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  • About
  • The Global ETD Search service is a free service for researchers to find electronic theses and dissertations. This service is provided by the Networked Digital Library of Theses and Dissertations.
    Our metadata is collected from universities around the world. If you manage a university/consortium/country archive and want to be added, details can be found on the NDLTD website.
1

The impact of wild dog predation and wild dog control on beef cattle production /

Allen, Lee Robert. January 2005 (has links) (PDF)
Thesis (Ph.D.) - University of Queensland, 2006. / Includes bibliography.
2

Spatial utilisation, habitat selection and population status of the wild dog (Lycaon pictus) population in Hluhluwe Umfolozi Park.

Andreka, Gunther Emil. January 1996 (has links)
The African wild dog (Lycaon pictus) was reintroduced into Hluhluwe Umfolozi Park (HUP) in 1980/81 after an absence of over 50 years. A 'hands off' management approach was applied. Although the reintroduction is regarded as successful, the population has not increased significantly and still only consists of a single pack. Various aspects which may affect this population were investigated to compile an active management strategy. Home range analyses identified extensive use of a home range which covered only 22.7 % of HUP and was situated entirely in Hluhluwe Game Reserve. The extensive movements of the dogs within their home range were primarily dictated by the movements and distribution of their prey species, especially nyala (Tragelaphus angasu) and impala (Aepyceros melampus). Forest habitats were preferred, but all available habitat types were utilised extensively by the wild dogs. Space and habitat were both considered to have no limiting effect on this population and HUP has sufficient space and suitable habitat to support a larger population of L. pictus. A number of potentially pathogenic antigens were identified in the population, indicating that it had been exposed to these at some time. Domestic dogs in the areas surrounding HUP were identified as the most likely source of these diseases which pose a threat to the wild dogs. Some genetic considerations are discussed in terms of their effect on the population status and management of the wild dogs. A number of management proposals based on the results of the project were formulated. It is suggested that an active management approach be adopted for the population. This includes managing it as part of a metapopulation which primarily involves the exchange of genetic material among similar wild dog populations on a regular basis. The immediate supplementation of the population with new genetic material is proposed. / Thesis (M.Sc.)-University of Natal, Pietermaritzburg, 1996.
3

The feeding ecology of the African wild dog Lycaon pictus in Hluhluwe- Umfolozi Park.

Krüger, Sonja. January 1996 (has links)
The small population size of wild dog Lycaon pictus (10) in Hluhluwe-Umfolozi Park (HUP) and the decline in their numbers since 1992, has caused concern for their survival and consideration of further introductions. In the light of many failed wild dog relocation and reintroduction programmes, this study contributes towards an understanding of the ecology of the HUP wild dog pack. Wild dog prey preference was determined from scat analysis and personal observations, and their potential impact on the primary prey species was modelled. The choice of physical habitat features by wild dog and their ranging behaviour within the Park were correlated with the distribution of their primary prey and other predators. To determine the susceptibility of prey to predation in three reserves with different predator diversities and densities, prey vigilance and prey response to playback recordings of predator calls were recorded. The results showed that wild dog preference for females, adult nyala Tragelaphus angasi and juvenile impala Aepyceros melampus, was a function of prey abundance, profitability calculated using a diet choice model, and ease of capture. Based on the overall lack of association of wild dog and their primary prey species and predators, and the overall lack of similarity of wild dog and prey choice of physical habitat features, predator presence was the most important determinant of wild dog ranging behaviour. Prey vigilance differed significantly between reserves and was inversely correlated with predator density. Prey response to predator calls did not differ significantly between reserves but prey did, however, react sooner to those calls unfamiliar to them. Nyala were more vigilant and responded sooner to playbacks than impala suggesting that nyala may experience greater levels of predation pressure. There was no evidence to suggest that the prey preference, habitat preference and ranging behaviour of the wild dog were influenced by the susceptibility of prey to predation. Models of prey population dynamics determined that although the introduction of an additional wild dog pack would result in a reduction of current prey population growth rates and an increase in prey population extinction probabilities, their predicted impact would be slight. Since emigration and population viability were identified as the primary causes of the HUP wild dog population decline, the introduction of two groups of wild dog individuals into Hluhluwe was suggested to boost population numbers and stimulate breeding and dispersal within the Park. The importance of future monitoring and proactive management was stressed to ensure the survival of this valuable species in the Park. / Thesis (M.Sc.)-University of Natal, Pietermaritzburg, 1996.
4

Conserving wild dogs ( Lycaon pictus ) outside state protected areas in South Africa: ecological, sociological and economic determinants of success

Lindsey, Peter Andrew 01 September 2005 (has links)
The restricted geographic range and tenuous conservation status of wild dogs in South Africa were the motivating factors behind this study. Wild dogs have been extirpated from most of their historic range in South Africa, and now occur in three limited distributions: a) one viable population in Kruger National Park; b) a protected meta-population, consisting of 1 packs in six sub-populations (four on state owned reserves – Hluhluwe-Umfolozi Park, Madikwe Game Reserve, Marakele National Park, Pilanesberg National Park, and two on privately owned reserves – Karongwe Game Reserve, and Venetia Limpopo Nature Reserve), and c) ` 76 unprotected individuals in 17 packs and dispersing groups occurring outside protected areas, primarily in the game ranching areas of the extreme north and north east. Prior to the establishment of the proposed transfontier parks, the best prospects for range expansion likely exist on private land. My study investigated some of the ecological, sociological and economic issues associated with wild dog conservation on private land under various scenarios. Over the last few years, the focus of conservation efforts and donor funding expenditure (72.6% of funding) has been the establishment of the meta-population. This been effective – the target size (nine packs) of the meta-population has been exceeded in six years, four years less than the targeted schedule (10 years). From here, there are two ways in which donor funding might be used to achieve further range expansion outside state protected areas, through expansion of the meta-population by reintroducing wild dogs onto private nature reserves, and through the conservation of wild dogs in situ on ranchland. For either strategy, an estimated minimum area of 158.5 km2 is required to support the predation requirements of a pack of 12 wild dogs in northern South Africa, 172.8 km2 in eastern South Africa, and 354.2 km2 in north-eastern South Africa. Private reserve owners may not be willing to accept the costs of predation by wild dogs in the absence of compensation. Compensation for predation ($9,563 - $101,762/year) in addition to the high start up costs of wild dog reintroductions ($36,880) would increase annual donor funding requirements by 1.3 – 4 times, and reduce the cost efficiency of this strategy below that of alternative conservation options. However, there is potential to generate substantial revenue from wild dog-based ecotourism ($11,000 - $60,000/pack/year), and given careful reserve selection, tourism benefits can exceed the costs. Consequently, private reserve owners might be encouraged to reintroduce wild dogs at their own cost. In line with this, the Wild dog Advisory Group-SA has received enquiries from several private reserve owners interested in reintroducing wild dogs onto their properties. The expansion of the meta-population should be limited to state-owned reserves and private reserves willing to carry the costs. There are more wild dogs occurring outside protected areas than previously recognised. Potentially important founder populations occur in game ranching areas in eastern (1-3 resident packs and dispersing groups), northern (1-5 resident packs and dispersing groups) and western Limpopo (1-5 resident packs and dispersing groups), and large areas (88,750 km2) of potentially suitable habitat for range expansion are currently available. Persecution by landowners remains a significant problem, however, and until this is controlled, range expansion is unlikely to occur. Negative attitudes (47.7% of ranchers) are typically based upon perceived or real economic costs associated with wild dogs, and the removal of cost burdens from landowners is the most direct way in which attitudes might be improved. Despite the high annual costs associated with predation by wild dogs on ranchland ($11,942 - $115,761), the low logistical costs ($3,572 initially, and then $15,382 annually thereafter) associated with conserving wild dogs in situ on ranchland render this option more cost efficient than the reintroduction of wild dogs onto private reserves (14-27 packs conserve / $100,000 cf. 3-19 packs / $100,000). Furthermore, tourism revenue from wild dogs has the potential to offset the costs of their predation on ranchland under most scenarios, and promoting the conservation of wild dogs in situ on ranchland by assisting ranchers in establishing wild dog-ecotourism operations should be the focus of future conservation efforts. A substantial proportion of ranchers (52.3%) are positive towards wild dogs, and private landowners are potentially important facilitators in the conservation of the species in South Africa. The focus on future conservation efforts involving wild dogs in South Africa should be to establish wild dog populations in the proposed Limpopo/Shashi and Lubombo transfrontier conservation areas as soon as they are established, to encourage private reserve owners to reintroduce wild dogs at their own expense ,and to promote the conservation of naturally occurring wild dogs in situ on ranchland, by encouraging and assisting ranchers to establish wild dog-ecotourism programmes. / Thesis (DPhil (Zoology))--University of Pretoria, 2006. / Zoology and Entomology / unrestricted
5

Drivers of farmer-African wild dog (Lycaon pictus) conflict in the Waterberg Biosphere Reserve, South Africa

Dube, Lungelo January 2020 (has links)
African wild dogs (Lycaon pictus) are the most endangered large carnivore in Southern Africa. There are as little as 5,000 individuals globally and less than 450 African wild dogs in South Africa alone. African wild dogs are listed as endangered by the International Union for Conservation of Nature (IUCN) Red List. Therefore, the time has never been more crucial to conserve the species. With increased human encroachment and inhabitation in and around protected areas, so are increased conflicts between humans and carnivores. Human-wild dog conflict is likely to rise where a common resource is found. Human-carnivore conflicts have often been induced by the uncomfortably close inhabitation of humans in areas predominantly occupied by large carnivores. For this reason, it is becoming vital to establish a harmonious relationship between carnivores and humans. This research investigated the extent and causes of human-carnivore conflict specific to private landowners and the African wild dog in the Waterberg Biosphere Reserve, Limpopo Province, South Africa between April 2018 and January 2019. The causes of conflict in the Waterberg and levels of tolerance by the farmers for African wild dogs were investigated. The methodology was two-fold, using spatial analyses and an online survey. Three African wild dogs from the same pack were collared using telemetry collars (Tag 2651, Tag 2953 and Tag 3017). These data were used for the spatial analysis part of the research, using Geographic Information System (GIS) to determine the African wild dogs’ home ranges, movement patterns, and proximities to commonalities with humans and preferred land use. The private landowners possibly experiencing human-carnivore conflict were surveyed using an online survey (n = 81), and this information was used to determine the extent of conflict and tolerance of African wild dogs amongst the farmers in the Waterberg. The information gathered will be used by the Endangered Wildlife Trust to develop an early warning system for private landowners affected by the presence of free-roaming African wild dogs in the area. In general, English speaking farmers in the Waterberg Biosphere Reserve were more tolerant of African wild dogs compared with Afrikaans speaking farmers. Results also showed that areas near food and water sources are high potential conflict hotspots. The results also showed that African wild dog movement patterns in Waterberg Biosphere Reserve have an influence on conflict hotspot areas during denning season, wet and dry months, different phases of the moon, and overall hunting patterns of African wild dogs. This research facilitated an understanding of aspects of utilisation, persecution, and how to mitigate conflict between humans and African wild dogs within the Waterberg Biosphere Reserve. / Dissertation (MSc (Environment and Society))--University of Pretoria, 2020. / GreenMatter Fellowship Mapula Trust Endangered Wildlife Trust (EWT) National Research Foundation (NRF) / Geography, Geoinformatics and Meteorology / MSc (Environment and Society) / Unrestricted
6

Contribuição ao estudo da história natural do cachorro do mato, Cerdocyon thous, e do cachorro vinagre, Speothos venaticus / Contribution to the study of the natural history of the crab-eating fox, Cerdocyon thous, and the bush dog, Speothos venaticus

Beisiegel, Beatriz de Mello 04 February 2000 (has links)
O objetivo deste projeto foi descrever a ecologia comportamental e a ontogênese do comportamento social de um grupo de Speothos venaticus, o único pequeno canídeo que caça em grupos, em uma área de Mata Atlântica no Estado de São Paulo, o Parque Estadual Carlos Botelho. Os cursos de água da área de estudos foram percorridos em busca de cachorros vinagre, seus indícios ou tocas, foram colocadas iscas para atrair os animais e foi feita “tocaia" nos locais onde estes foram vistos ou seus indícios encontrados. Devido à dificuldade de localização de um grupo de cachorros vinagre após 17 meses de trabalho no campo, o projeto foi ampliado para incluir o estudo comparativo dos mesmos aspectos em Cerdocyon thous, espécie filogeneticamente próxima a Speothos mas com características ecológicas e comportamentais muito distintas. Esta espécie foi estudada através de rádio-telemetria, análise de fezes e observações ad libitum. A dificuldade de localização de Speothos venaticus no PECB pode ser atribuída à grande extensão da sua área de uso ou a possíveis hábitos nômades. A área de uso do cachorro do mato foi estimada em 382,5 ha pelo MPC e 999,1 ha pelo Kernel Adaptativo. Sua dieta é onívora e varia sazonalmente. Os cachorros do mato no PECB não são estritamente noturnos como em outras áreas onde foram estudados, provavelmente devido à temperatura mais baixa e menor presença humana. / The aim of this project was to describe the behavioral ecology and the ontogeny of the social behavior in a group of Speothos venaticus, the only small canid that hunts in groups, in an Atlantic Forest area in the state of São Paulo, the Parque Estadual Carlos Botelho. The streams and rivers of the study area were searched for bush dogs or their tracks and for their dens, baits were placed to attract the animals and we waited for their passage in hides near the sites where they were seen before or where their tracks were found. Because of the difficulty to find the bush dogs even after 17 months of field surveys, the aim of the project was broadened to include the comparative study of the same aspects in Cerdocyon thous, a species phylogenetically close to Speothos but with very distinct ecological and behavioral characteristics. This species was studied through radio telemetry, scat analysis and ad libitum observations. The difficulty to find a Speothos venaticus group in the PECB can be attributed to their large home range or possibly to nomadic behavior. The MCP estimate of the crab-eating fox’s home range was 382.5 ha and the Adaptive Kernel estimate was 999.1 ha. These animals are omnivore and their diet differed between seasons. Crab eating foxes were not totally nocturnal in PECB, as they are in other areas where they have been studied, probably because of the lower temperatures and less human disturbance at PECB.
7

Contribuição ao estudo da história natural do cachorro do mato, Cerdocyon thous, e do cachorro vinagre, Speothos venaticus / Contribution to the study of the natural history of the crab-eating fox, Cerdocyon thous, and the bush dog, Speothos venaticus

Beatriz de Mello Beisiegel 04 February 2000 (has links)
O objetivo deste projeto foi descrever a ecologia comportamental e a ontogênese do comportamento social de um grupo de Speothos venaticus, o único pequeno canídeo que caça em grupos, em uma área de Mata Atlântica no Estado de São Paulo, o Parque Estadual Carlos Botelho. Os cursos de água da área de estudos foram percorridos em busca de cachorros vinagre, seus indícios ou tocas, foram colocadas iscas para atrair os animais e foi feita “tocaia” nos locais onde estes foram vistos ou seus indícios encontrados. Devido à dificuldade de localização de um grupo de cachorros vinagre após 17 meses de trabalho no campo, o projeto foi ampliado para incluir o estudo comparativo dos mesmos aspectos em Cerdocyon thous, espécie filogeneticamente próxima a Speothos mas com características ecológicas e comportamentais muito distintas. Esta espécie foi estudada através de rádio-telemetria, análise de fezes e observações ad libitum. A dificuldade de localização de Speothos venaticus no PECB pode ser atribuída à grande extensão da sua área de uso ou a possíveis hábitos nômades. A área de uso do cachorro do mato foi estimada em 382,5 ha pelo MPC e 999,1 ha pelo Kernel Adaptativo. Sua dieta é onívora e varia sazonalmente. Os cachorros do mato no PECB não são estritamente noturnos como em outras áreas onde foram estudados, provavelmente devido à temperatura mais baixa e menor presença humana. / The aim of this project was to describe the behavioral ecology and the ontogeny of the social behavior in a group of Speothos venaticus, the only small canid that hunts in groups, in an Atlantic Forest area in the state of São Paulo, the Parque Estadual Carlos Botelho. The streams and rivers of the study area were searched for bush dogs or their tracks and for their dens, baits were placed to attract the animals and we waited for their passage in hides near the sites where they were seen before or where their tracks were found. Because of the difficulty to find the bush dogs even after 17 months of field surveys, the aim of the project was broadened to include the comparative study of the same aspects in Cerdocyon thous, a species phylogenetically close to Speothos but with very distinct ecological and behavioral characteristics. This species was studied through radio telemetry, scat analysis and ad libitum observations. The difficulty to find a Speothos venaticus group in the PECB can be attributed to their large home range or possibly to nomadic behavior. The MCP estimate of the crab-eating fox’s home range was 382.5 ha and the Adaptive Kernel estimate was 999.1 ha. These animals are omnivore and their diet differed between seasons. Crab eating foxes were not totally nocturnal in PECB, as they are in other areas where they have been studied, probably because of the lower temperatures and less human disturbance at PECB.
8

Is the grass greener on the other side? : testing the ecological trap hypothesis for African wild dogs (Lycaon pictus) in and around Hwange National Park / L'herbe est-il plus verte de l'autre côté? : un test de l'hypothèse de piège écologique pour les lycaons (Lycaon pictus) dans et autour du parc national de Hwange

Van Der Meer, Ester 27 May 2011 (has links)
Lorsque des animaux montrent un choix préférentiel pour un habitat à effet puits, on dit alors qu’ils sont capturés par un piège écologique. La sélection de l’habitat est bénéfique dans les systèmes classiques de type source-puits, puisque les animaux vivant dans des habitats de haute qualité (natalité>mortalité), choisissent de migrer vers des habitats de faible qualité (natalité<mortalité), uniquement lorsqu’il n’y a pas suffisamment d’habitat de haute qualité disponible. A l’intérieur d’un habitat de type piège écologique le choix est dangereux, et peut conduire à l’extirpation rapide d’une espèce, puisque les animaux vivant dans des habitats de haute qualité choisissent de migrer vers des habitats de faible qualité, même lorsqu’il y a suffisamment d’habitat de haute qualité disponible. Les pièges écologiques ont lieu lorsque des changements naturels ou induits par l’homme se produisent rapidement et que des déterminants de la sélection de l’habitat qui étaient alors sélectionnés deviennent trompeurs, entraînant des choix d’habitats inadaptés de la part des animaux. Pour distinguer un habitat de type puits d’un piège écologique, des connaissances complémentaires sont nécessaires, sur la relation entre les préférences d’habitat et la qualité de l’habitat. Dans l’écosystème de Hwange, les lycaons semblent baser le choix d’habitat sur les déterminants écologiques améliorant la fitness. Ils ont une meilleure efficacité de chasse dans la zone tampon à l’extérieur du parc national de Hwange, une compétition moindre avec les lions et avec les hyènes, ainsi qu’un meilleur accès à des sites de terrier. En conséquence, à l’extérieur du parc national, les lycaons donnent naissance à des portées de chiots plus grandes. Cependant, la mortalité induite par l’homme, en raison de l’effet lisière, est si grande qu’elle excède la natalité. Néanmoins, du fait qu’ils sont incapables de juger avec justesse de la qualité de l’habitat, en intégrant la mortalité induite par l’homme, les lycaons font un choix d’habitat inadapté, et ils se déplacent vers le puits de mortalité, à l’extérieur de la sécurité de l’aire protégée. En d’autres mots, les lycaons de l’écosystème de Hwange sont capturés par le piège écologique, que constitue la zone tampon située à l’extérieur du parc national de Hwange. / When animals show a preferential choice for sink habitat they are said to have been caught in an ecological trap. Habitat choice behaviour is beneficial in classic source-sink systems, as animals living in high quality habitat (natality>mortality) only choose to migrate into low quality habitat (natality<mortality) when there is not enough high quality habitat available. Within an ecological trap habitat choice is detrimental and can lead to rapid extirpation of a species, as animals living in high quality habitat choose to migrate into low quality habitat even when there is enough high quality habitat available. Ecological traps occur when sudden natural or human induced changes cause formerly reliable settlement cues to be no longer associated with an adaptive outcome, causing animals to make a maladaptive habitat choice. To be able to distinguish a sink from an ecological trap additional knowledge of the relationship between habitat preference and habitat quality is required. Within the Hwange system African wild dogs seem to base their habitat choice on the right fitness enhancing ecological cues. They experience a higher hunting efficiency in the buffer zone outside Hwange National Park, less competition with lions and spotted hyenas and a better access to suitable den sites. As a result African wild dogs outside the National Park give birth to larger litters of pups. However, due to an ‘edge effect’, human induced mortality in the buffer zone is so high it exceeds natality. African wild dogs nevertheless make a maladaptive habitat choice and move into the mortality sink outside the safety of the protected area as they are unable to judge habitat quality accurately by taking this human induced mortality risk into account. In other words, African wild dogs in the Hwange system are caught in an ecological trap in the buffer zone outside Hwange National Park.

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