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Montana Field Guide

Montana Field Guides

Northern Short-tailed Shrew - Blarina brevicauda

Image Copyright and Usage Information
Potential Species of Concern
Native Species

Global Rank: G5
State Rank: SU
(see State Rank Reason below)


Agency Status
USFWS:
USFS:
BLM:
FWP SWAP: SGCN1-3

External Links

State Rank Reason (see State Rank above)
Species has one capture record in Montana and data to assess status are unavailable.
Northern Short-tailed Shrew (Blarina brevicauda) Conservation Status Summary
State Rank: SU
Review Date = 09/12/2024
How we calculate Conservation Status

See the complete Conservation Status Report
 
General Description
The Northern Short-tailed Shrew is realtively large and robust, with inconspicuous ears and minute eyes. The snout is pointed and somewhat proboscis-like but relatively shorter and thicker than in other shrews. The tail is relatively short (< 20% of total length), hairy, and faintly to distinctly bicolored. Dorsal pelage is slaty gray, darker in winter than summer (Jones et al. 1983, Van Zyll de Jong 1983, George et al. 1986). Large adult size and relatively short tail distinguishes this species of shrew from any other in Montana.

Diagnostic Characteristics
A relatively large and robust shrew (total length usually > 110 mm, occipito-premaxillary length usually > 21.5 mm) with a relatively short tail (20% of total length). Dental formula as in shrews of the genus Sorex, with 32 total teeth (including 5 unicuspids in each upper jaw).

Species Range
Montana Range Range Descriptions

Native

Western Hemisphere Range

 


Range Comments
Species is among the least observed of any taxa in the state. Limited information from the single observation near Johnson Lake and collections at the Fort Union National Historic Site along the Missouri River in North Dakota near Snowden, Montana, suggest that the species is present in the far northeastern region of Montana.

Observations in Montana Natural Heritage Program Database
Number of Observations: 1

(Click on the following maps and charts to see full sized version) Map Help and Descriptions
Relative Density

Recency

 

(Observations spanning multiple months or years are excluded from time charts)



Migration
The species is considered non-migratory, although information on movements is lacking for Montana.

Habitat
Considered hypothetical in extreme northeastern Montana since at least 1968 (Hoffmann and Pattie 1968) until two were captured in August 2005 in Sheridan County in marshy, prairie pothole habitat about 1.35 miles (2.2 km) south of the Saskatchewan border. Farther east, within the main range of the species, Northern Short-tailed Shrews are most common in hardwood forests with deep leaf litter and in brushy sites adjacent to ponds and streams, less common in conifer forest and grassland. In Manitoba, this shrew is reported to be most common in grass-sedge marsh and willow-alder shrubs (Jones et al. 1983, Van Zyll de Jong 1983, George et al. 1986).

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:
    1. 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);
    2. Evaluating structural characteristics and distribution of each ecological system relative to the species' range and habitat requirements;
    3. Examining the observation records for each species in the state-wide point observation database associated with each ecological system;
    4. 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.

    Literature Cited
    • 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.

Food Habits
Food habits have not been studied in Montana. Elsewhere, the diet includes a variety of invertebrates, including insects (esp. Lepidoptera, Diptera and Coleoptera larvae), millipedes, annelids (earthworms), mollusks (snails and slugs) and terrestrial amphipods (sowbugs). Vertebrates are less important than invertebrates, but during winter may capture small mammals such as voles (Microtus spp.) and smaller shrews (Sorex spp.). Sometimes food is hoarded. Infrequently attacks much larger animals (e.g. gartersnakes). The saliva is poisonous (even to humans) and aids in capture of prey; may vocalize when feeding (Jones at al. 1983, Van Zyll de Jong 1983, George et al. 1986).

Ecology
Little ecological information is available for the Northern Short-tailed Shrew in Montana. Elsewhere, the species is active throughout the year, both on the surface and in tunnel systems (its own and those of other small mammals). It is active day and night for short periods, but may be inactive up to 80% of the day, by drastically lowering its resting metabolic rate. Nests are built underground, and may be lined with vegetation or animal fur from voles. Two distinct age classes are evident in summer and autumn, representing adults born the previous year and young of the current breeding seasons. Densities can range from 1.6/ha to 121/ha, with home-ranges averaging about 2.5 ha. Winter mortality in some populatons may reach 90%. Raptorial birds and snakes appear to be the main predators of Northern Short-tailed Shrews, as they seem to be distasteful to most mammalian predators (Jones et al. 1983, Van Zyll de Jong 1983, George et al. 1986).

Reproductive Characteristics
No information from Montana. Throughout the range, breeding may occur any month, usually during February to October but greatly reduced during summer. Gestation is 21-22 days, average litter sizes range from 4 to 10, weaning occurs by 25 days of age, adult size (but not weight) is reached by about 50 days, females are reproductively receptive when about 50 days of age, males at about the same age (65 days the earliest successful reproduction reported). Adults may live up to 33 months (Jones et al. 1983, George et al. 1986).

Management
No management needs have been identified and no measures have been enacted to promote Northern Short-tailed Shrew conservation in Montana. Wetland drainage or alteration, and loss of riparian vegetation (e.g. aspen, birch, willow, cottonwood) in woody draws and around springs or seeps, has the potential to negatively impact local populations. Additional surveys for Northern Short-tailed Shrew can provide the basis for development of conservation protocols by determining its full distribution in Montana, the array of habitats in which it occurs, its relative abundance in different habitats, and, if properly designed, an idea of how different habitat disturbances affect this shrew at the margin of its global range.


References
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Citation for data on this website:
Northern Short-tailed Shrew — Blarina brevicauda.  Montana Field Guide.  .  Retrieved on , from