The Feasibility of Reintroducing African Wild Dogs (Lycaon Pictus) Into the Great Fish River Nature Reserve, Eastern Cape, South Africa

The Feasibility of Reintroducing African Wild Dogs (Lycaon Pictus) Into the Great Fish River Nature Reserve, Eastern Cape, South Africa

The feasibility of reintroducing African wild dogs (Lycaon pictus) into the Great Fish River Nature Reserve, Eastern Cape, South Africa. A thesis submitted in fulfilment of the requirements for the degree of MASTER OF SCIENCE of RHODES UNIVERSITY By SAMANTHA KARIN PAGE February 2014 Abstract With a declining population of roughly 3000-5000 individuals in Africa, African wild dogs (Lycaon pictus) are one of the most endangered carnivores in the world. As the global human population expands, it is becoming increasingly unlikely that large portions of land will be set aside for conservation, especially in developing countries. Thus, recent wild dog conservation efforts in South Africa have concentrated on establishing a managed metapopulation. A metapopulation is a group of geographically isolated subpopulations of a species that are managed (using supplementation and harvesting) to mimic natural gene flow. The Great Fish River Nature Reserve (GFRNR) in the Eastern Cape Province of South Africa has been identified as a potential reserve to become part of the national wild dog metapopulation. My research aimed to conduct a feasibility assessment of the long-term (~ 25 years) success of a wild dog reintroduction into the GFRNR. This assessment included biological modelling of wild dogs and their expected prey, and determining the potential anthropogenic threats to wild dogs on the private and communal land surrounding the reserve. I used VORTEX population modelling and determined that the GFRNR is likely to have a wild dog carrying capacity of ~22 individuals. Using a 25-year modelling simulation, the most appropriate wild dog reintroduction scenario would be to reintroduce six females and four males initially and supplement the population with one female and two males in years 3, 10, 15 and 23. In addition, the harvesting/removal of one male and one female in years 10 and 20 would be required to ensure 100% population persistence and adequate genetic diversity. Kudu (Tragelaphus strepsiceros) and bushbuck (Tragelaphus scriptus) are expected to be the two most important prey species for reintroduced wild dogs in the GFRNR. Furthermore, wild dogs are likely to prefer the north-western and south-western sectors of the reserve because of the relatively high prey densities in these areas. However, regular monitoring of both the potential prey and the wild dog populations is essential to ensure persistence of the wild dogs and to prevent prey populations decreasing precipitously. Using structured questionnaire interviews (n = 128), I found that while neighbouring land owners and local communities were generally positive about the potential wild dog reintroduction (56 % of all respondents), several threats to wild dogs were identified along the reserve boundary and on the adjoining unprotected land. Some private landowners and members of rural communities around the reserve (34 %) stated that they would kill any wild dogs that dispersed onto their land. In addition, some respondents (8 %) admitted to believing i in traditional uses for wild dog products (e.g. fur) which could result in the illegal killing of wild dogs outside of the GFRNR for traditional purposes. Poaching and the presence of unvaccinated domestic dogs on neighbouring land were also identified as being potential threats to a reintroduced wild dog population. However, such anthropogenic threats appear to be localised to the western and southern boundaries of the reserve. Therefore, by implementing preventative measures (such as anti-snare collars, anti-poaching patrols and vaccination against rabies and canine distemper) the likelihood of such threats occurring can be reduced. I conclude that the GFRNR can sustain a population of wild dogs and successfully contribute to South Africa‘s national metapopulation. An additional reserve will benefit the country‘s metapopulation by increasing the number of wild dogs available for translocation, thereby increasing genetic diversity and overall resilience (to environmental change, disease etc.) of South Africa‘s wild dog population. This will contribute towards the future conservation of this endangered species. ii Table of Contents Abstract.......................................................................................................................................i Table of contents.......................................................................................................................iii Acknowledgements....................................................................................................................v CHAPTER 1: Introduction…………………………………………………….……………1 1.1. Physical description 1 1.2. Taxonomy 2 1.3. Dispersal behaviour 3 1.4. Social behaviour 3 1.5. Reproduction. 4 1.6. Conservation status 6 1.7. Wild dog history in Africa and causes for their decline 6 1.8. The managed metapopulation conservation strategy 11 1.9. Wild dogs in the Eastern Cape Province 13 1.10. Motivation for the study 14 CHAPTER 2: Study Site……………………………………………………………………15 2.1. Location 15 2.2. Surrounding land use 15 2.3. Site description and history 16 2.4. Topography and geography 19 2.5. General climate 20 2.6. Vegetation units 22 2.7. Predator and prey populations 26 2.8. Management of the GFRNR 27 CHAPTER 3: The biological pre-requisites for an African wild dog reintroduction into the Great Fish River Nature Reserve, Eastern Cape, South Africa……………………..28 3.1. Introduction 28 3.2. Methods 34 iii 3.3. Results 44 3.4. Discussion 55 CHAPTER 4: The socio-demographic environment surrounding the Great Fish River Nature Reserve and how this relates to a potential African wild dog reintroduction……………………………………………………………………………….62 4.1. Introduction 62 4.2. Methods 69 4.3. Results 77 4.4. Discussion 98 CHAPTER 5: Synthesis……………………………………...……………………………109 CHAPTER 6: References……………………………………………………………..…..114 APPENDICES………..……………………………………………………………………129 Appendix A (VORTEX simulations) 129 Appendix B (Questionnaire) 131 Appendix C (The questions and scoring system used to determine the threat index) 140 iv Acknowledgements The contributions of the following organisations and individuals to this research are gratefully acknowledged: o To my supervisors, Dr Dan Parker and Dr Harriet Davies-Mostert, I am truly grateful for all your advice and guidance through this project. To Dan who reviewed each chapter countless times and to Harriet for helping me understand VORTEX and biological modelling. o To Dr Dean Peinke, all your help from stage one of this project made this research possible. With luck you will get your wild dogs soon. o To everyone at Eastern Cape Parks and Tourism Agency who helped with community surveys, especially Zimasa Gibisela, Nomatile Nombewu, Ntokozo Tembe, Zezetu Mnqetha, Nobendiba Shiyani and Melikhaya Pongolo. o Thanks to Gavin Shaw and Cathy Dreyer for all the help and fun you have provided this year. I hope in the next year you both have some wild dogs to run after (and I hope they won‘t provide you with too many grey hairs). o Thank you to Sirion Robertson for proof reading. [Pleasure! – S.R.] o Brendan Whittington-Jones for countless reviews of chapters and helping me sort through methodology. o The land owners who took the time to meet with me and complete these questionnaires, and the community members who were all so eager to learn more about these wonderful animals. o For financial support: The National Research Foundation (NRF) and Eastern Cape Parks and Tourism Agency. v o Thank you to Megan Murison who always trekked into the field with me (regardless of the time). You really made field work an incredible amount of fun. And an extra thank you for always driving safely! o The Zoology Master‘s class of 2013... Some of us have been together since 2009; what a wonderful journey it has been. I wish you all the best for years to come. o To Bryan Nicholson, thank you for the past 5 years, for always encouraging me and for all your love and support. o To my amazing friends, Sam Waterworth, Sam Humby, Kyra Lunderstedt, Tam Perks and Amy Pretorius. All your support and love helped me do this in a year. o And the biggest thank you goes to my family, who never stopped encouraging me. I never could have done this without you all. vi CHAPTER 1: General Introduction 1.1. Physical description African wild dogs (Lycaon pictus), also known as the painted hunting dog, are medium-sized, slightly-built carnivores, averaging 67 -78 cm in shoulder height and weighing approximately 20-25 kg (Vucetich & Creel 1999; Creel & Creel 2002). Males are generally three to seven percent heavier than their female counterparts (Creel & Creel 2002). They have several features which make them distinguishable from other African carnivores (Figure 1.1). Firstly, wild dogs have large, round, black ears which gives them excellent hearing and assists in thermoregulation (Estes 1993). Secondly, their coat patterns are individually unique, allowing them to differentiate easily between members of their pack. Their coats are a combination of mottled black, white and tan (Estes 1993; Creel & Creel 2002). Thirdly, their faces are a black and brown, with a black line extending up the face and along the sagittal crest and there is no white on the head (Estes 1993). Finally, their tails are bushy and are predominantly white. This is suggested to assist with maintaining visual contact within the pack (Creel & Creel 2002). Figure 1.1: African wild dogs (Lycaon pictus) have unique physical features which make them easy to distinguish from other African

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