Southern Mountain Caribou DPS (Rangifer tarandus ssp. caribou)
Taxonomy:
View taxonomy in ITISListing Status: Endangered
Where Listed: WHEREVER FOUND
General Information
There are four extant recognized subspecies of caribou in North America, of which woodland caribou (Rangifer tarandus caribou) is the southernmost, having historically ranged throughout most of southern Canada and portions of the United States. Currently, southern mountain caribou are the only population with the potential to occur in the contiguous United States (recently occupied habitat in northeastern Washington and northern Idaho; ephemeral use by transient individuals in northwestern Montana). Southern mountain caribou are located in steep, mountainous terrain west of the continental divide in the inland temperate rainforest ecosystem, which extends from east-central British Columbia to the inland northwestern United States and is characterized by the presence of arboreal lichens and deep winter snowpack. One feature that makes southern mountain caribou distinct is their dependence on arboreal (tree) lichens in the mid-canopy of forest habitats during the winter, while all other caribou populations depend on terrestrial lichens that grow in large mats on the ground. The U.S. Fish and Wildlife Service (Service) published a final rule in October 2019 designating the southern mountain caribou distinct population segment (DPS) of woodland caribou as endangered under the Endangered Species Act (ESA). This action amended the previously listed entity by defining the DPS, which includes the U.S.-Canada transboundary South Selkirk subpopulation (originally listed in 1983) and 16 additional subpopulations of caribou in Canada (some of which are extirpated). The Service is working to recover the southern mountain caribou DPS population and recognizes the importance of bi-national and cross-sovereign collaboration with Canada on the potential development and implementation of a recovery plan. Southern mountain caribou are a medium-sized member of the deer family that have large hooves, broad muzzles, and distinct antlers that both sexes develop annually. The average lifespan for caribou is eight to ten years. Female caribou do not breed until they are 2.5 years old and produce only one calf per year. Only about three out of ten calves typically survive to adulthood. Individual caribou can display tremendous variability in appearance and body form even within the same population. Woodland caribou are generally described as dark brown with a white mane and some white on their sides and have a noticeable band of white hairs (called socks) along the upper edge of each hoof. They are larger and darker than both the Peary caribou (Rangifer tarandus pearyi) and the barren-ground caribou (Rangifer tarandus groenlandicus). Adult males of woodland caribou are described as having a mane of longer hairs along the bottom of the neck to the chest. During rut, the light color of the neck and mane contrasts with the darker colored body. In addition, their ears are short, broad, and not pointed. Height of the woodland caribou at the shoulder is a little over 3 to 4 feet (ft) (1.0 to 1.2 meters (m)). Females weigh about 240 to 330 pounds (lbs) (110 to 150 kilograms (kg)) and males about 350 to 460 lbs (160 to 210 kg). Both male and female caribou grow antlers, although up to half of females may lack antlers or have one antler. The antlers of woodland caribou may be denser and flatter than those of barren-ground caribou. All caribou can withstand severe cold because their thick winter coat contains semi-hollow hair with strong insulative properties. However, woodland caribou are susceptible to overheating in summer months as their dark coat absorbs sunlight. One of the most distinctive characteristics of all subspecies of caribou is their large, rounded hooves. Their hooves reduce sinking into snow and wetlands and allow them to walk or stand on hard snowpack to reach tree lichens, and they can use their hooves as paddles while swimming. All caribou have prominent dew claws just above the hoof.The species historical range included Alaska, Idaho, Maine, Michigan, Minnesota, Montana, New Hampshire, Vermont, Washington, Wisconsin. See below for information about where the species is known or believed to occur.
» Range Information
Current Range
Current range maps are only shown within the jurisdictional boundaries of the United States of America. The species may also occur outside this region.
U.S.A. (wherever found), Canada (southeastern British Columbia)
Listing status: Endangered
This population has been proposed for downlisting (Endangered -> Threatened)- States/US Territories in which this population is known to or is believed to occur: Idaho, Washington
- US Counties in which this population is known to or is believed to occur: View All
- USFWS Refuges in which this population is known to occur:
- Countries in which this population is known to occur: Canada, United States
» Candidate Information
No Candidate information available for this species.
No Candidate Assessments available for this species.
No Uplisting Documents currently available for this species.
» Federal Register Documents
» Species Status Assessments (SSAs)
No Species Status Assessments (SSA's) are currently available for this species.
No Special Rule Publications currently available for this species.
» Recovery
- Species with Recovery Documents Data Explorer
- Recovery Priority Number: 3C
No Delisting Documents currently available for this species.
» Critical Habitat
To learn more about critical habitat please see https://ecos.fws.gov/crithab
» Conservation Plans
No Conservation Plans currently available for this species.
» Petitions
» Biological Opinions
To see all FWS Issued Biological Opinions please visit the BO Report.
» Life History
Habitat Requirements
Caribou are the most widespread ungulate species in the world and the ecosystems they have evolved to occupy are highly variable, including the tundra and taiga biomes on all northern continents. Occupied habitats vary from flat and open arctic and subarctic tundra to forested habitat, including high elevation and steep mountainous slopes. Variability in habitat occupancy has driven the evolution of many different ecosystem-specific behavioral and migratory traits within the species. Southern mountain caribou use steep, high-elevation (typically over 4,000 feet elevation), mountainous habitats with deep snowfall, and substantial arboreal (tree) lichens. Rather than embarking on long-distance migrations similar to other caribou populations, the southern mountain caribou DPS population instead stays within the same general latitude and undertakes as many as four altitudinal migrations per year. After wintering at high elevations, at the onset of spring these caribou move to lower elevations where snow has melted to forage on new green vegetation. Pregnant females will move to these spring habitats for forage. During the calving season, sometime from June into July, the need to avoid predators influences habitat selection. Areas selected for calving are typically high elevation, alpine and non-forested areas in close proximity to old-growth forest ridge tops, as well as high-elevation basins. These high-elevation sites can be food limited but are more likely to be free of predators. During calving, arboreal lichens again become the primary food source for pregnant females at these elevations because green forage is largely unavailable in these secluded, old growth conifer habitats. During summer months, southern mountain caribou move back to upper elevation spruce/alpine fir forests.
Food Habits
Caribou are variable in their diet. They feed on lichens, mosses, grasses, ferns, and shoots and leaves of deciduous shrubs and trees, depending on availability. Southern mountain caribou rely heavily on arboreal (tree) lichens. Arboreal lichens are critical in the winter months and may also be an important component for females seeking increased security in higher elevation areas during the calving season (June to July). Summer diets include selective foraging of grasses, flowering plants, horsetails, willow and dwarf birch leaves and tips, sedges, lichens, and huckleberry leaves. Their fall and early winter diets consist largely of dried grasses, sedges, willow and dwarf birch tips, and arboreal lichens. Arboreal lichens are pulled from the branches of conifers, picked from the surface of the snow after being blown out of trees by wind, or are grazed from wind-thrown branches and trees. The two kinds of arboreal lichens commonly eaten by the southern mountain caribou are Bryoria spp. and Alectoria sarmentosa. Both are extremely slow-growing lichens most commonly found in high-elevation, old-growth conifer forests that are greater than 250 years old.
Movement / Home Range
Historically, the southern mountain caribou DPS existed in an interconnected population, but recently this population has been fragmented into 17 isolated subpopulations, some of which are likely extirpated. Subpopulations at the southern extent of the range are among the six considered as confirmed or probably extirpated. The last known caribou in the southern mountain caribou DPS population from the South Selkirks and four caribou from the South Purcells were translocated to the larger Columbia North subpopulation using a soft release approach in early 2019. Southern mountain caribou were last reported to cross the border in late 2018 when a bull and cow were sighted in northwest Montana. Previous radio-tracking data indicated that a collared bull entered Washington for about 10 days in late 2014. Prior to extirpation, the average homerange of a South Selkirk Caribou in the southern mountain caribou DPS was estimated at 7,770 ha (19,200 ac) in size. The present distribution and abundance of the southern mountain caribou DPS is greatly reduced from historical accounts. According to the most recent status assessment in the Joint Protection Study (2017), only two of the extant southern mountain caribou DPS subpopulations (Groundhog and Narrow Lake) were documented as either increasing or stable. The nine other extant subpopulations within the DPS were declining, including two of the potentially more resilient subpopulations, which are located at the northern end of the DPS: the Hart Ranges and the North Cariboo Mountains (Hatter 2006). Six of the 11 extant subpopulations (groupings as defined by COSEWIC 2014) were estimated to consist of fewer than 50 individuals, three consist of between 50 and 250 individuals, and two consist of between 250 and 400 individuals (Joint Protection Study 2017).
Reproductive Strategy
Woodland caribou are polygynous, with dominant bulls breeding with multiple cows in the fall. Pregnant females travel to isolated, often rugged areas where predators and other prey animals are limited. Calves are born in late spring into early summer. A single young is born and is capable of following its mother soon after birth. The productivity of caribou is low compared to other cervids (e.g., deer and moose). Caribou have only one calf per year and most females reproduce for the first time around 3 years of age. Caribou reach sexual maturity at approximately 16 to 28 months of age. On average, mortality of woodland caribou calves is 50 to 70 percent within their first year. This mortality rate depends on the abundance of predators or the availability of winter forage during pregnancy, or both. Predation is the most common cause of calf fatalities. Calf fatality is also linked to the health of the calf at birth. It has been shown that female caribou may be nutritionally deficient in some years during pregnancy due to temporal variation in the accessibility of lichens and may be more likely to produce weak calves in low access years. Weak calves are likely more susceptible to predation and diseases such as pneumonia. As such, temporal variation in lichen availability may also be driving calf mortality and low calf recruitment in some years.
Other
For more information and citations see our Final Rule and Recovery Outline documents.
» Other Resources
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