The Gray Wolf is the largest of the wild dogs. Adult male Gray Wolves in Montana weigh around 47 kilograms (104 pounds) and females weigh around 36 kilograms (80 pounds). Males average approximately 186 centimeters (73 inches) in length, while 180 centimeters (70 inches) is the average for females, with the tail compromising a little less than one-third of the total length in both sexes (Foresman 2012). About half the Gray Wolves in Montana are black with the other half gray. Both color phases may be found in a pack or in a litter of pups.
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
(Observations spanning multiple months or years are excluded from time charts)
This species is not migratory but may move seasonally following migrating ungulates within its territory. Gray Wolves also disperse widely. Males in northwestern Montana can move an average of 113 km (70 miles) from their natal territory, and females 77 km (48 miles), before establishing a new territory or joining an existing pack (Boyd and Pletscher 1999). Dispersal peaks twice per year; first in January/February and second, in May/June (Boyd and Pletscher 1999). Some Gray Wolves are known to have dispersed up to 805 km (500 miles). Dispersal has been documented from Canada, Idaho and Wyoming to Montana. Montana Gray Wolves are also known to have dispersed to Canada, Idaho, and Wyoming.
The Gray Wolf exhibits no particular habitat preference except for the presence of native ungulates within its territory on a year-round basis. In Minnesota and Wisconsin, Gray Wolves usually occur in areas with few roads and human disturbance (Thiel 1985, Mech et al. 1988, Mech 1989). Gray Wolves establishing new packs in Montana have demonstrated greater tolerance of human presence and disturbance than previously thought characteristic of this species. They have established territories where prey are more abundant at lower elevations than expected, especially in winter (MTFWP 2003).
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: 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. 2012. Mammals of Montana. Second edition. Mountain Press Publishing, Missoula, Montana. 429 pp.
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- 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
Shrubland, Steppe and Savanna Systems
Sparse and Barren Systems
Wetland and Riparian Systems
- Occasionally Associated with these Ecological Systems
Gray Wolves are opportunistic carnivores that predominantly prey on large ungulates. Main prey items in Montana include deer, Elk, and Moose (MTFWP 2003). Bison are also taken where the ranges of the two species overlap in and around Yellowstone National Park. Domestic livestock such as cattle and sheep are also preyed upon. Gray Wolves may also eat alternative prey, such as rodents, vegetation and carrion. Gray Wolves commonly hunt in packs, but lone animals and pairs are able to kill prey as large as adult Moose (Thurber and Peterson 1993).
In most areas, Gray Wolves are territorial throughout the year. Packs generally consist of a socially dominant pair, their offspring of the previous year, and new pups, although other breeding-age adults that may or may not be related to the alpha pair may also be present (MTFWP 2003). More than 1 female in the pack can breed and give birth to pups. Pup survival when there are multiple litters is highly variable. Pack size varies and may include as few as 3 and as many as 37 (USFWS et al. 2001). In the Glacier National Park area, packs generally include 8 to 12 individuals (Bangs and Fritts 1993). Packs share pup-rearing responsibilities including food provisioning and tending pups at the den or rendezvous sites (MTFWP 2003). Pack activity is centered on the den site and nearby rendezvous sites from late April until September (MTFWP 2003). Lone Gray Wolves may move through territories of established packs (Thurber and Peterson 1993). Pack territories are dynamic and change from year to year depending on prey availability, Gray Wolf populations, and relationships with neighboring packs.
Summer home ranges are smaller than winter ranges; the annual range may be up to several hundred square kilometers (km). In the Glacier National Park area, territory size averages around 780 square kilometers (301 square miles)(Bangs and Fritts 1993). Gray Wolves may occasionally move several hundred kilometers, especially dispersing young. In Minnesota, most dispersers left when they were 11 to 12 months old; dispersal occurred mainly in February to April and October to November; 35% of known-age Gray Wolves remained in their natal territory for more than 2 years (Gese and Mech 1991). Average territory size in northwestern Montana was 220 square kilometers (185 square miles) but was highly variable (USFWS et al. 2002). Average territory size for Yellowstone Gray Wolves was larger, averaging 891 square kilometers (344 square miles) (USFWS et al. 2002).
Gray Wolves are generally not instrumental in causing prey declines but their effect varies with other environmental circumstances. In Quebec, winter weather appeared to affect the deer population trend more than did Gray Wolf predation (Potvin et al. 1992). In south-central Alaska, Gray Wolf predation may have limited Caribou recruitment (Bergerud and Ballard 1988), though winter starvation also was proposed as a significant population control. Gray Wolves may take livestock as secondary prey when deer fawns (the primary summer prey) are less vulnerable due to better prenatal nutrition resulting from mild winter (USFWS 1990). In Minnesota, snow-induced changes in deer distribution and mobility resulted in changes in Gray Wolf movement patterns, sociality, and feeding behavior. When snow was shallow, Gray Wolves traveled farther and more often, spent less time with pack members, and used conifer cover less and killed fewer deer (Fuller 1991). Gray Wolves have been implicated in declines in Elk numbers around Yellowstone National Park. This relationship is still being studied in conjunction with other environmental factors.
In Montana, Gray Wolves breed in mid- to late February (Boyd et al. 1993), with gestation lasting about 63 days (MTFWP 2003). A female can only give birth once a year. Breeding usually occurs between the dominant male and female in the pack and Gray Wolves normally do not breed until they are at least 22 months old (Mech 1970). Occasionally, more than 1 female in a pack may breed, resulting in more than 1 litter per pack (Ballard et al 1987). Young are typically born in late April in an underground burrow that has been abandoned by another mammal or dug by Gray Wolves. In northwestern Montana litter sizes range from 1 to 9 with a mean of 5.3 (MTFWP 2003). Pups emerge from the den in about 3 weeks and are weaned in 50 days (also reported as 5 weeks). Young vacate the den when they are about 3 months old (Hoffmeister 1986) and move to a series of rendezvous sites throughout the pack's territory. The pups are large enough to travel with the entire pack by September. Some offspring remain with the pack; others disperse as they mature. Lone Gray Wolves generally do not successfully rear young, but they may if food is abundant (Boyd and Jimenez 1994).
Pup survival is variable and influenced by a number of factors including disease, predation, and nutrition. In Montana, pup mortality was most often attributed to human causes (Pletscher et al. 1997), but canine parvo virus was strongly suspected as a main factor in low pup survival in Yellowstone Gray Wolves in 1999 (MTFWP 2003).
Although Gray Wolves dispersing from Canada were occasionally observed, they were essentially extirpated from Montana and the rest of the western United States in the early 1900s primarily due to conflicts with people. As a result, they were listed as Endangered under the Endangered Species Act in 1967 (32 FR 4001). Gray Wolves started recolonizing the area around Glacier National Park in 1979 and the first den documented in Montana in over 50 years was found in Glacier National Park in 1986. In 1995 and 1996 Gray Wolves were reintroduced into Yellowstone National Park and central Idaho. Wolves resulting from these reintroductions and those dispersing naturally from northwestern Montana and Canada have now colonized most of western Montana. Gray wolves reached biological recovery goals for the Northern Rocky Mountains at the end of 2002 and were delisted in May of 2009 (74 FR 15123 15188). However, they were relisted as Endangered/Experimental Nonessential on August 5, 2010 by federal court order. Then, on May 5, 2011, they were again removed from the Endangered Species Act by the Secretary of the Interior at the direction of the President of the United States and Congress under a rider associated with the Department of Defense and Full-Year Appropriations Act of 2011 (76 FR 25590-25592).
Montana Fish, Wildlife and Parks is the lead agency for Gray Wolves, including population monitoring, resolving wolf-livestock conflicts, research, and public outreach. Federal regulations continue to guide Montana Fish, Wildlife, and Parks management practices. You can access a variety of detailed information on Gray Wolves in Montana from the Montana Fish, Wildlife, and Park's Wolf Program
- Literature Cited AboveLegend: View Online Publication
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- Additional ReferencesLegend: View Online Publication
Do you know of a citation we're missing?
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