Cat Eradication Research Articles

MODELING THE BIOLOGICAL CONTROL OF AN ALIEN PREDATOR TO PROTECT ISLAND SPECIES FROM EXTINCTION

Introduced feral cat (Felis catus) populations are an important threat to many island vertebrate populations and to bird species in particular. Elimination of feral cat populations is desirable in most of these ecosystems. Release of a parasite species in these mostly immune-naive populations is thought to be an efficient eradication measure. Such an approach is theoretically investigated here, using a mathematical model that describes the effects of introducing a virus into the cat population on population dynamics of both the cat and its prey. We studied the effects of two types of introduced feline viruses: Feline Immunodeficiency Virus and Feline Leukemia Virus, both of which are good candidates for eradicating a cat population. Results show that eradication is possible with Feline Leukemia Virus, if natural immunity is sufficiently low. Feline Immunodeficiency Virus cannot fully eradicate cat populations, but can be an effective agent for long-term control of cat populations on islands where total cat eradication is not possible (e.g., there is a high likelihood of continued introduction of cats) or not desirable (e.g., when rats are present). Culling, which by itself would require a very prolonged and logistically demanding effort to eliminate cat populations, may be more efficient when applied simultaneously with virus introduction.

Leopard (Panthera pardus ciscaucasica) in Armenia: basic trends, dangers and hopes

SUMMARY This article describes ecological, genetic, psychological, juridical and economic aspects of the leopard (Panthera pardus ciscaucasica) conservation in Armenia. It also suggests certain tools for species preservation by means of ecotourism and ungulate breeding development and provides an overview of global perils to leopard, namely the cat skin trade, sport hunting and eradication by shepherds and livestock breeders. In the short-term perspective, the current abundance of leopard (25 individuals) ensures the reproduction group size (effective population size) of 15–20 animals and loss of genetic variability (heterozygosity) at a rate 2.5–3% per generation. Individual range and biomass values are 89.2 km2 and 0.5 kg/km2, respectively. If today's trends remain the same, leopard population in Armenia is likely to run down to extinction after approximately 30 generations. These data, however, do not imply the leopard's early demise as its ability to overcome the problem of inbreeding in small populations by adaptability and natural selection is still unknown. In psychological terms, the leopard has the highest preservation value of intangible characteristics — existence value, bequest value, option value and vicarious (recreational) value. The juridical and economic backgrounds of the man—leopard conflict are confined to the assessment of different views on the illegal killing of leopards by farmers and conservationists. Owners of the domestic animals attacked by leopards need full reimbursement of material detriment, while wildlife rangers and conservation authorities blame farmers for deliberate killing of the predators and punish them without understanding the reasons which instigate the livestock breeders to commit the misdeed.

Breeding of the Seychelles Magpie Robin Copsychus sechellarum and implications for its conservation

The total population of the Seychelles Magpie Robin Copsychus sechellarum declined from 38–41 birds in 12–13 territories in 1977–1978 to 17–21 birds in eight to nine territories in 1988–1990 and was entirely confined to Fregate Island (210 ha) in the Seychelles. After a successful cat eradication program in 1981–1982, recruitment improved, although the abandonment of agriculture had caused a reduction in the amount of feeding habitat and hence in the carrying capacity of the island. The population declined because of the failure of recruitment to compensate for the annual adult mortality. Foraging activity of the Magpie Robin was greater in high‐quality territories (measured by soil invertebrates available), leading to increased reproductive success. Through supplementary feeding, five times as many recruits were produced. Of the 11.5 potential annual breeding recruits, 5.3 are required to compensate for adult mortality, and the other 6.2 recruits can be regarded as “surplus” contributing to an increase. Magpie Robins prefer to breed in rotten trees, which are a scarce resource. The greater the distance between the nest site and feeding areas, the less time was spent in incubation and nest guarding, resulting in greater egg loss. Because of lack of suitable areas for establishing territories, many young Magpie Robins became “floaters”. Nest disturbance, both by these floaters and by the introduced Indian Mynah Acridotheres tristis, had adverse effects on the breeding success of robins. A recovery plan has been designed to save the Magpie Robin. Territories have been improved for feeding (by tree planting) and for breeding (by providing nestboxes and reducing nest disturbances). Given the vulnerability of one small island, the presence of surplus birds (supported mainly by supplementary food) and the suitability of neighbouring Aride Island (68 ha), successful translocations to this island took place in 1992 and 1994. Given the presence now of 47 individuals on two islands, it is hoped that the species will pull back from the brink of extinction.

MORPHOMETRICS AND BREEDING BIOLOGY OF THE WHITECHINNED PETRELPROCELLARIA AEQUINOCTIALISAT SUB-ANTARCTIC MARION ISLAND

Summary Berruti, A., Cooper, J. & Newton, I.P. 1995. Morphometrics and breeding biology of the Whitechinned Petrel Procellaria aequinoctialis at sub-Antarctic Marion Island. Ostrich 66: 74–80. Aspects of adult morphometrics and the breeding biology of the summer-breeding Whitechinned Petrel at sub-Antarctic Marion Island, southern Indian Ocean, are given, based on a study conducted in 1980/91, along with additional observations on breeding success made in 1990191. It is concluded that Whitechinned Petrels at Marion Island are similarly sized and breed in a similar manner to other studied populations of the nominate race. The eradication of cats at Marion Island in 1991 should now lead to a slow population recovery.

The Seychelles magpie robin Copsychus sechellarum: ecology and conservation of an endangered species

In 1977–1978 some 40 Seychelles magpie robins Copsychus sechellarum, the entire world population, survived on Frégate island. These lived in 12 territorial groups of up to six individuals. Their range on Frégate was limited by the amount of feeding habitat, specifically bare earth and leaf litter which occurred under mature shady woodland and in cultivated vegetable gardens. Two attempts were made to reintroduce the species to Aride Island in 1978 and 1979. These were unsuccessful and the translocations had to be abandoned when a new threat impinged on the parent population of Frégate in 1980. By 1981 numbers there had declined to 18, with virtually no recruitment, and an increase in the feral cat population was implicated. A successful cat eradication programme by trapping and poisoning was carried out in 1981–1982. By 1983–1984 the population showed a recovery with recruitment again healthy, although the abandonment of agriculture on Frégate between 1979 and 1983 had caused a reduction in the amount of feeding habitat and in the carrying capacity of the island to around 25 individuals in eight territorial groups. A range of management options is discussed.

Feral cat eradication of a barrier reef island, Australia

Feral cat eradication of a barrier reef island, Australia