Peregrine Falcon - Falco peregrinus
State Rank Reason (see State Rank above)
Impacts from the pesticide DDT in the mid 20th century caused catastrophic declines in abundance of this species across its range. A ban on this pesticide and subsequent conservation actions have recovered populations and resulted in delisting and removal of protections extended under the Endangered Species Act. In Montana the species had recolonized much of its historic range and continues to increase in abundance. This has resulted in its removal from the State species of Concern list in 2022.
- Details on Status Ranking and Review
Peregrine Falcon (Falco peregrinus) Conservation Status Review
Review Date = 12/22/2011
ScoreC - 250-1,000 individuals
CommentThe Montana Peregrine Institute documented 94 active Peregrine nest sites in 2011 which likely indicates a populaiton of between 250-1,000 individuals.
ScoreG - 200,000-2,500,000 km squared (about 80,000-1,000,000 square miles)
Comment380,531 square kilometers based on Natural Heritage Program range maps that appear on the Montana Field Guide
Area of Occupancy
ScoreU - Unknown
ScoreE - Relatively Stable (±25% change)
CommentAlthough species underwent drastic declines due to pesticides in the 1950s through 1970s, they have recovered to within +/- 25% of historic population sizes.
ScoreF - Increasing. Increase of >10% in population, range, area occupied, and/or number or condition of occurrences
CommentThe trend in Breeding Bird Survey (BBS) data is of very low credibility in Montana. Rangewide BBS shows a 64% increase per year. Raptor survey routes show 150% positive increase per year since 1976, but raptor survey route protocols may be inadiquate or marginal for detection of this species. Ralph Rogers report shows increasing trends with 14 active territories in 1994-1996 to 69 active territories between 2006-2008. In 2011, Jay Sumner from the Montana Peregrine Institute documented 94 active nesting sites.
ScoreF - Widespread, low-severity threat. Threat is of low severity but affects (or would affect) most or a significant portion of the population or area.
CommentNo major threat identified, but nest competition, falconry and nest disturbance may represent threats.
SeverityLow - Low but nontrivial reduction of species population or reversible degradation or reduction of habitat in area affected, with recovery expected in 10-50 years.
CommentSpecies has shown ability to recover relatively rapidly when pesticides were removed as a threat.
ScopeModerate - 20-60% of total population or area affected
CommentPotentially impact 20-60% of range/population.
ImmediacyLow - Threat is likely to be operational within 5-20 years.
CommentNo major operational threats identified
ScoreB - Moderately Vulnerable. Species exhibits moderate age of maturity, frequency of reproduction, and/or fecundity such that populations generally tend to recover from decreases in abundance over a period of several years (on the order of 5-20 years or 2-5 generations); or species has moderate dispersal capability such that extirpated populations generally become reestablished through natural recolonization (unaided by humans).
CommentModerately Vulnerable. Species exhibits moderate age of maturity, frequency of reproduction, and/or fecundity such that populations generally tend to recover from decreases in abundance within 5-20 years or 2-5 generations. Species has good dispersal capabilities such that extirpated populations generally become reestablished through natural recolonization.
ScoreB - Narrow. Specialist. Specific habitat(s) or other abiotic and/or biotic factors (see above) are used or required by the Element, but these key requirements are common and within the generalized range of the species within the area of interest.
CommentNarrow Specialist. Species is dependent on cliff habitat for nesting and these are relatively uncommon on the landscape. Other than that they are generalist forager for ducks, pigeons, and Galliformes.
Raw Conservation Status Score
3.5 – 0.5 (population size) + 0.0 (geographic distribution) + 0.25 (short-term trend) + 0.0 (threats)
The Peregrine Falcon has long pointed wings, a dark crown and nape, and a dark wedge extending below the eye. The forehead is pale in immature birds, which are mainly brownish above rather than black or gray as in adults. Arctic birds are relatively pale, and the Peregrine Falcons of the northwest coast of North America are very dark, compared to the intermediate coloration of the subspecies (anatum
) that once ranged across North America. They average 41 to 51 cm long and 91 to 112 cm in wingspan.
For a comprehensive review of the conservation status, habitat use, and ecology of this and other Montana bird species, please see Marks et al. 2016, Birds of Montana.
Smaller and less stocky in appearance than Gyrfalcons. Juvenile Peregrine Falcons are similar in size to Prairie Falcons, but are darker in color and have a heavy dark wedge on the side of the face.
Western Hemisphere Range
Observations in Montana Natural Heritage Program Database
Number of Observations:
(Click on the following maps and charts to see full sized version)
Map Help and Descriptions
SUMMER (Feb 16 - Dec 14)
Direct Evidence of Breeding
Indirect Evidence of Breeding
No Evidence of Breeding
WINTER (Dec 15 - Feb 15)
Not Regularly Observed
(Observations spanning multiple months or years are excluded from time charts)
Peregrine Falcons arrive in northern breeding areas late April to early May; departure begins late August-early September. In the Bozeman area, observations in the 1950's and 1960's suggested migration periods around May 5 and September 15 (Skaar 1969).
Nests typically are situated on ledges of vertical cliffs, often with a sheltering overhang. Ideal locations include undisturbed areas with a wide view, near water, and close to plentiful prey. Substitute man-made sites can include tall buildings, bridges, rock quarries, and raised platforms.
In fall in the Bozeman area, birds have been seen following flocks of shore birds at the lakes (Skaar 1969).
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 (common or occasional) 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 2012, 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 observation 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 listed as associated with 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 listed as 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.
Common versus occasional association with an ecological system was assigned based on the degree to which the structural characteristics of an ecological system matched the preferred structural habitat characteristics for each species as represented in scientific 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 assignment of common versus occasional association.
If you have any questions or comments on species associations with ecological systems, please contact the Montana Natural Heritage Program's Senior Zoologist.
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: mtnhp.org/requests
) 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. 2012. Mammals of Montana. Second edition. Mountain Press Publishing, Missoula, Montana. 429 pp.
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- 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
Sparse and Barren Systems
Wetland and Riparian Systems
- Occasionally Associated with these Ecological Systems
Forest and Woodland Systems
Shrubland, Steppe and Savanna Systems
Peregrine Falcons feed primarily on birds (medium-size passerines up to small waterfowl). They have occasionally been reported to prey on small mammals (e.g., bats, lemmings), lizards, fishes, or insects (by young birds). Prey is pursued from a perch or while soaring. Peregrine Falcons may hunt up to several km from nest sites (Skaggs et al. 1988). In general, much hunting occurs in morning, and to lesser extent toward evening, but may hunt anytime during day. Excess prey is cached, especially during the breeding season.
Great Horned Owl may be a serious nest predator.
Nestlings have been reported in Montana from July 10 to 17 (Johnsgard 1986). The nesting period is estimated to be June and July (Davis 1961).
Clutch size averages 4 at mid-latitudes, and 3 in the far north. Incubation lasts 32 to 35 days, and is done mainly by female (the male brings food). Young birds fledge at 39 to 49 days, and gradually become independent. Brood losses are apparently caused mainly by bad weather, and lost clutches are usually replaced at alternate site.
Peregrine falcons first breed typically at 2 to 3 years of age, and occasionally as yearlings. They usually form a lifelong pair bond.
In some parts of Montana, Peregrine Falcons were considered fairly common in summer during the early 1900's (Skaar 1969). Post-war use of pesticides has been the main cause of the decline of these birds (Skaar personal communication).
- Literature Cited AboveLegend: View Online Publication
- Davis, C.V. 1961. A distributional study of the birds of Montana. Ph.D. Dissertation. Corvallis, OR: Oregon State University. 462 p.
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- Skaar, P.D. 1969. Birds of the Bozeman latilong: a compilation of data concerning the birds which occur between 45 and 46 N. latitude and 111 and 112 W. longitude, with current lists for Idaho, Montana, Wyoming, impinging Montana counties and Yellowstone National Park. Bozeman, MT. 132 p.
- Skaggs, R.W., D.H. Ellis, W.G. Hunt, and T.H. Johnson. 1988. Peregrine falcon. In: Glinski et al., eds. Proceedings of Southwest raptor management symposium and workshop. Natural Wildlife Federation Science and Technical Series Number 11. p. 127-136.
- Additional ReferencesLegend: View Online Publication
Do you know of a citation we're missing?
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