Flammulated Owl - Psiloscops flammeolus
At 6.75 inches and only 60 grams, Flammulated Owls are one of the smallest owls in North America. Only Elf Owls (Micrathene whitneyi
) are smaller. Other than females being somewhat larger than males, the sexes are extremely similar in appearance. The species has short ear tufts and an incomplete facial disk beginning at the ears and ending at the moustache. The eyes are dark. The wings are longer and more pointed in comparison to other species in the genus. The plumage of Flammulated Owls is gray with dark streaks and crossbars (McCallum 1994a). Also, some rufous coloration is visible, especially near the face and on the shoulders. It is unsure whether a distinct red phase exists.
Flammulated Owls are usually heard more often than seen. The song of the male is described as a low-pitched, short, soft hoot like "poop"
which is repeated every two to three seconds (Sibley 2000). Females are usually higher-pitched, longer in duration, and more quavering (McCallum 1994a).
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.
The dark eyes of Flammulated Owls distinguish them from any other North American owl of similar size. Also, their size and short ear tufts distinguish them from all North American Megascops species. Lastly, the low-pitched, soft, monosyllabic hoots will rule out any other forest owl in North America, except for Long-eared Owls (Asio otus). Flammulated Owls' small size, vocalization, eye color, and head/ear shape in combination are diagnostic.
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)
Flammulated Owls are apparently a neotropical migrant, at least in the northern part of their range, but migration patterns are poorly understood (Winter 1974, McCallum 1994a). No banded owl has been recovered outside the vicinity of the capture site (McCallum 1994b), but plausible evidence of migration is based on prey availability, empirical lack of torpor, long-distance vagrancy, and seasonal timing of observations (McCallum 1994a). Capture evidence from Arizona and New Mexico suggests they migrate at night; capture occurred from mid-April to mid-May in spring and over a longer span from early September to late October in fall (Balda et al. 1975). Winter distribution is south of the U.S. border and in Texas, Arizona, and California.
In North America, spring arrivals mostly occur in late April and early May (McCallum 1994a). In several western U.S. states, they arrive generally in April and depart by the end of October (Voous and Cameron 1989). The species arrives in the breeding areas of central Colorado and Idaho in early May (Reynolds and Linkhart 1987b, Atkinson and Atkinson 1990). In Idaho, compilation of all distributional records showed the earliest date detected was March 30 and the latest was October 17 (Groves et al. 1997). Flammulated Owls are present in British Columbia from late April to late September (Howie 1988, van Woudenberg 1999).
Information on breeding habitat in Montana is limited to one study in the Bitterroot Valley (Wright 2000). In Montana, Flammulated Owls are associated with mature and old-growth xeric Ponderosa Pine/Douglas-fir stands (Holt and Hillis 1987, Wright et al. 1997) and in landscapes with higher proportions of suitable forest and forest with low to moderate canopy closure (Wright et al. 1997). They are absent from warm and humid pine forests and mesic Ponderosa Pine/Douglas-fir (McCallum 1994a, Wright et al. 1997). Information gathered from other studies throughout their range suggest the breeding habitat of Flammulated Owls is montane forest; usually open conifer forests containing pine, with some brush or saplings (typical of the physiognomy of pre-European settlement Ponderosa Pine forests). The species shows a strong preference for Ponderosa Pine (Pinus ponderosa) and Jeffrey Pine (P. jeffreyi) throughout its range (McCallum 1994b). They prefer mature growth with open canopy avoiding dense young stands. Flammulated Owls are found in a cooler, semi-arid climate, with a high abundance of nocturnal arthropod prey and some dense foliage for roosting (McCallum 1994a). Most often they are found on ridges and upper slopes (Bull et al. 1990, Groves et al. 1997).
In British Columbia, Flammulated Owls use dry interior Douglas-fir (Pseudotsuga menziesii) where Ponderosa Pine may be a codominant, but pure Ponderosa Pine is avoided. Also sometimes they are in pure aspen and, locally, in spruce (Picea sp.)/Douglas-fir and Lodgepole Pine (Pinus contorta)/Douglas-fir. They prefer forests dominated by trees more than 100 years old. The highest densities are found in 140 year-old to more than 200 year-old forests; owls were restricted to forests with multi-layered canopies with an abundance of large, well-spaced trees interspersed with grassy openings up to 2 hectares in size, and where cavity-bearing snags were "moderately common" (Howie and Ritcey 1987, van Woudenberg 1999). A study in the Kamloops area testing a habitat model in Douglas-fir/Ponderosa Pine found three variables to be significant predictors for occupied habitat: elevation (between 850 and 1,150 meters), age class (older stands), and canopy closure (40 to 50 percent) (Christie and van Woudenberg 1997).
In Idaho, they are found mostly in mature stands of Ponderosa Pine, Douglas-fir, or mixtures of the two with relatively open canopies (Atkinson and Atkinson 1990), occasionally in stands of pure Douglas-fir or aspen where Ponderosa Pine is absent. Sixty-five percent of detections were on upper slopes or ridges. Tree densities were approximately 500 per hectare and the mean DBH (diameter at breast height) for all trees was 32 centimeters (Groves et al. 1997). One nest cavity, excavated by a Northern Flicker, was in a 6.5 meter tall, 34 cm dbh, Douglas-fir snag (Atkinson and Atkinson 1990). In northeast Oregon, nest trees were located in stands of old-growth Ponderosa Pine or mixed conifers near small clearings (Bull and Anderson 1978). In Colorado, they show strong preference for old-growth Ponderosa Pine and Douglas-fir, using older trees for foraging and singing (Reynolds and Linkhart 1992, Linkhart and Reynolds 1997).
Territories consistently occupied by breeding pairs were those containing the largest portion (more than 75 percent) of old-growth (200 to 400 years), whereas territories occupied by unpaired males and rarely by breeding pairs contained 27 to 68 percent old-growth (Linkhart and Reynolds 1997). Aspen (Populus tremuloides) is often a component of nesting habitat in Colorado and Nevada (Reynolds and Linkhart 1987b, McCallum 1994b). In northern Utah, the species has successfully nested in nest boxes in montane deciduous forests dominated by aspen with some scattered firs (Marti 1997).
Flammulated Owls prefer to forage in yellow pine and/or Douglas-fir, and these forest types apparently support a particular abundance of favored lepidopteron prey (McCallum 1994b). In Oregon, they forage in Ponderosa Pine and Douglas-fir types with low to medium stem density, but show particular preference for forest/grassland ecotones (Goggans 1986, cited in McCallum 1994b). In Colorado, they preferred to forage in old-growth (more than 200 years), which was related both to an abundance of lepidopteron prey and to the open crowns and park-like spacing of trees which allowed greater room to maneuver for the owls (Reynolds et al. 1989). The species may focus foraging in a few "intensive foraging areas" within the home range, averaging 1 hectare per range (Linkhart 1984, cited in McCallum 1994b).
Flammulated Owls roost in dense vegetation and thickets that provide shade and protection from predators. They often roost close to trunks in fir or pine trees, or in cavities (McCallum 1994b, USDA Forest Service 1994). In Oregon, they use mixed coniferous forest rather than pure Ponderosa Pine (Goggans 1986, cited in McCallum 1994a). In Colorado, large Douglas-firs or pines with a spreading form are used (Linkhart 1984, cited in McCallum 1994a). They roost close to nests (20 to 25 meters) during the nestling stage and just before fledging, and farther away before and after (McCallum 1994a). In British Columbia, Flammulated Owls roosted in regenerating thickets of Douglas-fir (Howie and Ritcey 1987). Migration habitat is in wooded and open areas in lowlands and mountains, including riparian areas and breeding habitat (McCallum 1994a).
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.
- 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
Recently Disturbed or Modified
- Occasionally Associated with these Ecological Systems
Forest and Woodland Systems
Recently Disturbed or Modified
Wetland and Riparian Systems
No food habit data exists for Flammulated Owls in Montana. Information gathered from other areas of the species' range indicate Flammulated Owls mainly hunt at night and eat nocturnal arthropods (McCallum 1994a and 1994b). Marshall (1957) reported most hunting activity occurs at dawn and dusk. McCallum (1994a, 1994b) reported Flammulated Owls hunting exclusively at night. They feed on various insects (e.g., moths, beetles, grasshoppers, crickets, caterpillars) (McCallum 1994a, 1994b). Moths (especially Noctuidae and Geometridae) and beetles are especially important (Reynolds and Linkhart 1987b, Marshall 1957). They possibly respond to spruce budworm outbreaks (McCallum 1994b) and may occasionally eat small mammals or birds (Bull 1987, Holt 1996). Foraging tactics include hawk-gleaning, hawking, hover-gleaning, and drop-pouncing and they will also glean insects from trunks and branches (Reynolds and Linkhart 1987, Zeiner et al. 1990, USFS 1994). Flammulated Owls in Oregon and New Mexico mostly foraged along the interface between forest or woodland and grassland (McCallum et al. 1995). In New Mexico, sit-and-wait foraging occurred 3 to 50 meters from nests (McCallum et al. 1995).
No ecological information regarding Flammulated Owls is available for Montana. In general, individual Flammulated Owls occupy the same breeding territory in successive years (Reynolds and Linkhart 1987a) with territory sizes about 5.2 square kilometers. Males show strong territorial fidelity but females may disperse to adjacent territories (dispersal distance averaged 474 meters) (Reynolds and Linkhart 1987a). This species may be semi-colonial (Atkinson and Atkinson 1990, Rodrick and Milner 1991), but this assumption is based solely on patterns of calling males and not on nest locations (Hayward and Verner 1994). Territory size usually remains the same from year to year, even if adjacent territories are unoccupied (McCallum 1994a). Territorial boundaries often occur along ridgetops (Reynolds 1987).
Singing owls move widely within the home range. Male foraging, territorial defense, resting and day-roosting were confined to the home range in a Colorado study with home range sizes apparently influenced by canopy volume and range shape by topography (Linkhart 1984). Nesting home ranges vary from 5.5 to 24.0 hectares, and may diminish in size during the breeding season (McCallum 1994b). Home ranges diminished in Oregon from a mean of 15.9 hectares during incubation to 7.9 hectares during the nestling period, to 3.6 hectares during the fledgling period (Hayward and Verner 1994). In Colorado, territory size averaged 14 hectares with foraging activity concentrated in 1 to 4 areas within the home range (Reynolds and Linkhart 1987a). Both sexes make extra-range movements during the breeding season (Reynolds and Linkhart 1990).
Flammulated Owl density in Oregon, British Columbia, and Colorado was generally fewer than 4 singing males per 40 hectares. Densities of singing males in Idaho averaged 0.41 per 40 hectares (Atkinson and Atkinson 1990), and in Oregon from 0.28 to 0.52 males per 40 hectares (Groves et al. 1997). Nests per 100 hectares averaged 2.9 in New Mexico, 2.1 in Colorado, and 1.4 in Oregon (not significantly different) (McCallum et al. 1995). In New Mexico, nest sites averaged 260 meters from the nearest neighbor (McCallum et al. 1995). Territories remain the same size in successive years and rarely expand when a neighbor is absent (Reynolds and Linkhart 1990). Recorded predators of adults include accipiters and Great Horned Owls (Bubo virginianus). Nest predation by Northern Flying Squirrels (Glaucomys sabrinus) has been documented (McCallum 1994b). Squirrels and other avian cavity nesters compete for nest cavities, and as Flammulated Owls come late to the breeding grounds, these competitors may limit nest site availability.
No information specific to Montana is available, but other studies have found Flammulated Owls have low reproductive rates (McCallum 1994b). Clutch size is two to four (usually two to three) and incubation lasts 21 to 26 nights. In northeast Oregon, incubation ranged from June 8 to July 3; fledging occurred between July 25 and August 16 (Bull and Anderson 1978). Incubation is by females (male brings food). The nestling period is reported as 21 to 23 days. In Colorado, each of 5 broods averaging 2.8 young fledged over a 2-night period; young which fledged on the same night were associated into subgroups which separated on the 3rd night after fledging began; 1 parent attended each subgroup, and they dispersed in opposite directions (Hayward and Verner 1994).
Fledglings are tended by both parents and are independent at about 1 month after fledging. Fledging occurs in July to August. In Idaho, the nest fledged between July 19 to 22 (Atkinson and Atkinson 1990). Brood size most often is two. The maximum recorded longevity in the wild is about 7 to 8 years (Reynolds and Linkhart 1990). The rates of nest success and productivity are generally unknown.
No specific management activities for Flammulated Owls are currently occurring in Montana, however, management for old-growth ponderosa pine habitats is ongoing by a number of land management agencies. Management for the maintenance of this habitat type will be beneficial for Flammulated Owls in Montana.
- Literature Cited AboveLegend: View Online Publication
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- Bull, E. L. and R. G. Anderson. 1978. Notes on flammulated owls in northeastern Oregon. Murrelet 59:26-28.
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- Goggans, R. 1986. Habitat use by flammulated owls in northeastern Oregon. M.S. thesis, Oregon State University, Corvallis. 54 pp.
- Groves, C., T. Frederick, G. Frederick, E. Atkinson, M. Atkinson, J. Shepard and G. Servheen. 1997. Density, distribution, and habitat of flammulated owls in Oregon. Great Basin Naturalist 57:116-123.
- Hayward, GD. and J. Verner. 1994. Flammulated, boreal, and great gray owls in the United States: A technical conservation assessment. Rocky Mountain Forest and Range Experiment Station, Fort Collins, Colorado. USDA Forest Service General Technical Report RM-253.
- Holt, D. W. 1996. On winter records and vertebrate prey in Flammulated Owls. Journal of Raptor Research 30:46-48.
- Holt, D. W., and J. M. Hillis. 1987. Current status and habitat associations of forest owls in western Montana. Pages 281-288 in Biology and conservation of northern forest owls: Symposium proceedings (R. W. Nero, R. J. Clark, R. J. Knapton, and R. H. Hamre, Eds.). U.S. Forest Service General Technical Report RM-142, Fort Collins, Colorado.
- Howie, R.R. 1988. Status report on the flammulated owl, Otus flammeolus, in Canada. Committee on the Status of Endangered Wildlife in Canada. 58 pp.
- Howie, R.R. and R. Ritcey. 1987. Distribution, Habitat Selection and Densities of Flammulated Owls in British Columbia. pp 249-254 In: R.W. Nero, R.J. Clark, R.J. Knapton, and R.H. Hamre, Editors. Biology and Conservation of Northern Forest Owls. USDA For
- Linkhart, B. D. 1984. Range, activity, and habitat use by nesting flammulated owls in a Colorado ponderosa pine forest. M.S. thesis, Colorado State University, Fort Collins, CO.
- Linkhart, B. D. And R. T. Reynolds. 1997. Territories of Flammulated Owls (Otus flammeolus): Is Occupancy a Measure of Habitat Quality? pp 150-154 In: J.R. Duncan, D.H. Johnson, and T.H. Nicholls, Editors. Biology and Conservation of Owls in the No
- Marks, J.S., P. Hendricks, and D. Casey. 2016. Birds of Montana. Arrington, VA. Buteo Books. 659 pages.
- Marshall, J. T. Jr. 1957. Birds of pine-oak woodland in southern Arizona and adjacent Mexico. Pacific Coast Avifauna No. 32. 125 pp.
- Marti, C. 1997. Flammulated Owls (Otus Flammeolus) Breeding in Deciduous Forests. pp 262-266 In: J.R. Duncan, D.H. Johnson, and T.H. Nicholls, Editors. Biology and Conservation of Owls in the Northern Hemisphere. USDA Forest Service General Technic
- McCallum, D. A. 1994. Review of technical knowledge: Flammulated Owls. Pages 14-46 in Flammulated, Boreal, and Great Gray owls in the United States: A technical conservation assessment (G. D. Hayward and J. Verner, Eds.). U.S. Forest Service General Technical Report RM-253, Fort Collins, Colorado.
- McCallum, D. A., F. R. Gehlbach, and S. W. Webb. 1995. Life history and ecology of flammulated owls in a marginal New Mexico population. Wilson Bulletin 107:530-537.
- Reynolds, R. T., R. A. Ryder, and B. D. Linkhart. 1989. Small forest owls. In: National Wildlife Federation. Proceedings of the western raptor management symposium and workshop. National Wildlife Federation Scientific and Technical Series No.12. Washington, D.C. Pp 131-143.
- Reynolds, R.T. and B.D. Linkhart. 1987a. Fidelity to territory and mate in flammulated owls. Pp 234-238 In: R.W. Nero, R.J. Clark, R.J. Knapton, and R.H. Hamre, editors. Biology and conservation of northern forest owls. USDA Forest Service, General Technical Report RM-142.
- Reynolds, R.T. and B.D. Linkhart. 1987b. The nesting biology of flammulated owls in Colorado. Pp 239-248 In: R.W. Nero, R.J. Clark, R.J. Knapton, and R.H. Hamre, editors. Biology and conservation of northern forest owls. USDA Forest Service, General Technical Report RM-142.
- Reynolds, R.T. And B.D. Linkhart. 1992. Flammulated Owls in Ponderosa Pine: Evidence of Preference for Old Growth. pp 166-169 In: M. R. Kaufmann, W. H. Moir and R. L. Bassett, Technical Coordinators. Old Growth Forests in the Southwest and Rocky Mountain
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- Rodrick, E. and R. Milner (eds). 1991. Management recommendations for Washington's priority habitats and species. Washington Department of Wildlife, Olympia. Unpublished Report.
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- Van Woudenberg, A. M. 1999. Status of the flammulated owl (Otus flammeolus) in British Columbia. Working Report No. 96, British Columbia Ministry of Environment, Lands, and Parks, Victoria, B.C. 45 pp.
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- Additional ReferencesLegend: View Online Publication
Do you know of a citation we're missing?
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- Mccallum, D.A. 1994. Flammulated Owl (Otus flammeolus). Species Account Number 093. 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
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- Additional Sources of Information Related to "Birds"