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Beyond 2000 Symposium


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Beyond 2000 Symposium

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Discoveries in Wolf Behavior and Ecology - Thursday Session

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Beyond 2000:
Realities of Global Wolf Restoration

23-26 February 2000
Duluth, Minnesota USA

 


Characteristics of wolf dispersal in the Rocky Mountains

Diane Boyd, Edward Bangs, Joseph Fontaine, Thomas Meier, U.S. Fish and Wildlife Service, 100 North Park Street Suite 320, Helena, MT 59601, USA; Daniel Pletscher, Wildlife Biology Program, School of Forestry, University of Montana, Missoula, MT 59812, USA; Douglas Smith, Yellowstone Center for Resources, PO Box 621, Yellowstone National Park, WY 82190, USA; Curtis Mack, Nez Perce Tribe, PO Box 365, Lapwai, ID 83540, USA; Mike Jimenez, U.S. Fish and Wildlife Service, 190 North First Street, Lander, WY 82520, USA

Gray wolves were eradicated from Montana in the 1930s but recolonized these areas through natural dispersal from Canada in the 1980s. From 1979 to 1997, 31 of 58 wolves tagged in and near Glacier National Park (GNP), Montana, dispersed. By 1996, 8 wolf packs had colonized northwest Montana (MT) through dispersal. Wolves left their natal home range quickly (median = 4 days, mode = 1 day) after separating from the pack. Mean dispersal distance was not different between males (113 km) and females (78 km). GNP wolves tended to disperse in a northerly direction to areas of higher wolf density. January-February and May-June were peak months for dispersal. Mean dispersal age (M = 28.7 months; F = 38.4 months) was not correlated with maximum pack size. Annual survival rate (mean + SE) for dispersers and biders (philopatric wolves) did not differ (dispersers = 0.76 + 0.10; biders = 0.77 + 0.14). Wolves killed by humans died closer to roads (mean = 0.13 km) than wolves that died from other causes (mean = 0.85 km).

Eighty percent (n = 30) of wolf mortalities were caused by humans, with proportionately more dispersers (90%) than biders (60%) dying from human causes. Dispersers produced more litters than biders.

Additionally, wolves from Canada were reintroduced to central Idaho (ID) and Yellowstone National Park (YNP) in 1995-96, aiding recovery efforts demographically and genetically. The YNP and ID populations increased more quickly than expected, and each area now contains 2-3 times as many wolves as the colonizing northwest Montana population. However, wolf recovery is not assured and may be significantly impacted by stochastic environmental events and political pressures. Reintroduced wolves dispersing out of the ID and YNP core recovery areas have rarely survived long enough to reproduce because they were killed by people. Although the YNP and ID reintroductions have been lauded as a restoration success, the connectivity of dispersers between the reintroduced populations and the recolonizing population appears to be tenuous at this time. The greatest conservation challenge for western wolves will be expanding wolf recovery outside of the refugia provided by large blocks of public land. Managers can affect recovery positively by maintaining landscape connectivity and minimizing wolf mortalities caused by humans.