Osprey - Pandion haliaetus
FWP Conservation Tier
Ospreys are dark brown above and white below, with a barred tail. The head is white with a prominent brown eye stripe extending from the eye to the shoulders. Females and immature birds have brown streaking on the breast. Immature ospreys have light feather edges on the tops of their wings, giving them a speckled look. Ospreys have long, narrow wings, which are bent at the wrist when soaring. The underside of the wing often appears two-toned, with white along the leading edge of it (except for dark wrist patches), and brown-barred flight feathers. They have a loud whistled call. Ospreys range in length from 21 to 24 inches, and have a wingspan of 54 to 72 inches. A large diurnal raptor with long narrow wings, dark brown upperparts, white underparts, a white head with a prominent dark eye streak, and dark wrist patches (visible in flight) on the underside of the wings; immatures have pale buff edging on the dark feathers of the upper surface; females are more likely than males to have a necklace of dark streaking; average length 56 to 64 cm, wingspan 147 to 183 cm.
Bald Eagles are much larger and hold their wings straight out when soaring. Eagles have dark brown bellies and wings, in contrast to the white belly and barred wings of the Osprey. Differs from other hawks in having all of the following characteristics: white belly, dark wrist patches, and a white head with a prominent dark eye streak. other hawks do not habitually plunge feet-first into water to obtain prey.
Summary of Observations Submitted for Montana
Number of Observations:
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Map Help and Descriptions
(direct evidence "B")
(indirect evidence "b")
No evidence of Breeding
(regular observations "W")
(at least one obs. "w")
(Records associated with a range of dates are excluded from time charts)
Osprey depart by October for wintering areas in Central and South America. Bozeman area migration: April 20 to May 1 and September 15 to 30 (Skaar 1969). Migrates to CA, TX, FL or farther south.
Ospreys nest mainly near large lakes, reservoirs, and rivers in Montana. On upper Missouri, nest tree height variable but always as tall or taller than other trees. Presence of a flat, stable surface for nesting more important than tree species (Grover 1983).
Ecological Systems Associated with this Species
- Details on Creation and Suggested Uses and Limitations
How Associations Were Made
We associated the use and habitat quality (high, medium, or low) of each of the 82 ecological systems mapped in Montana for
vertebrate animal species that regularly breed, overwinter, or migrate through the state by:
- Using personal observations and reviewing literature that summarize the breeding, overwintering, or migratory habitat requirements of each species (Dobkin 1992, Hart et al. 1998, Hutto and Young 1999, Maxell 2000, Foresman 2001, Adams 2003, and Werner et al. 2004);
- Evaluating structural characteristics and distribution of each ecological system relative to the species’ range and habitat requirements;
- Examining the observation records for each species in the state-wide point database associated with each ecological system;
- Calculating the percentage of observations associated with each ecological system relative to the percent of Montana covered by each ecological system to get a measure of “observations versus availability of habitat”.
Species that breed in Montana were only evaluated for breeding habitat use, species that only overwinter in Montana were only evaluated for overwintering habitat use, and species that only migrate through Montana were only evaluated for migratory habitat use.
In general, species were associated as using an ecological system if structural characteristics of used habitat documented in the literature were present in the ecological system or large numbers of point observations were associated with the ecological system.
However, species were not associated with an ecological system if there was no support in the literature for use of structural characteristics in an ecological system, even if
point observations were associated with that system.
High, medium, and low habitat quality was assigned based on the degree to which the structural characteristics of an ecological system matched the preferred structural habitat characteristics for each species in the literature.
The percentage of observations associated with each ecological system relative to the percent of Montana covered by each ecological system was also used to guide assignments of habitat quality.
If you have any questions or comments on species associations with ecological systems, please contact Bryce Maxell at email@example.com
or (406) 444-3655.
Suggested Uses and Limitations
Species associations with ecological systems should be used to generate potential lists of species that may occupy broader landscapes for the purposes of landscape-level planning.
These potential lists of species should not be used in place of documented occurrences of species (this information can be requested at: http://mtnhp.org/requests/default.asp
) or systematic surveys for species and evaluations of habitat at a local site level by trained biologists.
Users of this information should be aware that the land cover data used to generate species associations is based on imagery from the late 1990s and early 2000s and was only intended to be used at broader landscape scales.
Land cover mapping accuracy is particularly problematic when the systems occur as small patches or where the land cover types have been altered over the past decade.
Thus, particular caution should be used when using the associations in assessments of smaller areas (e.g., evaluations of public land survey sections).
Finally, although a species may be associated with a particular ecological system within its known geographic range, portions of that ecological system may occur outside of the species’ known geographic range.
- Adams, R.A. 2003. Bats of the Rocky Mountain West; natural history, ecology, and conservation. Boulder, CO: University Press of Colorado. 289 p.
- Dobkin, D. S. 1992. Neotropical migrant land birds in the Northern Rockies and Great Plains. USDA Forest Service, Northern Region. Publication No. R1-93-34. Missoula, MT.
- Foresman, K.R. 2001. The wild mammals of Montana. Special Publication No. 12. Lawrence, KS: The American Society of Mammalogists. 278 p.
- Hart, M.M., W.A. Williams, P.C. Thornton, K.P. McLaughlin, C.M. Tobalske, B.A. Maxell, D.P. Hendricks, C.R. Peterson, and R.L. Redmond. 1998. Montana atlas of terrestrial vertebrates. Montana Cooperative Wildlife Research Unit, University of Montana, Missoula, MT. 1302 p.
- Hutto, R.L. and J.S. Young. 1999. Habitat relationships of landbirds in the Northern Region, USDA Forest Service, Rocky Mountain Research Station RMRS-GTR-32. 72 p.
- Maxell, B.A. 2000. Management of Montana’s amphibians: a review of factors that may present a risk to population viability and accounts on the identification, distribution, taxonomy, habitat use, natural history, and the status and conservation of individual species. Report to U.S. Forest Service Region 1. Missoula, MT: Wildlife Biology Program, University of Montana. 161 p.
- Werner, J.K., B.A. Maxell, P. Hendricks, and D. Flath. 2004. Amphibians and reptiles of Montana. Missoula, MT: Mountain Press Publishing Company. 262 p.
- Commonly Associated with these Ecological Systems
Forest and Woodland Systems
Open Water / Wetland and Riparian Systems
- Occasionally Associated with these Ecological Systems
Forest and Woodland Systems
Nearly all of their diet consists of fish, primarily rough fish such as suckers. On upper Missouri, catastomids most common prey, with salmonids and cyprinids eaten in similar quantities. Perch also eaten, but relative frequency not calculated (Grover 1983).
Upper Missouri nesting density = 0.03 occupied/km free flowing river, 0.54 occupied/km impounded river (Grover 1983). Becoming rare in Fortine area. Considered common 100 years ago in Gallatin valley; uncommon today (Skaar 1969).
Ospreys build their large nests on trees, power poles, docks, and other man-made structures. Ospreys prefer to build their nest at the top of dead, broken-topped trees, unlike eagles, which usually build nests in live trees below the tree canopy. Ospreys often build "frustration" nests if their first nest fails, although they rarely lay eggs a second time. Ospreys arrive in Montana in March and April, and lay one to four eggs in April or May. The young leave the nest in July and August, when about two months old. Upper Missouri average clutch size is 2.71; two-thirds of pre-fledglings killed were blown out. Successful nests = 52% of total occupied. Brood size of successful nests = 2.16. No eggs layed in 21.7% of occupied nests (Grover 1983). Nest dates April to July.
- Additional ReferencesLegend: View WorldCat Record View Online Publication
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- [PRESI] Powder River Eagle Studies Incorporated. 1998b. Spring Creek Mine 1997 wildlife monitoring studies. Powder River Eagle Studies Incorporated. Gillete, WY.
- Alt, K.L. 1980. Ecology of the breeding bald eagle and osprey in the Grand Teton-Yellowstone Parks complex. MS thesis, Montana State Univ., Bozeman.
- American Ornithologists' Union. 1998. Check-list of North American birds. 7th edition. American Ornithologists' Union, Washington, D.C. 829 pp.
- Bird, D. M., editor. 1983. Biology and management of bald eagles and ospreys. MacDonald. 325 pp.
- Decker Coal Company., 1991, Decker Coal Company West Pit Permit. Vol. 3. 26.4.304(10-11), 305, 306, and 307. Updated Rules Rewrite, July 1, 1991.
- Dobkin, D. S. 1992. Neotropical migrant landbirds in the Northern Rockies and Great Plains. U.S.D.A. For. Serv. N. Region Publ. R1-93-34. Missoula, Mont.
- Ehrlich, P., D. Dobkin, and D. Wheye. 1988. The Birder’s Handbook, A Field Guide to the Natural History of North American Birds. Simon and Schuster Inc. New York. 785 pp.
- Evans, D. L. 1982. Status reports on twelve raptors. U.S. Department of the Interior, Fish and Wildlife Service, Special Scientific Report No. 238. 68 pp.
- Ewins, P.J. 1997. Osprey (Pandion haliaetus) populations in forested areas of North America: changes, their causes and management recommendations. J. Raptor Res. 31(2): 138-150.
- Fjell, Alan K., 1986, Peabody Coal Company Big Sky Mine, Rosebud County, MT. Wildlife monitoring report: 1985 field season. March 1986.
- Flath, D. L. 1972. Canada goose-osprey interactions. Auk 89:446-447.
- Grover, K. E. 1983. Ecology of the osprey on the upper Missouri River, Montana. M.S. thesis. Montana State Univ., Bozeman. 79 pp.
- Grover, K.E., 1984. Nesting distribution and reproduction of ospreys along the upper Missouri river, Montana. Wilson Bull. 96:496-498.
- Johnsgard, P. A. 1986. Birds of the Rocky Mountains with particular reference to national parks in the Northern Rocky Mountain region. Colorado Associated University Press, Boulder. xi + 504 pp.
- Klaver, R. W., J. M. Smith, J. J. Claar, B. L. Betts, and L. C. Peterson. 1982. Osprey surveys in the Flathead Valley, Montana 1977 to 1980. The Murrelet 63:40-45.
- Land & Water Consulting, Inc., Missoula, MT., 2002, Montana Dept. of Transportation Wetland Mitigation Monitoring Report, Year 2001: Creston Site, Creston, Montana. Proj. No. 130091.007. July 2002. In 2001 Wetland Mitigation Monitoring Reports, Vol. I.
- Land & Water Consulting, Inc., Missoula, MT., 2002, Montana Dept. of Transportation Wetland Mitigation Monitoring Report, Year 2002: Batavia, Kalispell, Montana. Proj. No. 130091.006. February 2003. In 2002 Wetland Mitigation Monitoring Reports, Vol. I.
- Land & Water Consulting, Inc., Missoula, MT., 2002, Montana Dept. of Transportation Wetland Mitigation Monitoring Report, Year 2002: Cow Coulee, Townsend, Montana. Proj. No. 130091.013. February 2003. In 2002 Wetland Mitigation Monitoring Reports, Vol. I.
- Land & Water Consulting, Inc., Missoula, MT., 2002, Montana Dept. of Transportation Wetland Mitigation Monitoring Report, Year 2002: Hoskins Landing, Dixon, Montana. Proj. No. 130091.038. February 2003. In 2002 Wetland Mitigation Monitoring Reports, Vol. I.
- Lenard, S., J. Carlson, J. Ellis, C. Jones, and C. Tilly. 2003. P. D. Skaar's Montana Bird Distribution, 6th Edition. Montana Audubon: Helena, MT, 144 pp.
- Lockhart, J. Michael, 1976, Effects of coal extraction and related development on wildlife populations. Annual progress report; Calendar year 1976. In Decker Coal Company West Pit Permit. Vol. 3. 26.4.304(10-11), 305, 306, and 307. Updated Rules Rewrite, July 1, 1991. Appendix F.
- Lockhart, J. Michael, and Terrence P. McEneaney, 1978, Effects of coal extraction and related development on wildlife populations. Annual progress report; Calendar year 1978. In Decker Coal Company West Pit Permit. Vol. 3. 26.4.304(10-11), 305, 306, and 307. Updated Rules Rewrite, July 1, 1991. Appendix F.
- MacCarter, D.L. 1972a. Reproductive performance and population trends of Ospreys at Flathead Lake, Montana. M.S. Thesis. Humbolt State College, CA. 80 pp.
- MacCarter, D.L. and D.S. MacCarter. 1979. Ten-year nesting status of Osperys at Flathead Lake, Montana. The Murrelet 60: 42-49.
- MacCarter, D.S. 1972b. Food habits of Ospreys at Flathead Lake, Montana. M.S. Thesis. Humbolt State College, CA. 80 pp.
- Mace, R.D., D. Casey and K. Dubois. 1987. Effects of water level fluctuations on productivity and distribution of Ospreys and Bald Eagles in the northern Flathead Valley. Montana Fish, Wildl. and Parks, for Montana Power Company, Butte. 90 pp.
- Mullen, P. D. 1985. Reproductive ecology of osprey (Pandion haliaetus) in the Bitterroot Valley of western Montana. MS Thesis, Univ. of Montana, Missoula. 59 pp.
- Poole, A. F. 1989. Ospreys: A natural and unnatural history. The Press Syndicate of the University of Cambridge, N.Y. 246 pp.
- Poole, Alan F., Rob O. Bierregaard, and Mark S. Martell. 2002. Osprey (Pandion haliaetus). Species Account Number 683. The Birds of North America Online (A. Poole, Ed.). Ithaca, NY: Cornell Laboratory of Ornithology; Retrieved 3/25/2008 from The Birds of North America Online database
- Postupalsky, S. and J.P. Kleiman. 1965. Osprey preys on turtle. Wilson Bulletin 77(4): 401-402.
- Powder River Eagle Studies, Inc., Gillette, WY., 1999, Spring Creek Mine 1998 Wildlife Monitoring. March 1999.
- Powder River Eagle Studies, Inc., Gillette, WY., 2000, Spring Creek Mine 1999 Wildlife Monitoring. March 2000.
- Roy F. Weston, Inc., Bozeman, MT., and Western Technology and Engineering, Inc., Helena, MT., 1989, Stillwater PGM Resources East Boulder Project Addendum F: Supplemental Biological Studies. Final Report. December 1989.
- Swenson, J. E. 1975. Ecology of the bald eagle and osprey in Yellowstone National Park. Thesis. Bozeman, Montana: Montana State University. 146 p.
- Thomas, J. W. (ed). 1979. Wildlife habitats in managed forests: the Blue Mountains of Oregon and Washington. Agriculture Handbook 553, USDA, Forest Service, Wildlife Management Institute, Washington, DC. 512 pp.
- U.S. Forest Service. 1991. Forest and rangeland birds of the United States: Natural history and habitat use. U.S. Department of Agriculture, Forest Service Agricultural Handbook 688. 625 pages.
- Waage, Bruce C., compiler., 1985, Western Energy Company Rosebud Mine, Rosebud County, Montana: Annual Wildlife Monitoring Report, 1984 Field Season. October 1985.
- Waage, Bruce C., compiler., 1986, Western Energy Company Rosebud Mine, Rosebud County, Montana: Annual Wildlife Monitoring Report, 1985 Field Season. December 1986.
- Western EcoTech, Helena, MT., 1999, Wetland delineation report for the Haskins Landing Proposed Wetland Mitigation Area. MWFE? June 2, 1999.
- Western Energy Co., Colstrip, MT., 1981, Western Energy Company Rosebud Mine, Colstrip, Montana: Annual Wildlife Report, 1981.
- Zarn, M. 1974. Habitat management series for unique or endangered species. Rpt. No. 12. Osprey (PANDION HALIAETUS CAROLINENSIS). Bur. Land Mgmt. Tech. Note 254.
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