Throughout the world, tourism is booming and South Africa, like many developing countries, has a phenomenal resource base for tourism that includes unspoilt wilderness areas, varied and impressive scenery, accessible wildlife, good weather conditions, cultural diversity, as well as an increasingly developed infrastructure. South Africa though is mainly seen and experienced by international tourists and a small number of privileged locals and therefore, South Africa's full potential in local tourism has not been realised. In 2000, the World Bank financed a quantitative research project on Nature Tourism and Conservation in South Africa to assess the domestic tourism market. This study found that there might be a latent unrealised demand for nature tourism among the African and Indian population. It was this broader finding that prompted this study. Information for this study was gathered through household surveys and a two-week on-site survey in a game reserve. Three sets of participants were chosen to participate in this qualitative study. These were African youth (age 18 to 26 years), African adults (>30 years old) with children and finally Indian couples (aged < 30 years). Participants were also chosen based on their current income level or potential incomes once they leave university. In this case, only the middle to upper income group was targeted. All three groups participated in pre field focus groups and a select group were taken to the HluhluwelUmflozi Game Reserve for three days where additional focus groups were held. The methodology also encompassed a literature review, telephonic interviews and field observations. Information gathered during this study was used to understand the reasoning behind the vacation trends of middle to upper income Africans and Indians and to develop a marketing strategy to be used to attract other Africans and Indians to the game reserves of South Africa. The study found that there is a latent unrealised demand for nature tourism among the middle to upper income Africans and Indians. The vacation trends among Africans and Indians are also very similar in that those with families prefer to vacation in large groups cons isting of both friends and families. It was also found that their past vacation destinations included mainly built up, urban areas and that both the African and Indian participants had great misconceptions regarding game reserves. These misconceptions formed part of the reasons for them not vacationing at game reserves. With regards to an advertising strategy, the study found that current advertising strategies are not working. Participants were encouraged to come up with advertising strategies that would entice other middle to upper income African and Indian families to vacation at game reserves. The participants recommended the use of television, cinema, radio , and newspaper advertisements; as well as the use of brochures and competitions to encourage vis itation. Included in their detailed view of how each strategy should play out, they recommended that when developing advertisements and brochures, it is imperative that African and Indian models are used in the adverts. The current advertising only makes use of white models and this discourages potential African and Indian tourists. / Thesis (M.Dev.Studies)-University of Natal, Durban, 2003.

Kenya has one of the oldest and most developed national park and reserve systems among developing nations in Africa. Kenya's ecosystems have felt the impact of tourists, from big game hunters to photographic safaris, for over a century. This project contains the research on which the author intends to base a future book about Kenyan ecoturism for the general public.

Eco-tourism activities specifically, sometimes have very negative environmental impacts. One such activity which has been observed to have severe negative impacts is driving in dirt tracks (ungravelled natural soil) by game drive vehicles in private game reserves and some National Parks (Nortjé 2005; Laker 2009). It has also been observed that the severity of the impacts and the resilience (recovery potential) of the affected areas differ widely between different areas. It is strongly linked to the properties and qualities of different soils. This study has shown that off-road driving (ORD) has the same effects, and to a greater extent, if it is not well managed and judiciously controlled. Wild animals tend to concentrate in areas with the most nutritious en most palatable vegetation. Consequently these are also the areas where predators, e.g. lion, leopard and cheetah are most likely to be found. It can be expected that these will be the areas with the highest frequencies of ORD in order to get close to these animals. In many landscapes these are the areas which are the most vulnerable to negative impacts by actions like ORD and have the lowest resilience. It has also been observed during game drives and personal communications at several occasions that there is tremendous ignorance amongst tourists regarding the negative environmental impacts of certain activities. This study proved that ORD have strong negative impacts on vegetation recovery, soil resilience and root density distribution through soil crusting and sub-soil compaction. An important finding is that these negative impacts are during both dry and wet soil conditions. Game drive vehicles driving off-road damages the surface soil structure, which lead to soil crust formation and sub-surface compaction. A highly significant result is that most crusting and sub-soil compaction occurred during the first pass of the game drive vehicle, irrespective of the soil type and tyre pressure, thus rewriting the current guidelines for ORD of the South African National Parks, SANParks. Furthermore, results of this study indicated that a significant area in the flood plains of the Makuleke Contractual Park is impacted by ORD. The impacts are serious if one looks at the amount of land that an ORD vehicle can disturb. One of the recommendations would thus be to drive in the same tracks when driving off-road, and lower the tyre pressures. Driving in the same tracks is known as "controlled-traffic" in the agricultural industry. Controlled traffic is very important to minimize compaction. Driving in the same University of Pretoria etd Nortjé, G.P. (2013) tracks during off-road incidents does not significantly affect the degree of compaction under the tracks, but greatly reduces the compacted area. Further results indicated a strong lateral effect of the vehicle tracks, in most cases the whole area between the two tyre tracks as well as up to a distance outside of the vehicle tracks, thus increasing the total area disturbed by ORD. Comparing these vehicle impacts with animal path resulted in some important findings. Animals only caused a soil crust with soil strength values much lower than that of vehicles. The effects of animals are also much more vertical than lateral as with vehicles. Another important finding is the role that historical human activities play in such study areas and how it may influence results. The results in this study are aggravated by the historical human activities in this study area, as indicated. These historical activities were the main cause of the surface crusting, and the resultant low vegetation growth in the area. This, therefore, explains partially the relatively high control values and also the soil’s higher susceptibility to compaction due to vehicle ORD. The root density trials had very interesting and important results. Significant differences occurred between mean root density fractions across all tyre pressures at all three trial sites. The trend is that an increase in tyre pressure causes a decrease in root density distribution. These results show clearly that even lower tyre pressures are harmful, but are more environmental friendly than higher tyre pressures. Results of the second part of the study with regards to tourists' perceptions on ORD, and the impact of their activities on the environment, showed that the majority of tourists areignorant when it comes to the impacts of their activities on soil and vegetation. Tourists' had significantly variable demographic characteristics. Tourists' environmental perceptions varied, but a significant majority of tourists agreed that ORD has a negative impact on the environment. Contradictions exist between what they know or perceive as being damaging and what they prefer to act on. Results indicate a need for improved visitor education on the possible negative impacts of demands for ORD, and a need for government intervention with regards to the enforcement of legal measures to control ORD. The results also indicate that game guides and tourism operators can play a major role in educating the tourists. The results demonstrate that both an understanding of the chemical and physical factors influencing soil compaction, as well as tourists' environmental views are important in formulating a management strategy to control and manage these impacts. / Thesis (PhD)--University of Pretoria, 2014. / gm2014 / Animal and Wildlife Sciences / unrestricted

A research report submitted to the Faculty of Science, in partial fulfilment of the requirements for the degree of Master of Science in Environmental Science, University of the Witwatersrand, Johannesburg, 2015. / Wildlife conservation and management requires an in-depth understanding of the demographics and dynamics of the population concerned to enable sound management decisions. Yet it is often very challenging to obtain reliable information of cryptic and highly migratory species. I used photo identification and capture-recapture methods to study the population of nyala, a highly secretive species, in the Umkhuzi game reserve. The nyala species is individually identifiable by the mark pattern on their body. Photographs used for this project were taken at a waterhole in Umkhuzi game reserve between June 23rd and 01 July 2014, representing nine sampling occasions. Identification of individuals was achieved with a computer-assisted technique using open source pattern identification software called Wild-ID version 1.0.1. A total of 652 photographs were taken at the sampling site and from these pictures wild-ID identified 372 distinct animals. An encounter history for each individual during the nine sampling occasions was also produced using Wild-ID. The encounter histories of all individuals were entered into Program MARK. I used the closed population models in Program MARK to obtain population estimates. Program MARK indicated that Mh was the most appropriate model to fit this data as indicated by the AICc ranking. Mh showed population estimates as follows: adult males: 111.90 ± 16.07, adult females: 298.01 ± 36.66; young adult males: 21.33 ±19.34; juvenile males: 37.15 ±16.84; yearling males: 37.73 ±8.51; yearling females: 96.48 ±22.75 and juvenile unidentified: 69.03. ±28.96 Closure test performed to ascertain demographic and geographic closure during the sampling period showed a χ2= 21.74, p= 0.08, df = 14, for the Stanley & Burnham test and a p and z-values of 0.06 and -1.51 respectively for the Otis et al test. These results shows marginal violation of population closure, nevertheless closed population models were used to estimate population abundance due to the fact the violations are marginal and the sampling period iii was very short, nine days. The study revealed that there is as much as twice the number of females compared to males.

Balancing increasing elephant numbers with biodiversity conservation in small reserves has become a concern for many protected area managers. Elephants are considered important agents of disturbance creating heterogeneity and thus contributing to the maintenance of biodiversity. However elephants also damage vegetation through their destructive feeding habits, and this has led to pressure to reduce elephant populations in many reserves. Quantitative data on the impact of elephants on invertebrates, the main component of biodiversity at the species level, are lacking. The aim of this project was to assess the effect that habitat alteration by elephants has on the diversity of selected ground-dwelling invertebrates (ants, centipedes, millipedes, spiders, scorpions and termites) through the provision of logs and dung as a potential refuge niche for these invertebrate communities, and to determine the effect of spatial (vegetation types) and temporal (season and age of dung) variation on the invertebrates using these refugia. Variation in impacts was considered important because savanna is not homogenous and the impact of the refugia is likely to be dynamic in terms of seasonal trends in invertebrate populations, and in terms of changes in the environmental conditions offered by the refugia. Elephant impact on vegetation, quantity of refugia (logs and dung) produced and invertebrate diversity associated with refugia were determined for 115 transects within Madikwe Game Reserve in the North Western Province, South Africa. Invertebrate abundance, species richness and diversity were always higher under refugia than in areas without refugia. Vegetation utilisation, frequency of refugia production and invertebrate diversity showed strong temporal variation (seasonal); elephant impact and production of logs were higher in winter than in summer because elephants are more likely to feed on woody vegetation in winter when grass nutrient levels are low. Invertebrate diversity under the logs was higher in summer than in winter, and this probably reflected the higher abundance and diversity of invertebrates that are usually associated with the warmer, wetter summer months. The effect of adding refugia to three vegetation types on invertebrate diversity was tested experimentally at Makalali Private Game Reserve in the Limpopo Province, South Africa. Logs and elephant dung were set out in five plots each measuring 20m x 20m within Govender - iii mixed bushveld, riverine and mopane woodland. Significant differences were observed in invertebrate abundance, species richness and diversity between the refugia and control plots that lacked refugia and between the three vegetation types sampled. Similarity between invertebrate communities utilising the different refugia types and between the three different vegetation types were tested using the Jaccard similarity coefficient. The three vegetation types shared fewer than 50% of their species, as did the logs, dung and control sites. However the results obtained do illustrate a higher degree of similarity between the refugia substrates (logs and dung) than the control sites and between the more heterogeneous vegetation types (mixed bushveld and riverine) than the mopane veld. This indicated that invertebrate communities associated with refugia were not uniform, but were influenced by vegetation type. An experimental test of temporal changes in invertebrate community composition illustrated the importance of elephant dung as a microhabitat for different invertebrate groups over different ages of dung (three days, two, four, 12 and 32 weeks old). Colonisation of the dung, by dung beetles was immediate but as the microclimate of the dung changed with time, the new conditions were ideal for other invertebrate taxa. Over a period of eight months, the change of invertebrate communities utilising the dung included dung beetles, followed by millipedes and [mally ant and termite communities. The results of this study illustrated the importance of refugia (logs and dung) produced by elephants for ground-dwelling invertebrate species in the savanna environment. The extent of the influence of the refugia varied both spatially and temporally and this should be considered in future monitoring or in measuring impacts. While further research on a broader range of organisms and at larger scales is necessary, elephants do have a positive impact on at least some components of biodiversity, through the process of facilitation of refugia. / Thesis (M.Sc.)-University of KwaZulu-Natal, Pietermaritzburg, 2005.

In many parts of South Africa, a growing trend to convert traditional commercial agricultural farms to wildlife-based forms of land use is having significant but largely unexplored impacts on farm dwellers and neighbouring rural communities. This trend is very evident in the province of KwaZulu-Natal where there has been a significant shift in rural landscapes as land is being “rehabilitated”, from commercial cattle farming in particular, and developed into Private Game Reserves (PGRs). This research forms part of a larger project funded by Southern African Programme for Alternatives in Development (SANPAD). One of the research partners was the Association For Rural Advancement (AFRA), an independent Non-Governmental Organisation working on land rights and agrarian reform in KwaZulu-Natal, South Africa. AFRA‟s work focuses on black rural people whose rights to land have been undermined, whose tenure is insecure, and who do not have access to sufficient land to fulfil their development aspirations or their basic needs. Very little research has, however, been conducted on the large shift in land use in northern KwaZulu-Natal and how rural communities are being impacted in these areas; a situation this study intends to begin to remedy. This study focuses on the north-eastern area of the province, and in particular the Mkuze region, where the move to create PGRs has significantly changed the social and physical geography of the area. In order to gain a clearer understanding of this phenomenon, research was conducted on the relationship between the tribal/ traditional community of Ingwenya and five surrounding game reserves (namely, Thanda/ Intibane, Mkuze, Phinda, and Kube-Yini). While Mkuze is a state game reserve, created in the early twentieth century, the others are PGRs. The study was both quantitative and qualitative in nature which involved collecting household questionnaire surveys in the community of Ingwenya, in-depth interviews with ex-farm dwellers, questionnaire surveys with the managers of the five PGRs chosen in this study, oral and documentary evidence and participant observation. / Thesis (M.Soc.Sc.)-University of KwaZulu-Natal, Durban, 2011.

Thesis (M.Sc. (Statistics)) - Rhodes University, 2007. / A thesis submitted in partial fulfilment of the requirements for the degree of Master of Science.

Five lions were reintroduced to the Welgevonden Private Game Reserve in 1998. These lions were studied to increase the limited knowledge of the ecology of reintroduced lions on small wildlife reserves, and to provide baseline data to the reserve management from which to develop management decisions. In the past, reintroduction attempts of felids have often failed because the animals failed to establish ranges in the new environment. During the current study, homing behaviour and range establishment of the reintroduced lions were studied and used as an indication of the success of the reintroduction attempt. The ease with which lions on Welgevonden established ranges indicated that they did not experience problems with adapting to their new environment The population dynamics of the reintroduced lion population were investigated. The population grew rapidly due to early breeding and short inter-litter intervals. The collected data were used to model the lion population using VORTEX population modelling software. Various potential management strategies to reduce the population growth were also modelled and discussed. The feeding ecology and predation patterns of the reintroduced lions• were investigated to give an indication of the predator-prey relationships on Welgevonden. These data were used in a model that investigated the effect of lion predation on the various prey populations of Welgevonden. The model was also used to test the influence of other factors on the prey populations, as well as the number of killing lions that can be supported by the prey population. The study has shown that reintroduction can be used successfully to establish a lion population on a small game reserve, but that certain management actions will increase the chances of success. However, continual monitoring and management will be necessary to ensure the long-term viability of the lion and prey populations. <p. / Dissertation (MSc (Wildlife Management))--University of Pretoria, 2006. / Centre for Wildlife Management / unrestricted

This thesis explores human-wildlife interactions under community managed game parks. The thesis consists of an introductory chapter, study location chapter and four self-contained studies based on different samples from created clusters surrounding Nyatana Game Park, which make up the rest of the thesis chapters. Chapter one presents an introductory overview of wildlife management in Zimbabwe, specifically looking at human-wildlife interactions under CAMPFIRE projects, welfare dynamics and conservation implications for the surrounding communities who share boundaries with community-managed game parks. The chapter concludes by highlighting the challenges facing community-based wildlife conservation in Zimbabwe as well as the key concepts that will be the subject of the rest of the thesis. Chapter two presents the study location; it highlights the road map to the study area, starting with the provincial location, and indicates the specific districts from which respondents were selected. A brief agro-ecological summary of the study area is also presented; it looks specifically at climate, vegetation and a demographic data of the study area. Chapter three: Can game parks be trusted as livelihood sources? To answer this topical question, Chapter three explores livelihood adaptation strategies for households who share boundaries with Nyatana Game Park. Most of the community managed game parks, under CAMPFIRE principles in Zimbabwe, were established with the primary objective of generating revenue for the surrounding communities; this was done in the hope of using positive returns from game farming to promote the conservation of wildlife. Has this materialised in practice? Descriptive results from this study seem to suggest otherwise, where mixed farming and gold panning were the major livelihood adaptation choices reported by most households. The revenue from game farming was reported to be too low and inconsistent, to such an extent that the majority of the community regarded it as risky and unreliable. A multinomial logistic regression model for correlates of adaptation choices indicated that access to credit, markets, and extension may be some of the current institutional constraints inhibiting households from accessing off-farm sources for their livelihoods. In addition, household size, gender and age may enhance the adaptive capacity of households to move out of risky crop faming into other off-farm portfolio diversifications. The study, therefore, suggests that game parks, according to the evidence uncovered by the study, may not be trusted as a reliable and sustainable livelihood source. If local communities who share boundaries with game parks do not view them as reliable and sustainable livelihood sources, as concluded in Chapter three, how can they (local communities) be trusted to conserve them? To assess their perceptions of game parks, Chapter four presents a multinomial logistic regression model for perceptions of society on game parks using the African elephant as a typical example. The results suggest that Problem Animal Control (PAC) perceptions, livestock predation and issues of low and poor revenue distribution may be some of the critical perceptions capable of influencing surrounding communities to negatively participate in the conservation of wildlife. The results further suggest that using wildlife proceeds to finance observable local common pool infrastructure may positively influence the surrounding communities to conserve wildlife. The chief conclusion regarding game parks, therefore, was that the surrounding communities were in favour of the obliteration pathway, although minimal conservation perceptions were also available. Given the negative conclusions regarding game parks, as suggested in Chapters three and four, citizens would then wonder if any meaningful hope for community managed game parks exists. Chapter five probes the buffer zone livelihood link under community managed game parks, using evidence from the Nyatana Game Park. The binary logistic regression model results, for buffer zone participation and resource extraction combinations by surrounding communities, suggest that resource extraction may be market driven rather than focussing on domestic consumption. The study therefore concludes that the buffer zone livelihood link as currently practiced, though potential, may fail to address the livelihood expectations of the sub-district producer communities. The study therefore calls for extreme caution whenever the buffer zone livelihood link is considered, because several institutional and design conflicts exist within this dynamic. In Chapter six, the study further probed the buffer zone income dynamics for the sub-district producer community. The results of descriptive statistics suggest that the contribution of buffer zone activities to household income may be significant with a positive correlation to household agricultural income for communities who reside inside or close to the park (primary sub-district producer community). Using the Gini decomposition approach and Lorenz curves, the study concluded that a buffer zone income may be capable of contributing to more equally distributed incomes for rural communities who share boundaries with game parks. With respect to the correlates of household income, the results suggest that household size and age may negatively influence income from buffer zone activities, while gender may have a positive effect. This was also true for education and Livestock Units (LUs) with respect to income from self employment; the former positively and the latter negatively related. The results further suggest that land size may also be positively significant in order to explain income from agriculture as well as total income. With regard to the distance from the buffer zone, the results suggest a negative influence with respect to the buffer zone, agriculture and total income. The implied message therefore suggests that buffer zones may provide active livelihood sources which are capable of financing rural household agriculture. The income equalizing effect which is portrayed may also further imply that, if correctly targeted and promoted, a buffer zone income could possibly address the current income inequality which is generic in rural areas. However, this potential may not be realized due to the current buffer zone design status (created for local secondary use as opposed to commercial primary use), restrictive policies and poor institutional support. With this dilemma facing community managed game parks (threats as summarised in Chapters three and four amid the potential hope summarized in Chapters five and six), Chapter 7 concludes the study by suggesting that the human-wildlife interaction model, though currently theoretical, may have significant practical potential in addressing the livelihoods of the surrounding communities as well as promoting the conservation of wildlife. This could be possible if available challenges that range from low revenue, insecure property rights, high human-elephant conflict and institutional design conflict for buffer zone utilization are corrected by means of the free market system. This would allow market forces to deliver on the expectations of the ―human-wildlife interactions model‖ – sustainable livelihoods for the former and intergenerational conservation for the latter.

The study was conducted in the Greater Kruger National Park Complex (GKNP), which consists of the Kruger National Park (KNP) and adjacent private game reserves and focuses primarily on the following objectives: • To monitor and evaluate the standard of the existing disease surveillance programmes for the following diseases, Foot and Mouth, Anthrax, Tuberculosis, Brucellosis and Rabies, within the Kruger National Park and adjacent private game reserves by evaluating the level of competency and knowledge in field rangers, field guides and trails rangers with regard to these specific diseases. It can be stated that important differences exist between disease surveillance techniques used for domestic animals and those used for wildlife (Bengis, R.G., Kock, R.A., & Fischer, J., 2002). According to Morner, T., Obendorf, D.L., Artios, M., & Woodford, M.H., 2002, it is more difficult to monitor diseases in wildlife than in domestic animals because wild animals are not constrained by boundaries and can roam over large. distances. For significant diseases in wildlife, an active surveillance programme may be the preferred approach with the aim to collect a certain number of samples from a target population (live or dead animals) to determine the point prevalence of certain pathogens. Active veterinary participation is essential in protected area management, with emphasis on training of technicians, rangers and field biologists with regard to specific diseases and their clinical signs, surveillance and sampling techniques, data collection, and reporting. For the purpose of this study, data collection was conducted by means of a questionnaire drawn up according to the related critical points as described in the Dufour grid (Dufour, 1998). The results of this study clearly showed a need to address certain important aspects regarding a wildlife disease programme within the GKNP. A more efficient wildlife disease surveillance programme, which included more specific and “hands-on” trained staff, would definitely ensure a better early warning system which would detect new or emerging disease outbreaks. / M. Tech. (Nature Conservation))