Dissertations / Theses on the topic 'Private Game Reserves'

The primary aim of this research study was to determine the current state of practice of corporate social responsibility (CSR) within the ecotourism based private game reserve (PGR) industry in the Eastern Cape Province of South Africa. According to Carroll (1991) four kind of responsibilities constitute total CSR, namely economic, legal, ethical and philanthropic responsibilities. Given the context of this research a fifth responsibility concerning environmental responsibilities was added to Carroll 's (1991) pyramid ofCSR. A descriptive and illustrative case study approach, within the phenomenological research paradigm, was used for the purpose of this research. The unit of analysis is the Indalo group, the Association of Eastern Cape Private Game Reserves, made up of 12 ecotourism based PORs. As the current research focused on eight of the twelve PGRs a mUltiple case study was employed. To give effect to the aim a number of research objectives were identified. Firstly to desclibe and assess the current practice in implementing CSR within the ecotourism based PGR industry in the Eastern Cape Province. Secondly, to assess and evaluate the involvement of ecotourism based PGRs in the Eastern Cape Province in each of the five responsibilities comprising CSR. Thirdly, to identify the challenges faced by ecotourism based PGRs in the Eastern Cape Province with regard to the implementation of CSR initiatives. Lastly to provide pertinent conclusions and recommendations with regard to CSR strategies within the ecotourism based PGR industry in the Eastern Cape Province. Data were collected by means of in-depth interviews with the managers of each reserve. In addition the researcher conducted focus interviews with administrative employees at each of the member reserves of the Indalo group. Additionally the managers of each reserve were requested to respond to a structured five point Likert scale questionnaire based on the research by Aupperle, Carroll and Hatfield (1985). This research study found that the current practice at the Indalo group is towards a strategic, long term approach to CSR that aids in the development of a 'sustainable organisation.' The aspect of ' empowerment' emerged as the essence of the current practice ofCSR of the Indalo group. Based on the current practice it was concluded that the Indalo group is actively involved in the specific components of CSR namely, environmental, economic, legal, ethical and philanthropic responsibilities. With regard to the environmental responsibilities it was concluded that the environment is the foundation upon which all other components of CSR rest. In addition it was concluded that the economic responsibilities, if managed well, are key to unlocking the CSR potential of a reserve as well as ensuring widespread economic development. In terms of the legal and ethical responsibilities it was concluded that tourism policies both at the national and international level have not aided in the development of a CSR agenda of the Indalo group. Furthermore managers of the reserves have been instrumental in cultivating their own legal culture of CSR based on their experience in the tourism industry and their ethical stances. In terms of the philanthropic responsibilities it can be concluded that charitable activities that are long term and strategic in nature allow for direct and indirect benefits to all parties involved. Overall, it can further be concluded that despite Hudson and Miller's (2005:5) view that the "tourism industry is well hehind other industries in terms of CSR" the Indalo group is moving forward in terms of rooting CSR into their everyday operations.

The uniqueness of the wildlife and the luxurious nature of South African private game reserves could be seen as a valuable niche in the South African tourism market and for this reason make South Africa a desired destination. Due to complex visitor needs and demands regarding price, service, social connection, authenticity, quality or image, value perceptions will differ in terms of visitors’ experiences. If managers do not understand these value requirements, differences might exist between consumers’ and service providers’ perceptions of value. To maintain visitor satisfaction, loyalty and intention for return to the reserves, managers should continue to provide valued offerings and improve their visitors’ wildlife experience. This research investigated visitors’ perceptions of the value delivered by private game reserves in South Africa and compared these with reserve managers’ perceptions of the value delivered. The results of this research study could contribute to a better understanding of perceived value, which in turn could enhance the success of the private game reserves. The literature contextualised the South African private game reserve as part of wildlife tourism, the wildlife tourism offering and the characteristics of wildlife visitors. An overview of customer value, customer value models showing their development over time, and the conceptual framework of the current study was provided. The resulting conceptual model was used to evaluate managers’ and visitors’ perceptions of Quality, Monetary price, Behavioural price, Reputation, Emotional response, Social value and Novelty value delivered by South African private game reserves. The empirical data was collected by means of a survey, using two structured self-administered electronic questionnaires administered to the managers of, and the visitors to, private game reserves. One hundred and sixty two visitors and 30 managers participated in the survey. By performing exploratory factor analysis it was found that the seven value factors were consistent with the value dimensions reported in the literature. These were labelled as Quality, Emotional response, Monetary price, Reputation, Novelty value, Social value and Behavioural price. Most of managers’ perceptions of value provided exceeded visitors’ perceptions of value received. Both managers and visitors rated value items related to Emotional response highly. Considerably more managers (17 percent) thought that the reserve experience can be associated with good service, opposed to only 4 percent of visitors who perceived the service to be good. On the other hand, a larger proportion of visitors (29%) than the managers (20 percent) perceived the reserve experience as relaxing. Managers rated eleven of the thirteen game reserve attributes more positively than what the visitors did. Of these attributes, accommodation services, protection of the natural environment, game drives and service delivery, showed significant differences. It is recommended that South African private game reserve managers: • conduct market research to get a better understanding of what delights visitors. Research should be conducted on a regular basis to ensure management stays current with visitors’ changing needs; • determine whether the prices charged reflect the quality of the physical offerings, service delivery and the time and effort visitors spent to obtain the offering; • use the adventurous activities offered at the reserves as part of their promotional campaigns to attract adventure tourists; • train service delivery staff and game drive guides to educate visitors on the history, culture and eco-friendly practices related to their reserve; • always deliver superior service to ensure memorable wildlife experiences, value for money and exceed visitors’ expectations; • continue using websites, social media and magazines to inform the target market about the reserve offerings; and • stay in regular contact with visitors through social media, newsletters, blogs, follow up emails/calls or face to face discussions at the reserve.

Social media has become one of the defining features of the technological advances known as Web 2.0. As social media has increased in popularity, so businesses are expected to participate. Social media platforms enable businesses to widely broadcast a message as well as interact directly with individual customers. Customers are also able to interact directly with one another and share information and reviews about products and services offered. This suits the tourism industry particularly well. Internationally, research has shown that individuals use social media and other online tools to research potential holiday destinations. In addition social media is used during travel to share snapshots and commentary as well as after travel, through reviews and recommendations on platforms such as TripAdvisor. However, few studies have investigated how tourism destinations use social media to attract new clients and retain existing clients. Very little research has been done on tourism and social media in South Africa despite the importance of this industry to Gross Domestic Product (GDP). This study focused on four-star establishments within the photographic wildlife tourism industry in the Eastern Cape of South Africa. An initial survey of social media participation was carried out within the framework set out by Chan and Guillet (2011); this was then followed up with interviews with selected managers. Results showed that, in general, Private Game Reserves (PGRs) had embraced social media as a communication and marketing platform; despite concerns raised about the lack of control over content as well as poor understanding of the influence social media might have on the bottom line. TripAdvisor, Facebook and Twitter were the most commonly used platforms due to management familiarity with the platform and their ease of use. Few lodges utilised blogs or content sites such as YouTube and management cited time commitments associated with this type of platform as a reason for non-participation. However, although most PGRs or lodges had a profile on social media, this did not always mean active participation. Frequently, lodges began updating but gradually stopped after a few months. It was noted however that only one of the lodges interviewed retained an individual whose sole responsibility was social media; generally lodges did not feel that a dedicated person was necessary. This may result in a lack of time available on the part of the individual responsible or simply be a case of not understanding the platform or how to use it effectively. However, none of the PGRs with poor social media participation responded to interview requests and therefore it was not possible to determine the reasons for their poor participation. Among those lodges that actively participated, most succeed in retaining fans and followers through consistent posting of relevant and interesting content as well as customised responses that encouraged fans or followers’ interaction. However, there did not appear to be any evidence of using social media to learn about fans and followers in order to better customise the lodge offerings. This may not be necessary in this type of industry as PGRs sell a specific product and have a limited ability to customise offerings. In addition, there may be other sources of market information which lodges prefer to use. Special offers, competitions and promotions had limited success on social media. Generally, lodges used social media to promote links to a dedicated competition or promotions page. In conclusion, the managers interviewed felt strongly that social media had made a measureable impact on the tourism industry and was a channel that was here to stay. Further research around the best practice and most effective use will enable PGRs to develop and maintain effective strategies for social media participation.

Many large carnivores are declining globally; most threatened or risk extinction due to a loss of habitat, resources, and direct removal; often the later as a result of conflict with humans. Although leopards and many meso-carnivore species are still free roaming in South Africa, few data are available on these species outside large protected areas as they are often elusive, wide ranging and found at low densities. More data are needed on the population dynamics, ecology and biology of species such as leopard, if we are to implement evidence-based approaches to their conservation within small reserves and surrounding unprotected areas. Camera traps are being increasingly utilized in research, as they can record data on a species or a whole community at relatively low cost. Here we used a network of camera traps to monitor species presence at Thaba Tholo Wilderness Reserve, Mpumalanga, South Africa. We found that camera trap efficacy varied between species, with smaller carnivores significantly under-recorded more frequently than larger predators. However, leopards were successfully captured by camera trap when compared with more traditional monitoring methods (i.e. spoor). Small reserves may play an important role in the conservation of carnivores, but often these reserves are surrounded by farmland and the successful separation of livestock and game using a fence can affect vegetation composition, fragmenting the land further. However, these effects may be limited by the free movement of wild browsers and grazers through holes in the fence which may also decrease the negative effects of fencing while supporting endangered and highly mobile species such as the leopard Panthera pardus. Leopard densities were found to be 3.04 (S.E. +/-1.55) to 4.97 (S.E. +/-2.14) leopards per 100km2, which was lower than other estimates from South Africa, however the population was stable throughout the study suggesting the reserve was a source for leopard and offspring were dispersing. Although there was no evidence of habitat preference by the leopard, habitat was found to be more significant in influencing relative local abundances of meso-carnivores than potential associations with leopard and other larger carnivores. However abundance may have been affected by factors outside the reserve as conflict with humans was evident. Negative actions towards leopard and other carnivores in retaliation to the predation of animal stock occurred in the farmland surrounding the study site, with a significantly higher percentage of commercial game farmers responding that they would take action against one or more species of carnivore compared to livestock owners. The financial loss sustained with increasing game prices in South Africa could therefore increase the conflict between humans and carnivores across the country, which in turn could have detrimental effects on local leopard and other carnivore populations. The relatively high numbers of the extremely rare erythristic leopard occurring within the relatively low density leopard population is likely to be the result of genetic drift, which may have been a result of this conflict; highlighting that although small reserves may play an important role in the protection and propagation of threatened species it is human acceptance of carnivores which is likely to be vital in the successful conservation and long term survival of predators outside protected areas.

The reintroduction of lions, cheetahs and African wild dogs to Kwandwe Private Game Reserve in the Eastern Cape Province of South Africa created the opportunity to study the biology and behaviour of these large carnivores in an enclosed system. The research focused on space utilisation and feeding ecology of the predators, using standard observational methods. Changes in the structure of the carnivore guild, and changes in the prey base that occurred during the study were used as natural experiments to examine factors affecting space use and diet. In general, the diets of the predators were similar to previous studies and prey abundance was more important than prey species size in determining prey selection. Changes in the abundance of certain prey species was matched by a dietary switch in lions from kudu to warthog and an increase in the proportion of springbok kills by the cheetahs. There was no significant difference in the proportions of prey species detected by ad hoc or continuous observations. Core areas occupied by the predators were significantly smaller than home ranges except when females were denning. Home ranges overlapped both within and between species, but there was very little overlap of core areas. An increase in the number of lion prides in the area during the study resulted in an increase in overlap of home ranges of lions and cheetahs, but did not result in a change in home range size. Space use by female cheetahs with cubs increased as the cubs grew older. The use of thicket vegetation by cheetahs decreased with an increase in the number of lion prides. Minimum Daily Energy Expenditure, energy intake and net benefit were calculated for the predators using data from continuous observations. All predators exhibited a large net benefit and the net benefit for single female cheetahs was greater than for the members of the coalition. Net benefit for the alpha pair of African wild dogs was lower than that of the pack.

Over the past fifteen years there has been an extensive conversion of land use from traditional farming practices to conservation and private game reserves. It has been suggested by Langholz and Kerley (2006:2) that privately owned preserved areas can engage in ecotourism initiatives by protecting biodiversity, succeeding financially and contributing to social upliftment. However, ecotourism has to operate within the context of historical land dispossession of the majority black population and current land reform initiatives to address this problem. In view of the economic, social and environmental importance of ecotourism based private game reserves (PGRs) in South Africa, particularly the Eastern Cape, the main goal of this research is to examine the Indalo association of private game reserves in the Eastern Cape Province’s development model for ex-farmworkers and adjacent communities. This was done through a literature survey and analysis of existing studies and by interviewing the managers of the Indalo PGRs and a few farmworkers to get their opinions of the tension between what they are doing and the imperatives of land reform. This involved an exploration of their community development work, particularly around issues of job creation, participation in decision-making, capacity building and sustainability. The thesis comes to the following conclusions. The first is that the establishment of PGRs have a significant positive impact on the local areas in which they are established. As a land-use, ecotourism based game reserves are an economically and ecologically desirable alternative to other land uses. Therefore the ecotourism based private game reserve industry with its extensive community development focus for farmworkers and local communities is a viable and sustainable alternative to conventional land reform. The second is that the Indalo PGRs development work has built capacity in the communities it has served. However, community participation, particularly in decision-making is limited and needs more attention if productive and sustainable development is to be achieved. Lastly, communities rely heavily on external support for their development and upliftment. However, the majority of the PGRs have/or are putting measures in place to ensure the continuation of community development projects to ensure the long-term sustainability of projects.

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

Includes bibliographical references (leaves 89-98).
Worldwide, nature conservation paradigms have changed markedly since the turn of the 19th century. These changes have affected the way that conservation has been practiced in the eastern lowveld of South Africa. At the same time sociopolitical conditions in South Africa have also undergone enormous shifts which have affected the distribution of rural people and land use practices in the rural lowveld. This study examines private nature conservation and its relationship to local rural people in the lowveld using Londolozi Private Game Reserve as a case study. Various methods of data collection were used. These included focus group interviews with local rural people, a survey questionnaire with lodge staff, informal interviews with land owners, and visits to rural homes and schools. In addition the author drew on eight years of work and research experience on private game reserves in and around the study area. The application of fortress conservation in the lowveld resulted in the removal of black people from Crown and privately owned land, land that they were living on. They were removed to the western borders of the current Sabi Sand Wildtuin (SSW). This complete exclusion of local people from the conservation land in the Kruger National Park (KNP) and SSW remained the status quo until Londolozi, in 1976 and almost at least a decade before the rest of the conservation world began to engage with local black people on its borders. Londolozi paid particular attention to the rural staff working at the lodge. In the 1990's fortress conservation was replaced with community conservation approaches which sought to use market-based strategies to demonstrate the value of conservation to rural people bordering conservation areas. Londolozi retracted from its essentially bottom-up approach and implemented a number of infrastructural, management devised, top-down community projects in the local areas. It did this through the Conservation Corporation Africa (CC Africa) Rural Investment Fund. These projects, although more obvious to the wider community outside the reserve, were inefficient and wasted money in some cases. In 2007, Londolozi returned to focussing on individual rural staff members rather than on infrastructural community development projects. The effect has been very positive for the 200 or so rural staff at Londolozi, but the wider community outside the fences sees little benefit or point to this approach. The community lodged a number of land claims on the SSW and Londolozi. The merits of the only gazetted claim on Londolozi would seem to be tenuous at best.

The cheetah (Acinonyx jubatus) has experienced a drastic decline in numbers over the last 20 years globally and is currently listed as vulnerable by the International Union for the Conservation of Nature (IUCN). In South Africa, there are only an estimated 763 free-ranging cheetahs and conflict with humans is arguably the most significant reason for this low number. The aim of my study was to determine the population size and demographic characteristics of the cheetah population within the Timbavati Private Nature Reserve (TPNR), South Africa, and to contribute to a better understanding of cheetah space use and habitat selection. The research was conducted on TPNR between November 2009 and June 2011 and I used a photographic survey to assess cheetah population size and demographic characteristics. Location data was obtained by collaring two adult male cheetahs with GPS/GSM collars and ad hoc sightings data from across the reserve for an adult female with cubs and three adolescent females. A relatively high minimum population density of 4.46 cheetahs/100km² was estimated, signifying a relatively healthy cheetah population. The sex ratio data indicated a higher male to female ratio and an average litter size of three cubs. The relatively high cub survival rate and density is promising in terms of the status of species within the area, as the data denote the success and potential persistence of the species. Cheetah home ranges varied between 20.97km² for the female with cubs and 659.65km² for the younger collared male. Season did not appear to be a determining factor in terms of home range sizes for the three social groups within the TPNR. However, the males did show a slight increase in their home range sizes during the dry season when resources where presumably more widespread. My results indicate that the cheetah is an adaptable species, flexible in behaviour and able to tolerate a variety of habitat types. Such knowledge is fundamental for planning and implementing the effective management and conservation of cheetahs in South Africa.

During the last 25 years, the Eastern Cape Province of South Africa has seen the establishment of many small to medium sized (≤ 440km2) game reserves. These reserves have reintroduced many of the larger indigenous wildlife that had been extirpated by the early 20th century. As such, these reserves and wildlife introductions have created many research opportunities, including investigations on the ecology of reintroduced carnivores in the Thicket biome. Brown hyaenas (Hyaena brunnea) are one of the large carnivore species that have been reintroduced into the area. As these animals have predominantly been studied in more open, arid systems, their reintroduction has provided an excellent opportunity to study the species in an alternate natural habitat. Information gathered from such investigations adds to our knowledge of the species and also provides information for the management of brown hyaenas within small, enclosed reserves. Data were collected over the period of one calendaryear, from February 2013 to February 2014 at Kwandwe Private Game Reserve in the Eastern Cape, South Africa. Brown hyaena population estimates were calculated using capture-recapture methods from individually identifiable images captured during a three month camera trapping survey. Images of brown hyaenas were separated into left- and right-side profiles. Twenty-eight individuals were positively identified from left-side images and 27 from right-side images. Non-spatial and spatially explicit capture-recapture analyses were both run in the program DENSITY 5.0. Density estimates ranged from 14 to 20 individuals/100km2 (equivalent to a total abundance of 26-37 individuals) depending on the method used. Despite the range of estimates, all are considerably higher than in other areaswhere densities have been calculated. Satellite/GPS collars were fitted to three individual brown hyaenas (two males and one female) to measure their home range size and use of space. Home range size was calculated using two different methods, Kernel utilisation distributions and Brownian bridges. Home range estimates were similar using both methods; however Brownian bridge methods appeared to exaggerate the use of space by individuals. Kernel home range sizes for the three individuals ranged between 42.62km2 and 79.88km2. These estimates are considerably smaller than previous findings from other parts of Africa and suggest that sufficient resources may be available within this enclosed system. The results from this study suggest that brown hyaenas are successful generalists in this enclosed system and are able to persist at high densities and occupy relatively small home ranges. This information is important for the managers of small reserves who wish to reintroduce brown hyaenas. Should brown hyaenas be introduced into reserves in the Thicket biome with sufficient resources, the numbers are likely to increase rapidly. If high numbers are not desired then preventative measures (e.g. contraception) should be investigated before release.

Predator reintroductions are becoming increasingly more common for multiple reasons, including assisting with the conservation of a predator species, the restoration of ecosystem functions and the economic benefits of their reintroduction for ecotourism ventures. There remains however, little knowledge on prey species responses to these predator reintroductions. As such, the reintroduction of cheetah (Acinonyx jubatus) into Samara Private Game Reserve provided an opportunity to investigate prey responses to predator reintroduction across a range of spatial and temporal scales. More specifically, the aim of this study was to investigate the effect of cheetah predation risk on habitat use and behavioural responses of the resident ungulate community. Samara is divided into “predator present” and “predator absent” sections, providing the opportunity to conduct a comparative study investigating the effect of cheetah on prey responses. It was hypothesized that different ungulate species would respond differently to the presence of cheetah, depending on differences in perceived vulnerability to cheetah predation. To address this, shifts in habitat use, and behavioural responses of the ungulate community reflected at landscape and patch scale were investigated. Overall, ungulate species have not shifted habitat use since cheetah reintroduction, this was possibly related to life history strategy constraints and the need for individuals to obtain suitable forage and therefore remain in specific habitats. While no shift in habitat use was observed for the majority of ungulate species, a shift in behaviour was observed for kudu (Tragelaphus strepsiceros) at a landscape scale, where kudu dedicated more time to vigilance and less time to foraging within the predator section. In addition, individuals within smaller kudu groups were observed to be more vigilant than individuals within larger groups of kudu within the predator section. Although the other three ungulate species monitored did not increase time spent vigilant within the predator section, they still maintained relatively high levels of vigilance, potentially as a means of social monitoring. At a patch level, ungulate species responded strongly to a predator cue as a proxy for cheetah proximity, and increased time spent vigilant with a trade-off of lower foraging effort. This vigilant response was strongest for kudu. Differences in perceived predation risk were reflected within eland (Tragelaphus oryx) and kudu species demographic classes, with juvenile eland and kudu, adult female kudu and subadult female kudu spending more time vigilant within manipulated patches than respective males of each species. Kudu were also observed adopting fine-scale behavioural responses to minimize predation risk within patches. The asymmetrical prey species response to perceived predation risk from cheetah supports the hypothesis that different species respond differently to the presence of a predator. Furthermore, this study illustrated the importance of measuring prey responses to predation risk across multiple scales and highlighted the need to replicate this study for a number of different sites where predators have been reintroduced, to better understand the range of factors influencing these predator-prey interactions.

The re-introduction of cheetah onto small reserves in the Eastern Cape Province has created the opportunity to study this species in an environment (Valley Bushveld) in which it has not previously been studied and which is quite different from the less wooded habitats in which previous studies have occurred. Thus the aim of this study is to add to the growing number of studies of cheetah in more wooded habitats and to contribute a better understanding of the level of specialization or adaptability in space use, habitat selection, diet and hunting behaviour that the cheetah possesses. The research was conducted on Kwandwe Private Game Reserve from February 2003 to August 2004. Direct observations, scat analysis and continuous observations were used to avoid bias towards large sized prey found when only using direct observations to study diet. The cheetah killed 15 species and four of the five most important prey species (kudu, springbok, grey duiker and bushbuck) were hunted according to their abundance on the reserve, while impala, the fifth most important prey species, was avoided (i.e. preference index less than one) by the cheetah. The cheetah’s main prey was medium sized ungulates, although the three male coalition killed larger prey than females and females with cubs. The daily food intake per cheetah per day was calculated to range from 5.3kg/cheetah/day for the coalition to 8kg/cheetah/day for a solitary female. Home range areas ranged from 11.1 km² for female cheetah with cubs in a den to 65.6 km² for single female cheetah and core areas ranged from 6 km² for the three male coalition to 26.5 km² for independent cubs. Habitat selection by cheetah on Kwandwe varied between the social groups depending on their susceptibility to predation by lions, their need for cover and need for water, and was similar to what has been previously reported. The home range of the coalition incorporated the most open vegetation type (karroid shrubland) with surrounding denser vegetation, while females occupied areas of denser vegetation. Activity patterns and hunting behaviour varied between different cheetah social groups with female cheetah being more active during day light hours compared to males which made 38% of their kills after dark. The average chase distances for the various cheetah groups varied considerably, and the chase distance for successful hunts was longer than for unsuccessful for all groups except single female cheetah. The percentage of kills’ kleptoparasitised on Kwandwe was very low compared to other studies possibly due to the low density of direct competitors, which in turn lead to longer mean kill retention times. These results suggest that cheetah are more adaptable than previously thought and this adaptability may have important implications for their conservation.

In recent years several regions in South Africa including KwaZulu-Natal (KZN) have experienced a significant shift in their farming practice, moving away from conventional commercial farming to the apparently more lucrative private game farming. This is clearly evident in the northern parts of KZN, where most Private Game Reserves (PGRs) occur in semi-arid areas, which are poorly suited to agriculture or livestock farming. These conversions of land cover or change in land use (i.e. from conventional commercial farming to private game farming) is occurring fairly swiftly even though the extent (area of change), impacts and implications of this trend have not been established. Very limited scientific research has been carried out on the environmental effects, impacts and implications of these land cover/use changes related to PGRs. In an attempt to document these changes as well as the environmental implications, three PGRs i.e. Kube Yini, Thanda and Phinda and the Mkhuze Game Reserve within northern KZN were selected for in-depth study. Mkhuze, which is owned and managed by the state, was selected as the control for this study, as it has remained relatively undisturbed for a long period of time. A comparison between the PGRs and Mkhuze was carried out to compare the land cover/use changes within the study area since the establishment of the PGRs. Remote sensing software was used to achieve the aim and objectives of this study. Using satellite images from 1990 and 2007, a change detection analysis was performed to determine the land cover/use changes that occurred within the study area during the period 1990-2007. Sixty-four land cover/use classes were generated from the analysis. These sixty-four classes were reclassified into five broad land cover/use classes which were identified as (1) water and riverine vegetation, (2) sand forest, forest and rock faces, (3) woodlands, (4) old fields and disturbed areas, (5) and grasslands. The results illustrated that during the period 1990 to 2007, the land cover/use of the entire study area changed significantly, with the overall land cover/use changes illustrating a decrease in the water bodies and riverine vegetation (6 percent to 3 percent); sand forest, forest and rock faces (19 percent to 16 percent); woodlands (26 percent to 25 percent); and old fields and disturbed areas (26 percent to 25 percent) whilst an increase in the grasslands (23 percent to 31 percent) was evident. Within each individual PGR, significant land cover/use changes related to private game farming were evident. In Kube Yini PGR, a decrease in the water bodies and riverine vegetation (4 percent to 1 percent); old fields and disturbed areas (23 percent to 11 percent); and grasslands (6 percent to 5 percent) were observed whilst an increase in the sand forest, forest and rock faces (31 percent to 47 percent); and grasslands (6 percent to 5 percent) land covers were seen. There has been no change in the woodlands cover (i.e. remains 36 percent). Old fields and disturbed areas have decreased due to the clearing programme that was implemented by Kube Yini, which has also contributed to the increased sand forest, forest and rock faces; and grassland land covers. At Thanda PGR, water bodies and riverine vegetation remained the same overall, while an increase in the grasslands cover (19 percent to 49 percent) was clearly evident. A decrease in the sand forest, forest and rock faces (13 percent to 4 percent); woodlands (29 percent to 18 percent); and old fields and disturbed areas (38 percent to 28 percent) was also noted. This was due to Thanda‟s Management Plan, whereby management had cleared the old fields and disturbed areas to accommodate the increased tourist accommodation, increased game species as well as the increased space that is required for these species. Furthermore over the recent years, Thanda has been practicing bush clearing and thinning of vegetation, which has resulted in the creation of a grassland landscape. A grassland landscape was required for viewing the game species, which resulted in a decreased sand forest, forest and rock faces; woodlands; and old fields and disturbed areas. In Phinda too, the water bodies and riverine vegetation remained the same (i.e. 1 percent). The sand forest, forest and rock faces (32 percent to 19 percent); and woodlands (43 percent to 41 percent) decreased whilst an increased old fields and disturbed areas (15 percent to 26 percent); and grasslands (9 percent to 13 percent) were observed. Sand forests are sensitive and decrease in extent rather easily as a result of disturbances experienced in the area. The decrease in sand forest, forest and rock faces during this period may be due to the increased wildlife and especially elephant population experienced on this reserve. The woodlands land cover decreased in size as a result of clearing to accommodate tourist infrastructure as well as creating a grassland landscape i.e. open space and clear viewing for the game species. The changes in Phinda‟s land cover resulted can be explained by the different management practices that were practised on the reserve. The results from the PGRs were compared against Mkhuze so as to determine whether private game faming was in fact changing the landscape of the study area. During this period 1990 to 2007, Mkhuze experienced only slight changes within it‟s land cover/use classes: water and riverine vegetation (2 percent to 1 percent); sand forest, forest and rock faces (16 percent to 15 percent); and grasslands (29 percent to 26 percent) decreased whilst an increase in the woodlands (27 percent to 30 percent); and old fields and disturbed areas (26 percent to 28 percent) were noted. Since Mkhuze is managed by the state with its priority being conservation first and not increased monetary gain, competition between species and habitants occurred with the least amount of human influence. It is most likely that the water and riverine vegetation; and grasslands decreased due to the drought experienced in the area between 2001-2006, which may have led to the increased old fields and disturbed areas. In addition woodlands may have increased due to its resistance to harsh conditions. Also contributing to the increased old fields and disturbed areas could be the increased wildlife numbers experienced in the reserve. The slight drop in the sand forest, forest and rock faces land cover most likely resulted due to natural competition between the vegetation species as well as management realising the significance of the sand forest, thus assisting in the preservation of the sand forest, forest and rock faces cover. An accuracy assessment was carried out to determine the accuracy of the image classification, and a 75 % accuracy was achieved for the overall analysis. The results illustrate that during the period 1990-2007, the study area‟s land cover changed significantly and that this was mostly like due to the changes within the land cover of the individual PGRs. Climatic data for this period was also taken into consideration to see whether climate variations had occurred and whether this had impacted the change in land cover/use of the study area. The results from the PGRs were compared against the state reserve results as well as the climatic data. The results suggest that the majority of the land cover/use changes within the study area had occurred largely due to private game farming rather than natural processes. The climatic variables such as temperature of the area remained fairly unchanged whilst humidity remained fairly high. With the exception of the drought experienced in the area between the period 2001-2006, it is most likely that the changes in the area are the result of the change to private game farming. Private game farming is having a significant effect on the landscape of the study area and this is largely due to the different management practices practised on each individual PGR. It is recommended that PGRs be monitored and regulated consistently in order to prevent the degradation of the environment and its ecosystem. The study exhibits the value and usefulness of satellite imagery in detecting land cover/use changes related to private game farming. Landsat 5 TM imagery was the most suitable and accurate in identifying and mapping broad scale land cover/use changes related to private game farming. If a more detailed level of investigation is required, the use of higher resolution imagery (e.g. Spot/Landsat 7) is advised.
Thesis (M.Sc.)-University of KwaZulu-Natal, Westville, 2010.

South Africa presently experiences high levels of crime daily. Although crime is accepted as an everyday occurrence for its citizens, it affects the economy of the country. This study analysed security measures implemented on Commercial Private Game Reserves (CPGRs) in Limpopo and the impact of crime thereof. CPGRs are enclosed areas containing various species of fauna and flora. Visitors from domestic and foreign origins visit these reserves to enjoy nature and its tranquillity. This study analysed the security measures to determine their effectiveness for CPGRs. The study further explored the use of security risk management strategies and risk assessments as crime reduction tools. The study was carried out using a case study research design. Data were collected by the researcher using three methods: observation, onsite checklists and semi-structured one-on-one interviews which were conducted on site. Validity and reliability indicate the trustworthiness of the study. The researcher reduced the data gathered through the use of thematic data analysis. Interviews were transcribed and themes were created and identified by the researcher. The comprehensive data indicated the importance of a security risk manager on a CPGR. The research found that very few security risk managers are employed and that managers of security risks employed on CPGRs have various titles. However, while the CPGRs have similar risks, their risk reduction strategies vary. The most commonly used measures are people, physical and technological measures with each having various subdivisions. The security measures implemented by CPGRs in the Limpopo province which were analysed are not formulated using a scientific approach as most properties do not make use of a formal security risk assessment. The study is deemed valuable as a model was developed from the findings that could be used by game reserves to guide them to apply relevant security measures. A formal security programme is often limited due to financial constraints of the reserve or the reserve owners, however, not all strategies should be considered as a financial expense as much can be done without exhausting financial reserves. The findings contributed to making recommendations to improve the overall security of CPGRs. This study encourages more research into the subject to improve the security industry and to stimulate the tourism industry.
Security Risk Management
M. Tech. (Security Management)

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. Dissertation (MSc (Wildlife Management))--University of Pretoria, 2006.
Centre for Wildlife Management
unrestricted

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))

Knowledge of habitat use and selection is essential to managing ungulate populations. This study assesses habitat use by elephant (Loxodonta Africana), giraffe (Giraffa camelopardalis), kudu (Tragelaphus strepsiceros), nyala (Tragelaphus angasii) and impala (Aepyceros melampus) in Thanda Private Game Reserve, KwaZulu-Natal. Firstly, I examine the effects of body size dimorphism, sexual segregation and predation on habitat selection and resource partitioning by ungulates. The mechanisms driving resource partitioning strategies were studied at three environmental scales, namely broader habitat (using habitat preference ratios), local environment (using Multi-Dimensional Scaling (MDS) and Analysis of Similarity (ANOSIM)) and plant (feeding heights using Analysis of Variance (ANOVA) and Regression analyses). At the habitat level, ungulates show distinct habitat preferences, independent of body size, which did not overlap, thus promote resource partitioning. Habitat selection, at the local environment level, varied among species but not between sexes. Therefore, body size class may influence selection for particular environmental characteristics. At the plant level, resource partitioning was evident among the larger species (giraffe and elephant) versus the smaller species (nyala and impala), but there was no apparent segregation among the sexes within species. Therefore, resource partitioning was strongest at the habitat level, bit less noticeable at the intermediate and finer plant scale. Secondly, I assessed the antipredator behaviour of multi-species assemblage in an experimental context (before vs. after lion reintroduction). I examined herbivore responses in terms of aggregation (forming safer groups), predator avoidance (selecting areas that predators avoid), and habitat selection in terms of habitat structure (selecting areas where capture is less likely), in response to lion reintroduction. Ungulates shifted habitats to avoid lion presence, i.e. into habitats least preferred by lion, and dominant species (based on body size) forced subordinate species into suboptimal habitats. However, counter predictions, ungulates did not increase their group size after lion were released. With the development of small private game reserves, intensive management is essential to maintain ecological heterogeneity, in this case through trophic cascades which promote coexistence. Managing ungulates as ecologically different according to body size will accommodate differences among herbivore populations. Long-term studies of habitat use by ungulates and predators will provide management with information to manipulate factors affecting habitat selection and predation, and thus sustainability of ungulate populations.
Thesis (M.Sc.)-University of KwaZulu-Natal, Westville, 2008.

Dissertation submitted to the Faculty of Science in fulfilment of the requirements for the degree of Masters of Science, Johannesburg 2018
This research examines the influence of surface water availability, which depends on rainfall, and temperature on faunal occurrence patterns at naturally-forming waterholes in Shamwari Private Game Reserve, Eastern Cape, South Africa. The objectives assess the occurrence and diversity of species at three naturally-forming waterholes and to examine the implications that rainfall and temperature have on species visitation patterns at naturally-forming waterholes. On a local scale, this research makes use of camera trap images activated by motion sensor, capturing at 10 second intervals to establish the faunal occurrence patterns and to determine wallowing activity of elephants, white rhino, and warthog at the waterholes over a short-time scale (June 2016 to November 2016). The frequencies of mammal species visiting times per hour were grouped into daily and monthly periods. Monthly data were examined, as this was a short-term study, hence shifts in faunal activity could be easily identified with local weather conditions monthly rather than seasonally (as seasonality was not the focus of the study). The occurrence of different species per hour at the waterholes was established over a period of six months (June to November). Distribution curves were created to determine species peak visitation times per hour, both daily and monthly, and pie charts were produced to determine shifts in individual species abundance each month. Local weather data were statistically analysed (Pearson`s correlation coefficient and cross-correlation) with faunal occurrence to determine the influence of these local weather conditions on faunal behaviour. Species-specific occurrences (daily and monthly) were established for all species that visited the three selected waterholes. Herbivore visitation occurred predominantly during diurnal hours and carnivores were observed during nocturnal hours. Temperature influenced species visitation times at these waterholes. As temperatures peaked (Tmax and Tmin), there was a decrease in species sighted at the waterholes. However, surface water availability, which is influenced by rainfall, was the crucial variable that drove faunal occurrence at the naturally-forming waterholes. More species were observed at the waterholes after rainfall events, compared to before rainfall. A delay in faunal occurrence was evident at the waterholes, two weeks after rainfall events. This lag exists due to the surface water, which was made available after rainfall events. Surface water availability and temperatures were, however, not the only factors that drove the occurrence of species at these waterholes. Other factors such as predator-prey relationships, tourist presence, cloud cover, inter- and intra-species competition, vegetation, soil type, and waterhole morphology influenced faunal occurrence patterns. iii Other objectives were to establish wallowing activity at the naturally-forming waterholes and to determine if there is a relationship between local weather variables and wallowing behaviour. As elephants, white rhino, and warthog are sparsely haired mammals, it is essential that they wallow for means of thermoregulation. Wallowing activity of these species only occurred during diurnal hours. In Shamwari at the three naturally-forming waterholes, warthogs wallowed more frequently than elephants and white rhino. Local weather variables influenced the wallowing behaviour of these species. An increase in temperature corresponded with an increase in wallowing activity. In addition, peak wallowing activity occurred at midday, when temperatures were at their highest. However, this depended on whether there was surface water available in these waterholes. A significant two week interval occurred between rainfall and wallowing activity (cross correlation function = 0.75), where the quantity of rainfall directly influenced the presence of surface water available in these waterholes. Without rainfall, the three naturally-forming waterholes remained dry and species did/could not undergo wallowing activity. It is essential to understand faunal visitation patterns and wallowing behaviour in relation to local weather variables, in particular with projected climate change scenarios. This study contributes to the knowledge necessary for the management decisions that ensure sustainability of wildlife in protected areas in South Africa. This can provide essential information for the construction of artificial waterholes, which should mimic natural waterholes and faunal distribution.
XL2019

With the development of digital technology during the last decade and the improvement of Geographic Information Systems (GIS), it has become easier for various scientific fields to predict and extrapolate data. Various organisations and institutions continuously develop algorithms and software to assist with specific challenges in multiple fields of science. These technologies and principles have also been effectively applied in the soil science field of pedology. Traditional soil mapping, although effective, is time consuming, arduous and expensive. It is thus important to develop methods whereby the soil forms of an area can be identified faster while providing accurate information to the reader/ user. Conservation areas, such as Phinda Private Game Reserve (Phinda), which covers a large area (greater than 28 000 ha) can benefit from a soil map. The importance of a proper soil map has a great many uses in conservation, but not every organisation or individual can afford it. This is where digital soil mapping (DSM) or Predictive Soil Mapping (PSM) comes into its own. Substantial research and development have been done in the form of methodology and software systems for DSM although it has not been effectively applied to conservation management. By applying these techniques, accurate and interactive soil maps were developed without the burdensome expenses or dangers associated with traditional soil observations in a conservation area. The application of DSM and the use of the soil land inference model (SoLIM) at Phinda resulted in maps based on the Fey soil-form classification as well as a soil sensitivity index (SSI). The SSI was developed based on the various soil forms present at Phinda and the factors that determine its sensitivity to various types of degradation. These digital maps indicated accuracies of 71% (Fey classification) and 72% for the SSI. The kappa values indicated a substantial agreement (0.63) for the Fey classification map and a moderate agreement (0.57) for the SSI map. The SSI was then combined with the predator sightings and the location of infrastructure and commercial lodges to derive the agreement of activities, game drives, which includes off-road driving (ORD) on sensitive soils. As erosion is a concerning problem, predominantly caused by human activities within Phinda, it was necessary to use the SSI map as a base of comparison. This digitally produced soil map will be presented to the conservation management at Phinda whereby planning can be conducted, literally, from the ground up. Proper planning will thus prevent a loss of soil and consequently a loss of biodiversity. All the information was then combined to developed recommendations for Phinda as to improve the overall road network by upgrading, removing and rehabilitating certain roads and provide advice concerning ORD. These decisions, in turn, prevent long-term soil and biodiversity loss while still providing clients with a true African bush experience.
College of Agriculture and Environmental Sciences

South Africa’s growing elephant populations are concentrated in relatively small enclosed protected areas resulting in the over utilisation of the available food sources. Elephants and other herbivores as well as other natural disturbances such as fires and droughts play an important role in maintaining savannah environments. When these disturbances become too concentrated in a particular area the vegetation composition may be negatively affected. Excessive damage to the vegetation would result from exceeding the capacity of a protected area to provide food resources. The effect of the 120 elephants on the vegetation of Welgevonden Private Game Reserve, is not known. The rugged terrain of this reserve makes it a difficult, time consuming and labour intensive exercise to conduct ground studies. Satellite images can be used as a monitoring tool for vegetation change and improve the quantity and quality of environmental data to be collected significantly, allowing more informed management decision-making. This study evaluated the use of satellite imagery for monitoring elephant induced vegetation change on Welgevonden Private Game Reserve. The LANDSAT Thematic Mapper multispectral images, acquired at two yearly intervals from 1993 until 2007 were used. However, no suitable images were available for the years 1997, 2001 and 2003. A series of vegetation change maps was produced and the distribution of water sources and fire occurrences mapped. The areas of change were then correlated with the spatial distribution of water points and fire occurances, with uncorrelated areas of change. This was analysed using large animal population trends, weather data and management practices. On the visual comparison of the vegetation maps, it was seen that over this time period there was some decrease and thinning of woodland, but the most notable change was the increase of open woodland and decrease in grasslands. Using only the digital change detection for the period 1993 to 2007, a general increase in vegetation cover is seen. But this generalisation is misleading, since comparing the digital change detection to the vegetation maps indicates that while vegetation cover may have increased, significant changes occurred in the vegetation types. Most of the areas of significant change that were identified showed a strong positive correlation with burnt areas. The distribution of the water sources could not be directly linked to the vegetation change although rainfall fluctuations seemed to have accelerated vegetation changes. Years with high game counts, such as 1999, also coincide with very low rainfall making it difficult to differentiate between the effects of heavy utilisation of vegetation and low rainfall. Furthermore, many of the initial vegetation changes could be the result of land use changes due to the introduction of browsers, selective grazers and elephants that allow for more natural utilisation of the vegetation. Remote sensing makes it possible to successfully track changes in vegetation and identify areas of potential elephant induced vegetation change. Vegetation changes caused by disturbances, such as fire and anthropogenic activities, can be accounted for but it is not possible to conclude with a high level of certainty that the further changes seen are solely a result of elephant damage. Further work is required to reliably isolate elephant induced vegetation changes, as well as to establish the effects these changes have on the ecosystem as a whole.
Environmental Sciences
(M. Sc. (Environmetal Sciences))

Accelerated erosion is a major environmental, social and economical threat in South Africa. It is estimated that in excess of 400 million tones of soil is lost every year in South Africa, with much of this erosion being attributed to improper land management and little or no erosion control methods. This study was aimed to determine the efficiency of soil erosion structures, which were constructed in the Mabula Private Game Reserve (Limpopo Province), in reducing the amount of sediment eroded at the sites as well as to determine the amounts of sediments deposited due to their presence. Factors such as rainfall, slope, soil type and particle size were measured to determine their influence on sediment erosion and the ultimate deposition of this sediment. The geology of the area is characterised by Waterberg Sandstones and igneous intrusions of mostly granite. Rainfall in the area occurs between the October and April, with an average of 550 – 750 mm. The temperatures range from 18°C - 32°C during the summer months and 4°C to 22°C in the winter months. The study area falls within the Sour Bushveld and the Sourish Mixed Bushveld, according to the Acocks classification. These veld types are characterised by open an open savanna of tall trees and shrubs. Five sites affected by soil erosion were selected and at each site structures were constructed, the size and number of structures at each site was dependant on the extent of the sites area. The structures are made from a shade net product known as T65, a shade cloth developed by Alnet, which has not been UV treated allowing it to disintegrate in the open atmosphere after 2-3 years. Soil measurements and samples were taken before the rainfall season to establish baseline data to compare the results with once the filed work has been concluded. Thereafter samples and measurements were taken every month during the rainfall season, which extended from October 2004 to April 2005. In conjunction with the measurements taken at each structure the slope of each site was determined and the profiles of the sediment deposited at the structures after the rainfall season were studied. From the measurements it was clear that as the rainfall increased so the amount of sediment being deposited at the structures increased. There were structures that experienced more iii sediment deposition than others and theses differences could be attributed to factors such as parent material, soil texture, slope angle and soil type. Due to the deposition of sediment and the reduction in surface flow caused by the structures, vegetation established itself and began to flourish in the newly deposited soil. Through the establishment of vegetation at the sites an element of success was achieved. With a total of 2 101 mm of sediment being deposited at the structures and the establishment of vegetation in areas where there was none previously it can be concluded that the soil erosion structures are successfully curbing soil erosion in Mabula Private Game Reserve.
Professor J.T. Harmse

The objective of the study was to establish the behaviour and experience of tourists while visiting privately owned game lodges in Mpumalanga and the Northern Province. The theoretical objectives were to determine from a demand and a supply perspective what the phenomenon wildlife tourism entails. The aim was to unveil the consumer behaviour of wildlife tourists and to delineate the components and levels of the game lodge product. It was also deemed necessary to investigate wildlife utilisation issues in a South African context and to describe the tourism industry in South Africa with special reference to game lodges and ranches, and the holiday markets of Mpumalanga and the Northern Province. Lastly the complexities of marketing destinations and attraction products had to be uncovered. The objective of the empirical study was to ascertain what attracts visitors to game lodges, what they do and experience during the visit and what they find most appealing. The hypothesis was that wildlife tourists customise the components of the overall product which they consume in order to create memorable and differentiated experiences. Interviews with 68 visitors were held on location and at a regional airport who stayed at least one day and night at a lodge, and with 50 people who influenced the visitor experience, such as game rangers, tourist guides, managers, personnel, intermediaries and so forth. The findings contribute to an understanding of the features and benefits of the game lodge product from a visitor’s perspective. The core attraction for foreigners is to experience something unusual; to have an intimate new emotional experience. To go ‘on safari’ is in vogue and it satisfies a spirit of adventure, as well as a long held fascination with seeing animals in a genuine wilderness, especially the Big Five. Visitors want to live in a fantasy world of the past and share the animal’s world for a while. Whereas overseas visitors want to be busy and have a catered experience, South Africans want to confirm their emotional bond with Africa and experience timelessness and solitude amongst the animals; they want a being experience. Overseas visitors are on holiday and visiting a game lodge is part of a personal growth experience, whilst South Africans take short breaks and will return to for the genuine magic of the bush.
Prof. J.A. Bennett

In South Africa, conservation and tourism planning that incorporate local communities, has a greater significance today than before given the historical Apartheid legacy, which marginalised the majority of the population from democratic processes and economic opportunities. Community participation in the critical facets of conservation and tourism, that is planning, decision-making and management has been an object of research discourse for a long time. Issues around sustainability, governance, employment opportunity and equity, cost and benefit-sharing, land rights, capacity-building, active participation and conflicts have received great attention from scholars throughout the world. Externally-generated (observer) views on the nature and extent of local community participation in conservation and tourism management, more often than not, fail to depict the perceptions of the local residents. Explanations tend to be more prescriptive and are forced onto the stakeholders, who are directly affected by the circumstances around them. The voice of the local residents clearly articulates their views and attitudes much more than any other external views. The goal of this research study is to investigate the perceptions of local community on their participation in wildlife conservation, ecotourism and social development and the information gathered will be used to develop a new model for enhanced private sector-community collaboration and communication for sustainability. The study interrogates factors constraining collaboration, which include organisational culture, power differentials and communication, from the perspectives of stakeholders, especially the grassroots community. It engages with the community for its views and opinions and as a result, delivers valuable criticisms of and suggestions for the improvement of the process followed. A qualitative approach was adopted. Data collection and analysis methods were identified, explained, justified and implemented. This project is a Case Study, carried out in Umkhanyakhude District of KZN, in which Phinda Game Reserve and the surrounding local communities are located. Makhasa and Mnqobokazi are situated about 30-40 kilometres north-east of Hluhluwe, on the R22 Road that links the town with Sodwana Bay. Semi-structured individual and group interviews allow the study participants to identify and describe concerns or concepts that may not have been expected or considered by the researcher Interviews are of particular importance to ensure honesty and impartiality. Documentary analysis allowed to generate inferences through objective and systematic identification of core elements of a written communication. Observation was used to capture situations of interest not readily volunteered by the participants due to notable different views among members of the particular community. The Adapted Nominal Group Technique workshop was prepared and conducted, to augment the other methods. A multi-method approach ensured the reliability of the findings and the validity of both the approaches and the data collected. The historical background of &Beyond, its philosophy and journey towards sustainable wildlife conservation, tourism and social development was discussed. It was evident that due to the proximity of Makhasa and Mnqobokazi, activities of Phinda directly affected the communities and the same applies to those of the communities in Phinda. There was an apparent need to carefully and properly manage the cultural, socio-economic, political and spatial relationships to build a common understanding about roles and responsibilities of stakeholders in a mutually beneficial manner. The findings of the study illustrates that the perceptions and attitudes of the local residents on their participation in decision-making and management of conservation, tourism and social development are important for sustainability. The understanding of land rights issues was restricted to a few. While there was general appreciation for the activities of Phinda and Africa Foundation, the participants expressed their unfulfilled expectations, concerns and also made suggestions for a way forward to prevent conflict and ensure sustainable conservation and tourism. Skewed power relations, lack of participation in decision-making, poor governance, employment opportunities and equity, lack of transparency and poor communication strategies were among the main issues raised by the participants. Constructive criticism and recommendations, together with the Bending the Curve Model could serve as a valuable community engagement framework for private sector tourism companies and private game reserves to involve and work with surrounding communities to ensure more sustainable private game reserves in the future. The study recommends the model with some concrete, practical measures adapted from ideas of collaborative theory, for sustainable development
School of Agriculture and Environmental Sciences
Ph. D. (Environmental Management)