Targeting hunter distribution based on host resource selection and kill sites to manage disease risk
Article first published online: 1 OCT 2013
© 2013 The Authors. Ecology and Evolution published by John Wiley & Sons Ltd.
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Ecology and Evolution
Volume 3, Issue 12, pages 4265–4277, October 2013
How to Cite
Ecology and Evolution 2013; 3(12): 4265–4277
- Issue published online: 23 OCT 2013
- Article first published online: 1 OCT 2013
- Manuscript Accepted: 28 AUG 2013
- Manuscript Revised: 14 AUG 2013
- Manuscript Received: 13 MAY 2013
- Parks Canada (Riding Mountain National Park)
- PrioNet Canada
- University of Saskatchewan
- Manitoba Conservation
- Canadian Council on Ecological Areas
- Manitoba Agriculture
- Food and Rural Initiatives
- Riding Mountain Biosphere Reserve
- Nature Conservancy of Canada
- Manitoba Wildlife Federation
- Louisiana Pacific
- Earth Rhythms Inc.
- Westlake and Seven Oaks Wildlife Associations
- Friends of Riding Mountain National Park
- Canadian Food Inspection Agency
- Natural Science and Engineering Research Council of Canada (NSERC)
Table S1. A priori selection of environmental covariates for elk (Cervus canadensis manitobensis) to derive resource selection function models and selection ratios at the scale of the quarter section (n = 20,970) during the hunting season (September–February) in southwestern Manitoba, Canada.
Table S2. Standardized parameter estimates from logistic regression resource selection function models for collared and hunter-killed adult females and juvenile males during the hunting season (September–March; 2002–2012) in southwestern Manitoba, Canada. Model-averaged β coefficient for each predictor covariate derived from an average of all possible models with a change in Akaike value < 2 (ΔAIC, 2.0). Covariates are described in Supporting Information, Table S1.
Figure S1. Overall schematic outline of the analyses to map disease risk management areas.
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