Grizzly bear depredation on grazing allotments in the Yellowstone Ecosystem

被引:13
作者
Wells, Smith L. [1 ,5 ]
McNew, Lance B. [1 ]
Tyers, Daniel B. [2 ]
van Manen, Frank T. [3 ]
Thompson, Daniel J. [4 ]
机构
[1] Montana State Univ, Dept Anim & Range Sci, POB 172900, Bozeman, MT 59718 USA
[2] US Forest Serv, Northern Rocky Mt Sci Ctr, 2327 Univ Way,Suite 2, Bozeman, MT 59715 USA
[3] US Geol Survey, Northern Rocky Mt Sci Ctr, Interagency Grizzly Bear Study Team, 2327 Univ Way,Suite 2, Bozeman, MT 59715 USA
[4] Wyoming Game & Fish Dept, 260 Buena Vista Dr, Lander, WY 82520 USA
[5] Montana Dept Fish Wildlife & Pk, 1420 East 6th Ave, Helena, MT 59620 USA
关键词
conflict; Forest Service; grazing allotment; Greater Yellowstone Ecosystem; grizzly bear; habitat; livestock depredation; management; Ursus arctos; MOUNTAIN RANGELAND; HABITAT SELECTION; WHITEBARK-PINE; CATTLE; MOVEMENTS; MORTALITY; ABUNDANCE; BEHAVIOR; MONTANA; MODELS;
D O I
10.1002/jwmg.21618
中图分类号
Q14 [生态学(生物生态学)];
学科分类号
071012 ; 0713 ;
摘要
Grizzly bear (Ursus arctos) conflicts with humans, including livestock depredation on public land grazing allotments, have increased during the last several decades within the Greater Yellowstone Ecosystem (GYE) in the western United States as the grizzly bear population has grown in number and occupied range. Minimizing conflicts and improving conservation efficacy requires information on the relationships between livestock depredations, allotment management, grizzly bear habitat conditions, and their interactions. We used generalized linear mixed models to evaluate spatio-temporal relationships between grizzly bear depredation of livestock and the characteristics of 316 United States Department of Agriculture Forest Service and National Park Service grazing allotments in the GYE during 1992-2014. We evaluated relationships at 2 spatial extents, representing daily and annual grizzly bear activity areas. During the study period, more grazing allotments became occupied by grizzly bears and most livestock depredations were associated with these areas of population expansion. Number of livestock (beta = 1.15 +/- 0.19 [SE]) and grizzly bear density index (beta = 1.13 +/- 0.10) had the greatest effects on the number of livestock depredation events relative to other allotment attributes. Estimated number of depredation events increased by approximately 20% when cow-calf pairs increased by 100 pairs and grizzly bear density index increased by 1 bear/196 km(2) (the average annual home-range size of a female grizzly bear in the GYE). Additionally, grazing allotment size was positively related to the number of depredation events (beta = 0.56 +/- 0.16), whereas the presence of bull cattle or horses was associated with an approximately 50% reduction in depredations (beta = -0.71 +/- 0.37). Livestock depredation events were greater for allotments with lower road density (beta = -0.89 +/- 0.28), less rugged terrain (beta = -0.57 +/- 0.25), higher vegetative primary productivity (beta = 0.33 +/- 0.16), and more whitebark pine coverage (beta = 0.30 +/- 0.15). Relationships between depredations and grizzly bear habitat conditions varied across spatial extents. As the grizzly bear population continues to expand, natural resource managers and livestock producers could focus efforts on allotments with a higher density of grizzly bears, fewer roads, and quality grizzly bear habitat, including higher vegetative productivity, when developing cooperative management plans and preventative measures to reduce the likelihood of depredation. The perspectives gained from our analysis provide context for long-term, landscape-level planning to accommodate livestock production on public lands while meeting conservation goals for grizzly bears. (c) 2018 The Wildlife Society.
引用
收藏
页码:556 / 566
页数:11
相关论文
共 74 条
[1]  
Anderson CR, 2002, URSUS, V13, P247
[2]  
[Anonymous], UPD EV APPR EST POP
[3]  
Apps CD, 2004, J WILDLIFE MANAGE, V68, P138, DOI 10.2193/0022-541X(2004)068[0138:EGBDAA]2.0.CO
[4]  
2
[5]   Uninformative Parameters and Model Selection Using Akaike's Information Criterion [J].
Arnold, Todd W. .
JOURNAL OF WILDLIFE MANAGEMENT, 2010, 74 (06) :1175-1178
[6]   Fitting Linear Mixed-Effects Models Using lme4 [J].
Bates, Douglas ;
Maechler, Martin ;
Bolker, Benjamin M. ;
Walker, Steven C. .
JOURNAL OF STATISTICAL SOFTWARE, 2015, 67 (01) :1-48
[7]   MORTALITY OF CATTLE ON 2 TYPES OF GRAZING AREAS IN NORTHWESTERN ALBERTA [J].
BJORGE, RR .
JOURNAL OF RANGE MANAGEMENT, 1983, 36 (01) :20-21
[8]  
Bjornlie D. D., 2015, YELLOWSTONE GRIZZLY, P51
[9]   Methods to Estimate Distribution and Range Extent of Grizzly Bears in the Greater Yellowstone Ecosystem [J].
Bjornlie, Daniel D. ;
Thompson, Daniel J. ;
Haroldson, Mark A. ;
Schwartz, Charles C. ;
Gunther, Kerry A. ;
Cain, Steven L. ;
Tyers, Daniel B. ;
Frey, Kevin L. ;
Aber, Bryan C. .
WILDLIFE SOCIETY BULLETIN, 2014, 38 (01) :182-187
[10]   Whitebark Pine, Population Density, and Home-Range Size of Grizzly Bears in the Greater Yellowstone Ecosystem [J].
Bjornlie, Daniel D. ;
Van Manen, Frank T. ;
Ebinger, Michael R. ;
Haroldson, Mark A. ;
Thompson, Daniel J. ;
Costello, Cecily M. .
PLOS ONE, 2014, 9 (02)