Pygmy Rabbit - Brachylagus idahoensis
The body size of Pygmy Rabbits is smaller than any other North American leporid. The hind legs are very short, and the hind feet comparatively broad and heavily haired. The ears are short, rounded and densely haired inside and out, and are edged with buff. Whiskers are black and white. The tail is small and inconspicuous, and buff on all surfaces. The upper parts are buffy-gray, the nape and anterior surfaces of the legs are cinnamon-buff; by winter pelage becomes worn and appears silver-gray. On the skull the supraorbital processes are relatively long both anteriorly and posteriorly; auditory bullae are inflated. Molariform teeth are relatively small, with the first upper one possessing but a single reentrant angle. There are 28 teeth in the skull (dental formula: I 2/1, C 0/0, P 3/2, M 3/3). Body measurements are: total length 232 to 305 millimeters, tail 15 to 24 millimeters, hind foot 66 to 76 millimeters, adult mass 246 to 458 grams (Green and Flinders 1980a, Verts and Carraway 1998, Foresman 2012).
Pygmy Rabbits have an entirely gray-brown tail, lacking the white underside of the tail that is present in all cottontail (Sylvilagus) species. This and the small body size (ears less than 50 millimeters, hind foot less than 75 millimeters) help eliminate confusion with adult and juvenile cottontails as well as jack rabbits and hares. The presence of a nonfused interparietal bone on the skull distinguish Pygmy Rabbits from the jack rabbits and hares (Lepus); long anterior supraorbital processes and the first upper cheek tooth with only one reentrant angle on the anterior surface distinguish the skull of the Pygmy Rabbit from the cottontails (Green and Flinders 1980a, Foresman 2001, 2012).
Summary of Observations Submitted for Montana
Number of Observations:
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Map Help and Descriptions
(Records associated with a range of dates are excluded from time charts)
Little information is available on movements. At one site, Pygmy Rabbits had to cross about 500 meters of relatively open terrain to occupy a coulee-bottom stringer of dense sagebrush (Rauscher 1997). Information from other portions of its range suggest that Pygmy Rabbits are non-migratory with daily winter movements usually less than 100 meters (averaged 30 meters in Wyoming). A radio-collared individual moved 3.5 kilometers between burrow systems in February, and evidence indicated other individuals moved at least 2.0 kilometers (Katzer and Parker 1998).
Occupied habitats in Montana include shrub-grasslands on alluvial fans, floodplains, plateaus, high mountain valleys, and mountain slopes, where suitable sagebrush cover and soils for burrowing are available. Some occupied sites may support a relatively sparse cover of sagebrush and shallow soils, but these usually support patches of dense sagebrush and deeper soils. Big sagebrush was the dominant shrub at all occupied sites, averaging 21.3 to 22.6% coverage; bare ground averaged 33% and forbs 5.8%. Average height of sagebrush in occupied sites was 0.4 meter (Rauscher 1997). In southwestern Wyoming, Pygmy Rabbits selectively used dense and structurally diverse stands of sagebrush that accumulated a relatively large amount of snow; the subnivean environment provided access to a relatively constant supply of food and protection from predators and thermal extremes (Katzner and Parker 1997).
Pygmy Rabbits dig burrows extending to a depth of 1 meter and they form chambers as part of the burrow system. Burrows have been excavated but no nests have been found and the location of nests is not known (Green and Flinders 1980a).
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
Shrubland, Steppe and Savanna Systems
- Occasionally Associated with these Ecological Systems
Shrubland, Steppe and Savanna Systems
Big sagebrush (Artemisia tridentata) is the primary food source (up to 99% of the winter diet), but grasses and forbs are eaten in mid- to late summer, and can comprise up to 40% of the diet during that season. They sometimes climb into tops of sagebrush to feed (Green and Flinders 1980a, 1980b, Lyman 1991, Verts and Carraway 1998). Diet in Montana has not been reported, although samples have been collected for analysis (Rauscher 1997); browsing on big sagebrush near burrows was noted, however.
Pygmy Rabbits may be active at any time of day, but mostly early in the morning and late in the afternoon. They make extensive use of burrows, largely of their own construction. Burrows have several entrances (typically 4 or 5 but as few as 2 and up to 10), and usually are located at the base of sagebrush plants. Use of burrows is variable but greatest with juveniles. Individuals occupy more than one burrow and share several (Green and Flinders 1980a). One Montana female was captured at four different burrows, and at one burrow two adult females, one adult male, and one juvenile were captured (Rauscher 1997). During the day, they use forms under vegetation in a manner similar to other rabbits and hares (Green and Flinders 1980a). In southwestern Wyoming, winter home range size was 548 to 18,464 square meters (mean 2568 square meters and 10,204 square meters in two different years) (Katzner and Parker 1997).
Annual mortality can be quite high, but has not been quantified satisfactorily. Predators include weasels (Mustela spp.), Coyote, Red Fox, Bobcat, Northern Harrier, Long-eared Owl, and Great Horned Owl (Green and Flinders 1980a, Verts and Carraway 1998). Predators reported in Montana include Coyote and Long-tailed Weasel (Rauscher 1997).
Population density fluctuates dramatically among years. Densities have been estimated as low as 0.7 to 1.4 per hectare in Utah and up to 45.0 per hectare in ideal habitat in Idaho (Green and Flinders 1980a, Verts and Carraway 1998). The density estimate at one Montana site was 3.0 per hectare (Rauscher 1997).
Few data are available on Pygmy Rabbit reproductive biology. Females become reproductively active sometime prior to May, by which time females are pregnant or have already given birth. Gestation probably lasts about 27 to 30 days. Two litters per year may be produced; size of two litters from near Bannack was 5 and 7 fetuses. Lactation continues into August. Adult males become scrotal prior to May and remain so into July. Juveniles were captured between May 8 and August 8 (Rauscher 1997). Data from other sources in the species' range indicate the breeding period extends from late winter to early summer. Testis size in males increased from December to April; pregnant females are encountered from February to May. Average litter size was 6 young, the range being 4 to 8 (Ingles 1965, Green and Flinders 1980a, Verts and Carraway 1998). This species may give birth underground.
No special management activities have been developed or implemented in Montana specifically for Pygmy Rabbits. The loss of habitat from conversion to cropland and pasture is probably not great in southwestern Montana. Burning and other methods of sagebrush removal, however, have been used in past and recent years to improve rangeland for livestock. Such activity will make the landscape unsuitable for Pygmy Rabbits. This species is found where grazing occurs, so long as sagebrush cover is maintained, but overgrazing could result in loss of forbs and grasses that are summer foods to Pygmy Rabbits, and livestock could damage sagebrush structure by trampling plants and thinning the shrub canopy. Dense stands of sagebrush along streams, fence lines, and borrow ditches are probably essential avenues for dispersal of pygmy rabbits. If sagebrush is removed, it may isolate or eliminate Pygmy Rabbits in some areas, unless it is done in such a way as to maintain a mosaic of patches of relatively large size isolated only by narrow expanses of unsuitable habitat. All areas within the range of the Pygmy Rabbit in Montana where sagebrush removal is planned should first be evaluated for impact to this species (Rauscher 1997).
- Literature Cited AboveLegend: View WorldCat Record View Online Publication
- Foresman, K. R. 2001. Key to the mammals of Montana. University of Montana Bookstore, Missoula, Montana. 92 p.
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- Green, J. S. and J. T. Flinders. 1980. Brachylagus idahoensis. Mammalian Species 125:1-4.
- Green, J.S. and J.T. Flinders. 1980. Habitat and dietary relationships of the pygmy rabbit. Journal of Range Management 33 (2): 136-142.
- Ingles, L. G. 1965. Mammals of the Pacific states. Stanford University Press, Stanford, California. 506 p.
- Katzner, T. E. and K. L. Parker. 1997. Vegetative characteristics and size of home ranges used by pygmy rabbits (Brachylagus idahoensis) during winter. Journal of Mammalogy 78:1063-1072.
- Katzner, T. E. and K. L. Parker. 1998. Long-distance movements from established burrow sites by pygmy rabbits (Brachylagus idahoensis) in southwestern Wyoming. Northwestern Naturalist 79:72-74.
- Lyman, R. L. 1991. Late quaternary biogeography of the pygmy rabbit (Brachylagus idahoensis) in eastern Washington. Journal of Mammalogy 72:110-117.
- Rauscher, R. 1997. Status and distribution of the pygmy rabbit in Montana. Montana Department of Fish, Wildlife and Parks, Non-game program. Unpublished report, 19 pp plus appendices.
- Verts, B. J. and L. N. Carraway. 1998. Land mammals of Oregon. University of California Press, Berkeley. xvi + 668 p.
- Additional ReferencesLegend: View WorldCat Record View Online Publication
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- Abstracts from Montana Rare Animal Meeting. 1992. [November 5-6, 1992]. Lewistown, MT. 20 pp.
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- Estes-Zumpf, W.A. and J.L. Rachlow 2005. Natal Dispersal of Juvenile Pygmy Rabbits: Preliminary Results. Department of Fish and Wildlife Resources, University of Idaho, Moscow, ID. Presentation during The Montana Chapter of The Wildlife Society, Annual Conference. Helena, Montana. March 2, 2005.
- Foresman, K. R. 2001. The wild mammals of Montana. American Society of Mammologists, Special Publication Number 12. Lawrence, KS. 278 p.
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- Heady, L.T., K.I. Gabler, and J.W. Laundre. 2001. Habitat Selection by Pygmy Rabbits in Southeast Idaho. BLM Technical Bulletin No. 01-7.
- Hoffmann, R. S. and D. L. Pattie. 1968. A guide to Montana mammals: identification, habitat, distribution, and abundance. University of Montana, Missoula. 133 p.
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- NatureServe. 2005. Online search for element information on population/occurrence delineation of pygmy rabbit (Brachylagus idahoensis).
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- USFWS. 2003. Endangered and Threatened Wildlife and Plants; Final Rule to List the Columbia Basin Distinct Population Segment of the Pygmy Rabbit (Brachylagus idahoensis) as Endangered . Federal Register: March 5, 2003 (Volume 68, Number 43)] Page 10388-10409.
- Washington Department of Wildlife. 1993. Status of the pygmy rabbit (Brachylagus idahoensis) in Washington. Washington Department of Wildlife, Olympia.
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- Whisenant, S. G. 1990. Changing fire frequencies on Idaho's Snake River plains: ecological and management implications. Pages 4-10 in E. D. McArthur, E. M. Romney, S. D. Smith, and P. T. Fuller, editors. Proceedings of a symposium on cheatgrass invasion, shrub die-off, and other aspects of shrub biology and management. USDA Forest Service, Intermountain Research Station, Ogden, Utah.
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