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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I' <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />"'!"1~'" ~~ <br />'J - ..' .) . <br />SEenO.THREE <br /> <br />WhOOping Grane <br /> <br />available from the BOR GIS database. The only available information on water width and depth <br />profiles is 85 transects at 16 sites, completed in the 19805. This existing stream profile data may <br />no longer accurately represent the individual bridge' segments in the late 19905. <br /> <br />3.4.2 Wet Meadow Habitat <br /> <br />During migration, whooping cranes forage in sma1l-grain croplands, upland grasslands, and <br />wetland habitat areas where they have been observed feeding on frogs, fish, crayfish, insects, <br />plant tubers, and waste grains (FWS 1981). A major part of the whooping crane's energy <br />requirements during migration across the Great Plains probably comes from waste agricultural <br />crops. Although the proportions of plant and animal food in the diet are not known, whooping <br />cranes, like sandhill cranes, require animal t1llItter to satisfy their nutritional needs. In general, <br />the foraging strategies of whooping cranes are more closely associated with wetland feeding <br />habitats than are those of sandhill cranes (Johnsgard 1996). <br /> <br />Foods used by migrating whooping cranes and that are available in wetlands and bottomland <br />grasslands along the Platte River include small fish, snakes, frogs, frog egg m,,<'leS, crayfish, <br />grasshoppers, crickets, and other insects (FWS 1981, 1994; Currier et al. 1985; Ballinger 1980; <br />Cocbnarand Jenson 1981; Ratcliffe 1981; Davis and Vohs 1993). Many of these organisms <br />depend on aquatic moistUre regimes, or seasonally moist or saturated soils for all or part of their <br />life cycle. <br /> <br />3.4.3 Platte River Habitat Decline <br /> <br />The area of open channel and of adjacent wet meadow habitats in the study area have greatly <br />decreased since construction of the Kingsley Dam. Existing habitats and habitat decline are <br />described in Section 2. <br /> <br />The mid-continent population of sandhill cranes principally rely on three habitat types during <br />their annual stopover along the Platte River. These are relatively broad channels for roosting and <br />cropland and meadows for feeding. The Platte River near Overton was at one time one of the <br />major spring staging areas for sandhill cranes, but deterioration of habitats has affected sandhill <br />crane distribution (Krapu et al. 1982). Degraded habitat conditions between North Platte and the <br />J-2 Return does not suppon crane use. Sandhill cranes that use the Platte for physiological <br />conditioning and pair bonding prior to their northward migration have also abandoned most of <br />the degraded reach of the river from the J-2 Return to Kearney (Faanes and LeValley 1993). <br />Sidle et aL (1993) and Currier et al. (1985) describe trends of sandhill crane distribution and <br />habitat degradation observed along the Platte River. Sidle et al. (1993) attribute sandhill crane <br />roost distribution to juxtaposition of two primary limiting habitats of wet meadows and open <br />channeL Similar observations were reponed by KIapu et al. (1982). <br /> <br />Habitat changes that have affected sandhill crane use of these reaches have affected whooping <br />crane use to an even greater degree. Whooping cranes are more sensitive to. disturbance, and <br />select wider channels for nightly roosting on the Platte River than do sandhill cranes. Whooping <br />cranes rarely use channels less than 500 feet wide and prefer channels 900 feet wide or greater. <br />Though wider channels are highly suitable for sandhill cranes, they often use channels of widths <br /> <br />., a'lIIal!r ~ltClJde <br />,..,....... <br /> <br />08F_._6I2/1~S2~'" 3-9 <br />