Cassin's Finch - Haemorhous cassinii
State Rank Reason (see State Rank above)
Data show recent short-term declines in population for this species
- Details on Status Ranking and Review
Cassin's Finch (Haemorhous cassinii) Conservation Status Review
Review Date = 12/20/2011
ScoreU - Unknown
ScoreG - 200,000-2,500,000 km squared (about 80,000-1,000,000 square miles)
Comment234,081 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)
CommentPonderosa Pine habitats seem relatively stable (+/- 25%) since European arrival.
ScoreC - Rapidly Declining. Decline of 30-50% in population, range, area occupied, and/or number or condition of occurrences
CommentIn Montana BBS data is of moderate credibility and is -0.5% per year or -5% per decade. Similar or greater rates of decline are noted for all surrounding states and provinces. Across the Northern Rockies, BBS data is of high credibility and is a -3.9% per year or a 33% decline per decade. Score reflects high credibility data for entire Northern Rockies.
ScoreE - Localized substantial threat. Threat is moderate to severe for a small but significant proportion of the population or area.
CommentFire, climate change, forest disease, and timber harvest probably represent the greatest threats to the species.
SeverityModerate - Major reduction of species population or long-term degradation or reduction of habitat in Montana, requiring 50-100 years for recovery.
CommentLoss of forests would require a significant time for recovery.
ScopeLow - 5-20% of total population or area affected
CommentLikely not lose up to 20% of forests in the next couple decades.
ImmediacyHigh - Threat is operational (happening now) or imminent (within a year).
CommentOngoing and climate change could increase threat.
ScoreC - Not Intrinsically Vulnerable. Species matures quickly, reproduces frequently, and/or has high fecundity such that populations recover quickly (< 5 years or 2 generations) from decreases in abundance; or species has high dispersal capability such that extirpated populations soon become reestablished through natural recolonization (unaided by humans).
CommentNot Intrinsically Vulnerable. Species matures quickly, reproduces frequently, and/or has a high fecundity such that populations recover quickly (< 5 years or 2 generations) from decreases in abundance. Species has good dispersal capabilities such that extirpated populations generally become reestablished through natural recolonization.
ScoreC - Moderate. Generalist. Broad-scale or diverse (general) habitat(s) or other abiotic and/or biotic factors are used or required by the species but some key requirements are scarce in the generalized range of the species within the area of interest.
CommentModerate generalist. Broadly distributed in drier conifer forests.
Raw Conservation Status Score
3.5 + 0.0 (geographic distribution) + 0.0 (environmental specificity) - 0.5 (short-term trend) + 0.0 (threats) = 3.0
Cassin's Finch is the largest of the North American Carpodacus
finches (includes Purple Finch and House Finch); length is 14.5-15.5 cm (5.7-6.1 inches). Adults are sexually dimorphic in plumate traits. Adult males have rose-red coloration on the head throat and upper breast, the crown is bright pinkish-red contrasting with the paler nape and back; rump and upper tail coverts are dull rose-pink and streaked with brown. The lower breast and belly appear generally whitish, the undertail coverts with fine brown streaks. Females have an overall brownsih plumage; the head has supercillium and submoustacial regions with fine brown streaks, back and rump dusky and streaked with brown, the throat, breast and flanks whitish with crisp brown streaks. Juneniles and immatures resemble females.
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.
Male Cassin's Finch has fine streaking on the undertail coverts and flanks, in contrast to pure white of the Purple Finch. In females and immature males, breast and flanks more cleanly white and more finely streaked in Cassin’s Finch than in Purple Finch. Larger and more chunky than the House Finch. Red on male House Finch is usually brighter and oranger, not rose-red. Male Cassin's Finch is much less streaked on the lower breast and belly than male House Finch; female Cassin's Finch with a noticable supercilliary stripe lacking in female House Finches, and the breast streaking more distinct and less diffuse. Cassin's Finch the only of the three Carpodacus finches routinely encountered higher in the mountains.
Western Hemisphere Range
Cassin’s Finches occur year-round in the mountains west of the Great Plains and east of the Cascades from southeastern British Columbia and southwestern Alberta south to southern California, northern Arizona, and northern New Mexico; an isolated population occurs in Baja California Norte. They winter as far south as the interior mountains of central Mexico, well south of the known breeding range (Howell and Webb 1995, Hahn 1996).
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)
Cassin’s Finches are short-distance elevational or latitudinal migrants in some parts of their range, the movements somewhat irregular and possibly dependent on food supply (Hahn 1996). In Montana, flocks have been reported to arrive from early March to April and depart from September to October (Hand 1969, Skaar 1969, Weydemeyer 1973). Flocks usually contain fewer than a dozen birds, but 30 were seen at Missoula on 20 February 1949 (Hand 1953).
Cassin’s Finches occur in every major forest type and timber-harvest regime in Montana, including riparian cottonwood, but are especially common in ponderosa pine and postfire forests; they occur less often in lodgepole pine, sagebrush, and grassland (Manuwal 1983, Hutto and Young 1999). They often visit bird feeders and occasionally venture into alpine terrain (Johnson 1966, Pattie and Verbeek 1966).
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
Wetland and Riparian Systems
Foods include seeds, especially of grasses, composites, conifers, alders, and birches, as well as buds, leaves, and invertebrates (including spruce budworm larvae).
A male Cassin's Finch’s breeding territory is centered around a female rather than on a specific piece of terrain, in part because populations contain many more males than females, so competition for females is intense (Samson 1976). During winter, Cassin’s Finches form dominance hierarchies, similar to other species that gather in flocks after the breeding season. However, females tend to dominate males, a trait shared by House Finches and Purple Finches but few other passerine species (Samson 1977). Why females are dominant over males is not clear, but it may relate to a nomadic life style that results in a lack of site fidelity to specific winter areas, lack of stable flock membership, and a male-biased sex ratio. Nevertheless, survival of females in winter is enhanced by preferential access to food and roosting sites. Cassin’s Finches were one of three finch species that regularly appeared in flocks during summer on the grounds of the University of Montana’s Biological Station on Flathead Lake. Outdoor experiments conducted by Bennetts and Hutto (1985) demonstrated that the finches were attracted to bare soils containing increased concentrations of sodium and calcium salts from building construction, but it wasn’t clear why the finches had an extra-dietary need for these salts. BBS data from 1980-2007 suggest a nonsignificant decline in numbers of 7.9% per year in Montana and a significant decline of 3.9% per year survey-wide. Cassin’s Finches were recorded every winter on Montana CBCs from 1979-80 to 2009-10 (mean = 92 per winter), with a high of 203 birds on nine counts in 2000-01 (0.16 birds per party hour) and a low of six birds on two counts in the winter of 1980-81 (0.01 birds per party hour). The largest single counts were 144 birds at Hamilton on 30 December 1988 and 105 at Libby on 18 December 1993.
Generally a single-brooded species with 4 to 5 eggs per clutch. Incubation period is 12 to 14 days. Young are able to fly about 14 days after hatching. Breeding has been poorly documented in Montana but generally occurs from late May through July (Skaar 1969, Weydemeyer 1975, Montana Bird Distribution Committee 2012). A nest found under construction on 29 May 1968 at Lubrecht Experimental Forest was the first reported for the state; it was later abandoned (Manuwal 1968). A nest was found under construction on 20 June 1996 at Bear Canyon in the Pryor Mountains, and two nests were reported on 11 July 1993 between Miles City and Mizpah. The nest is an open cup of twigs, grasses, and rootlets placed near the tip of a tree branch. Montana nests have been reported 9 m above the ground in Douglas-fir and 2 m above ground in big sagebrush (Manuwal 1968; P. Hendricks, personal obsservation).
No management activities specific to Cassin's Finch are currently occuring in Montana. Cassin’s Finches are one of the more abundant birds in early postfire conifer forests, where their numbers can increase significantly regardless of fire severity; attraction to these sites may result from increased seed resources. They also are attracted to harvested forests and stands where postfire salvage logging has occurred, although these habitats may serve as ecological traps (Hutto 1995, Hutto and Young 1999, Smucker et al. 2005). Given their occurrence in burned and harvested forests, the population declines that have been identified recently are difficult to explain.
Threats or Limiting Factors
No significant threats have been identified that account for apparent population declines, unless recent extent of severe wildland fire in conifer forests has produced postfire ecological traps for Cassin's Finches. There is no evidence that the incidence of Mycoplasmal Conjuntivitis or West Nile Virus among Cassin's Finches is as extreme as in some populations of House Finches in the western U.S.
- Literature Cited AboveLegend: View Online Publication
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- Samson, F.B. 1977. Social dominance in winter flocks of Cassin's finch. The Wilson Bulletin 89(1): 57-66.
- 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.
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- Additional ReferencesLegend: View Online Publication
Do you know of a citation we're missing?
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