecosystems where sagebrush is a conspicuous feature. <br /> Braun et al. (1977) divided seasonal requirements into <br /> 1) leks, 2) nesting areas, 3) brooding areas, and <br />• 4) wintering sites. These are discussed briefly: <br /> Leks tend to consist of openings within the <br /> sagebrush community - areas with low stratum vegetation. <br /> Reported sites include grassy areas, roads, sagebrush <br /> eradication areas, prairie dog towns, and mine spoils. <br /> Braun (pers. comm.) reported that leks appear to have <br /> only one characteristic in common - "visibility". <br /> Wallestad and Schladweiler (1974) believed that <br /> the breeding complex embraced an area extending 2.4 km <br /> from the lek. Braun et al. (1977) considered the <br /> breeding complex as an area within 3 km of a lek. <br /> In the course of current studies in the area <br /> (T. Schoenberg, unpubl.), seven leks have been located, <br /> with a peak male attendance on respective Leks ranging <br /> from 0 - 144 in 1980. Perdiz lek, south of the lease <br /> area, was located in 1978, and had a peak male attendance <br /> of 16 in 1979 and 8 in 1980. Radiotelemetry has shown <br /> an interchange of males between leks. <br />• <br />-7- <br />