Abstract
We used multiple logistic regression to model how different landscape conditions contributed to the probability of human-grizzly bear conflicts on private agricultural ranch lands. We used locations of livestock pastures, traditional livestock carcass disposal areas (boneyards), beehives, and wetland-riparian associated vegetation to model the locations of 178 reported human-grizzly bear conflicts along the Rocky Mountain East Front, Montana, USA during 1986-2001. We surveyed 61 livestock producers in the upper Teton watershed of north-central Montana, to collect spatial and temporal data on livestock pastures, boneyards, and beehives for the same period, accounting for changes in livestock and boneyard management and beehive location and protection, for each season. We used 2032 random points to represent the null hypothesis of random location relative to potential explanatory landscape features, and used Akaike's Information Criteria (AIC/AICC) and Hosmer-Lemeshow goodness-of-fit statistics for model selection. We used a resulting "best" model to map contours of predicted probabilities of conflict, and used this map for verification with an independent dataset of conflicts to provide additional insights regarding the nature of conflicts. The presence of riparian vegetation and distances to spring, summer, and fall sheep or cattle pastures, calving and sheep lambing areas, unmanaged boneyards, and fenced and unfenced beehives were all associated with the likelihood of human-grizzly bear conflicts. Our model suggests that collections of attractants concentrated in high quality bear habitat largely explain broad patterns of human-grizzly bear conflicts on private agricultural land in our study area.
| Original language | English |
|---|---|
| Pages (from-to) | 47-59 |
| Number of pages | 13 |
| Journal | Biological Conservation |
| Volume | 130 |
| Issue number | 1 |
| DOIs | |
| State | Published - Jun 2006 |
Funding
We thank the livestock producers and residents of the Teton watershed for their time, support, and help. We thank A. and S. Rollo, C. Crawford, the Teton River Watershed Group, and the Nature Conservancy for their help with different aspects of this project. Special thanks to Montana Department of Fish, Wildlife and Parks. Thanks to G. Neudecker of the US Fish and Wildlife Service, Blackfoot Challenge, and ranchers and landowners in the Blackfoot Valley, Montana for help with pretests. Financial support was provided by the University of Montana’s College of Forestry, National Science Foundation Experimental Program to Stimulate Competitive Research, Bolle Center for People and Forests, Y2Y Science Grants of the Wilburforce Foundation, Pumpkin Hill Foundation, the National Fish and Wildlife Foundation, Y2Y/LaSalle Adams Fund, the Bunting Family Foundation, the Northern Rockies Conservation Cooperative, and Montana Department of Fish, Wildlife and Parks. Very special thanks to Dr. Jim Burchfield and Dr. Jill Belsky for all their support. D. Pletscher, D. Fenn, R. Barrett, and M. Patterson provided valuable editorial remarks on earlier versions of this manuscript.
Keywords
- Attractants
- Beehives
- Conflict
- Grizzly bear
- Landscapes
- Livestock
- Montana
- Private lands
- Ranches