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2007b). If this does not occur, or where it is impossible, then continued management of animals will be required to avoid loss of genetic diversity. A second potential problem is the effect of fencing on the spatial and social behaviour of the reintroduced species. Large predator home range sizes are generally negatively related to the biomass of preferred prey (Nilsen and Linnell 2006; Hayward et al. 2008). Thus, their territory size can be predicted using the biomass of preferred prey. Data from Addo Elephant National Park show that the range size of lions and spotted hyaenas (and a leopard) are not constrained by the fences and conform to predictions based on the availability of preferred prey (Hayward et al.
De Tores (*) • N. J. W. J. de Tores and N. Marlow Background to 1080 Baiting in Western Australia: A Demonstrated Need for Control of the Fox A number of landmark studies in WA in the 1980s and 1990s demonstrated the effectiveness of repeated 1080 baiting. Successes included: • Increased trap success of woylies, or brush-tailed bettongs, Bettongia penicillata at Dryandra Woodland and Tutanning Nature Reserve (Kinnear et al. 2002) and the Perup Forest (Christensen 1980a, b). • Increased sightings of numbats Myrmecobius fasciatus (Friend 1990; Friend and Thomas 2003) at Dryandra Woodland.
2008) Do fences constrain predator movements on an evolutionary scale? Home range, food intake and movement patterns of large predators reintroduced to Addo Elephant National Park, South Africa. Biodiversity and Conservation, 18, 887–904. , Mduma, S. E. (2006) Effective enforcement in a conservation area. Science, 314, 1266. , Slotow, R. D. (2007) Restoring lions Panthera leo to northern KwaZulu-Natal, South Africa: short-term biological and technical success but equivocal long-term conservation.