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channel area (Figure 4). According to land survey maps, channel widths in 1965 were 21 to 73 <br />percent of the 1865 widths recorded. Because of controlled releases from reservoirs upstream, <br />there is less variability in over-all river flows than there were historically. The Pathfinder <br />Reservoir, completed in 1909, was the first major impoundment on the North Platte, followed by <br />Guernsey (completed in 1927), Alcova (1938), Seminole (1939), McConaughy (1941) and Glendo <br />(1957). These reservoirs dropped peak flows on the North Platte by 86% (Currier, Lingle, and <br />Walker 1985: 96). This change has resulted in a net loss of water-filled channel and an associated <br />increase in vegetated river-banks. This, in turn, has meant loss of roosting, nesting and feeding <br />habitat that comes with loss of ineanders and grasslands-wetlands near the main river channel. <br />With 80% of the North American crane flock dependent on the central Platte, any further <br />loss of habitat would be most threatening. Reduction of available habitat for all the species of <br />birds that traditionally made use of the Platte basin creates two forms of hardship: 1) competition <br />for the limited food supply; and 2) crowded conditions exacerbates disease transmission. Avian <br />cholera and tuberculosis brought in by snow geese poses a threat to the health of many birds and <br />most particularly cranes. Crowding contributes to disease transmission. As wetlands have been <br />drained and woodlands grown up along the banks, crane habitat has shrunk from hundreds of <br />miles of prime river habitat to less than 70 miles in the Kersey and Grand Island area. Here cranes <br />and other bird crowd dangerously close in the few good habitat reaches that remain (Currier, <br />Lingle, and Walker 1985: 18). <br />? Caloric requirements for migration used to be met by starchy tubers from a variety of <br />? aquatic plants, worms, snails, snail shells and insects in the floodplain. Now, within 8 miles of <br />• the river, 96% of the cranes' diet is found in waste corn. The remaining 4% is the critical <br />invertebrate component which provides protein and calcium for egg production. What little <br />? habitat is left for spring and autumn stopovers is as important as the suinmer and winter <br />? destinations themselves and not only for cranes, but also for snow geese, mergansers, mallards, <br />? teal, pintail ducks, and bald eagles. <br />The interior least tern is a small bird approximately nine inches in body and twenty inches <br />in wingspan. In recent decades, this species has been found on only a fraction of its former habitat <br />that, early in the twentieth century, had stretched from Texas to Montana and &om the front range <br />of eastern Colorado and New Mexico to Indiana. The species was listed as threatened in 1985 <br />and recent estimates place its population at about 4,800 W.S. Fish & Wildlife Service 1990). <br />Interior least terns nest in colonies where there is little or no vegetation, in shallow inconspicuous <br />depressions in open sandy areas. In Nebraska, they are found on sandbars of the Missouri, the <br />Loup, the Nebraska, and the Platte rivers, on the beaches of Lake McConaughy, and on shores of <br />sandpits created by human extraction of gravel. <br />Piping Plovers are similar to least terns in that they nest in the same areas and compete for <br />the same resources. This species was listed under the Endangered Species Act as threatened in <br />1985. A 1991 census estimated its population in both Canada and the U.S. to be about 2440 <br />breeding pairs. The population is distributed from southeastern Alberta to northwestern <br />Minnesota and along prairie rivers and reservoirs to southeastern Colorado. About 10% were <br />estimated to breed primarily along rivers and 90% nested around lakes and ponds (U.S. Fish & <br />12