We examined nocturnal roosting and diurnal perching habitat used by nonbreeding bald eagles (Haliaeetus leucocephalus) in North Carolina during 1986 and 1987. Eagles used roost areas that were less dense, had less canopy cover, were closer to forest edges, and had larger trees than randomly selected areas, and they used trees that were larger than random trees for roosting and perching. Suitable perch trees were the most important attribute of perching habitat. Eagles used loblolly pines (Pinus taeda) and trees with leafless crowns, probably because these crowns were most accessible for perching. Eagles perched in the bottom of tree crowns during summer, but they perched in tree tops during fall and winter. Eagle did not use perches that were different from forest stand characteristics within 20 m of perch trees, forest cover types in 1-ha blocks surrounding perches, or habitat disturbances. Roosting habitat should receive primary management emphasis because of its apparent low occurrence in central North Carolina. Perch trees were plentiful, but long-term management is desirable. J. WILDL. MANAGE. 54(2):223-234 Bald eagles are listed as endangered or threatened throughout much of North America (50CFR ? 17.11), but populations have stabilized or increased in recent years (Nickerson 1989, Bohall Wood et al. In Press). Shooting, trapping, electrocution, poisoning by pesticides and lead shot, and habitat loss to human encroachment through cutting of nest trees, perch trees, and roost sites remain a serious concern for management of eagles (Stalmaster 1976, Stalmaster and Newman 1979, Hansen et al. 1980, Nash et al. 1980). Since summer 1985, relatively large numbers (>30) of bald eagles have been observed on B. Everett Jordan and Falls lakes in central North Carolina, apparently representing a substantial increase in the state bald eagle population (W. Adams, U.S. Army Corps Eng., pers. commun.). The Jordan and Falls lakes populations primarily represent a transient summer assemblage of mostly immature, nonbreeding eagles. Little has been published about communal summer roosts and postnesting summer habitat use of bald eagles. Research emphasis has been on communal winter roosting and nesting habitat use (e.g., McEwan and Hirth 1979, Hansen et al. 1980, Anthony et al. 1982, Keister and Anthony 1983). Identification of summer postnesting habitat requirements is necessary for management of bald eagles during part of the nonbreeding period. Our objectives were to describe the vegetative characteristics of roost and perch sites in relation to overall habitat characteristics and to develop management guides for eagle habitat on reservoirs in North Carolina. Funding was provided by the U.S. Army Corps of Engineers, Wilmington District. M. T. Gaudette and A. K. DeLong provided field assistance. A. R. Davidson, K. K. Stout, and G. N. Hirsh assisted with data input. Thanks to J. Rich and C. Adams of the North Carolina Wildlife Resources Commission, and M. Tippett of AeroServices, Inc. for pilot services. L. G. Jervis provided information on forestry practices at the Mason Point roost and allowed access to North Carolina State University property. R. C. Duckson, S. Brown, and B. Adams provided information and cooperation throughout the study. 1 Present address: Box 2434, Cordova, AK 99574. 2 Present address: 778 Palmer Avenue, Falmouth, MA 02540. 3 Present address: Wildlife Division, Department of Natural Resources, 2455 N. Williams Lake R ad, Pontiac, MI 48054.
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