Species: Alces americanus

Moose
Species
    Kingdom
    Animalia
    Phylum
    Craniata
    Class

    Mammalia

    Order

    Artiodactyla

    Family

    Cervidae

    Genus

    Alces

    Classification
    Other Global Common Names
    orignal
    Informal Taxonomy
    Animals, Vertebrates - Mammals - Other Mammals
    Formal Taxonomy
    Animalia - Craniata - Mammalia - Artiodactyla - Cervidae - Alces - See Kraus and Miyamoto (1991) for a phylogenetic analysis of pecoran ruminants (Cervidae, Bovidae, Moschidae, Antilocapridae, and Giraffidae) based on mitochondrial DNA data.
    Migration
    true - true - false - May make short elevational or horizontal migrations between summer and winter ranges.
    Non-migrant
    true
    Locally Migrant
    true
    Food Comments
    Summer: prefers to browse on new growth of trees and shrubs (leaves, twigs, and bark), and vegetation associated with water (attracted to high-sodium aquatic plants). Winter: typically restricted to conifer and hardwood twigs.
    Reproduction Comments
    Breeds September-late October; peak in mid-September. Gestation lasts 240-246 days. One calf (less commonly 2) born late May-early June. Sexually mature in 1.5 years, though females do not reach peak productivity until age 4 years and most males do not breed until 5-6 years old due to intrasexual competition.
    Ecology Comments
    Depending on habitat, home range may be up to several thousand hectares (Lawson and Rodgers 1997). Population density has been reported as up to 1-3 per sq mile (= 11.6 per 10 sq km) (Peterson 1955), but 18-20 per 10 sq km in unhunted area in eastern Quebec (Crete 1989). May herd in winter. <br><br>Winter weather (snow accumulation) may strongly affect populations, even more so than wolf density (Mech et al. 1987); however, Messier (1991) found that competition for food, but not wolf predation and snow, had a regulatory impact on moose. Van Ballenberghie and Ballard (1994) found that in naturally regulated ecosystems predation by bears and wolves often is limiting and may be regulating under certain conditions. See also Messier (1994, Ecology 75:478-488) for population models of moose-wolf interactions. <br><br>Under favorable conditions, capable of large annual increases (20-25%) in population size; large populations may degrade habitat, resulting in population crash. See Albright and Keith (1987) for study of population dynamics of introduced population in Newfoundland (poor winter condition but high calf-survival [few predators]). <br><br>See Nudds (1990) for discussion of relation between white-tailed deer, moose, and meningeal (brain) worms. Brainworm may limit moose populations in areas where white-tailed deer are common. Deer are not negatively impacted by the brainworm, the larval stage of which is passed in deer feces. Snails, often inadvertently ingested by moose feeding on vegetation, are the intermnediate host for the worm. Deer, through worm-mediated impacts, commonly are believed to exclude moose and caribou from areas where deer occur; however, an analysis by Schmitz and Nudds (1994) concluded that moose may be able to coexist with deer, albeit at lower densities, even in the absence of habitat refuges from the disease. Whitlaw and Lankester (1994) found that the evidence that brainworm has caused moose declines is weak. <br><br>Moose may alter the structure and dynamics of boreal forest ecosystems. At Isle Royale, Michigan, moose browsing prevented saplings of preferred species from growing into the tree canopy, resulting in a forest with fewer canopy trees and a well-developed understory of shrubs and herbs; also, browsing may have caused an increase in spruce and a decrease in balsam fir (McInnes et al. 1992).
    Length
    279
    Weight
    630000
    NatureServe Global Status Rank
    G5
    Global Status Last Reviewed
    2006-03-27
    Global Status Last Changed
    1996-11-19
    Other Status

    LC - Least concern

    Conservation Status Map
    <img src="http://www.natureserve.org/explorer/servlet/GetMapGif?CA.AB=S5&CA.BC=S5&CA.LB=S5&CA.MB=S5&CA.NB=S5&CA.NF=SE&CA.NT=S5&CA.NS=S1&CA.NU=SNR&CA.ON=S5&CA.QC=S5&CA.SK=S4&CA.YT=S5&US.AK=S5&US.CO=SE&US.CT=S4&US.ID=S5&US.ME=S5&US.MA=S4&US.MI=S4&US.MN=SNR&US.MT=S5&US.NH=S5&US.NY=S3&US.ND=SNR&US.PA=SX&US.UT=S3&US.VT=S5&US.WA=S2&US.WY=S5" alt="Conservation Status Map" style="width: 475px; height: auto;" />
    Global Range
    Alaska and Canada south through Rockies, northern Great Lakes, and New England; Russia, east of the Yenisei River, east to Anadyr region (eastern Siberia) and south to northern Mongolia and northern China; introduced but now extirpated in New Zealand (Boyeskorov 1999; Grubb, in Wilson and Reeder 2005). This range does not include that of the Eurasia elk (<i>Alces alces</i>) here recognized as a distinct species, following Boyeskorov (1999) and Grubb (in Wilson and Reeder 2005).<br><br>Arrived in North America from Asia about 11,000-14,000 years ago, shortly before flooding of the Bering land bridge (Hundertmark et al. 2003).
    ELEMENT_GLOBAL.2.792092