Food habits and livestock depredation of two Iberian wolf packs (Canis lupus signatus) in the north of Portugal
By J. Vos. 2000
144 citations recorded by the source corpus.
Subfields: Ecology
View Paper: https://www.semanticscholar.org/paper/92bb4b1eb422f0b9d1bdf4aab2e75de4a3d61733
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In Ecology
- Aaron J. Wirsing
- W. Ripple
- Kay E. Holekamp
- T. Newsome
- Chris R. Dickman
- J. Kolowski
- R. Kays
- F. Azevedo
Citations in the corpus
- Wolf Canis lupus numbers, diet and damage to livestock in relation to hunting and ungulate abundance in northeastern Belarus during 1990–2000 (2003, background): “ Vos (2000) emphasised that reintroduction of native prey species is essential for conservation of wolves in Portugal.”
- Spatial, temporal, and physical characteristics of livestock depredations by large carnivores along a Kenyan reserve border (2006, background): “Large carnivores, humans and their livestock have coexisted for millennia, but recent decades have seen dramatic increases in the frequency of . su.edu (K.E. Holekamp). human–carnivore conflict, resulting mainly from an exponential increase in the human population (Woodroffe, 2000; Conover, 2002).”
- Spatial organization and food habits of jaguars (Panthera onca) in a floodplain forest (2007, background): “Our detection of carcasses of prey killed may have been biased in favor of larger prey; to minimize this influence, we focused on the scat sample analysis (Karanth and Sunquist, 2000; Vos, 2000; Biswas and Sankar, 2002).”
- Livestock predation by lions (Panthera leo) and other carnivores on ranches neighboring Tsavo National ParkS, Kenya (2004, background): “Varying intensity of livestock predation by large carnivores with availability of native prey has been documented spatially for big cats in Venezuela (Polisar et al., 2003) and temporally for carnivores in Zimbabwe (Butler, 2000), Kenya (Karani, 1994; Rudnai, 1979), and Europe (Meriggi and Lovari, 1”
- The ecological effects of providing resource subsidies to predators (2015, background): “Of the studies that reported > 90% utilisation of a resource subsidy (Macdonald, 1979; Vos, 2000; Abay et al., 2011; Yirga et al., 2012), all were in peri-urban or agricultural systems where the most readily available prey was the resource subsidy itself (Appendix S1).”