The aim of this study was to comparatively evaluate the Conservation Education programmes of the National Zoological Gardens of South Africa (NZG) in Pretoria, South Africa, the Uganda Wildlife Education Centre (UWEC) in Entebbe, Uganda and Zoo Negara in Kuala Lumpur in Malaysia, in order to devise a Model for an effective zoo Conservation Education Programme. A mixed-methods strategy, namely concurrent triangulation, was used for data-collection. The quantitative method was that of surveys by means of group-administered questionnaires. The population for the quantitative study was school groups that visited the zoos. The qualitative research questions were addressed by means of individual semi-structured interviews. Interpretive analysis was used to analyse the qualitative data. The participants of the qualitative study were staff members at the zoos and other key figures in the zoo – and conservation sector. The impact of Conservation Education programmes of the zoos were evaluated by means of a logic model. The quantitative results indicated that the Conservation Education programmes were successful in increasing the knowledge of the learners and in increasing their intention to change behaviour. This study further indicated that, although attending zoo Conservation Education programmes has the potential to increase the attitudes and values of learners, this was not always the case. Furthermore, the results show that when learners tested high with regard to their knowledge, attitudes and values prior to attending a Conservation Education programme, their knowledge, attitudes and values will not change significantly after they attended a Conservation Education programme. Furthermore, the results of the qualitative study indicated that the evaluation of Conservation Education programmes and the training of zoo educators should receive more attention to ensure the success of these programmes. It can be concluded that the role of zoos have become even more important to conserve biodiversity through their Conservation Education programmes. / Curriculum and Instructional Studies / D. Ed. (Didactics)

香港的山火主要是由於氣候及人類活動所引發，嚴重威脅著一些陸地上生物多樣性豐富的生境（如灌木林和林地）。在華南地區，有關火燒地的動物群落恢復生態學硏究的資料非常少，所以本硏究旨在調查山火後動物群落的復原，以及比較天然復原的林區及人工植林的生境恢復之差異。此外，枯枝落葉、物理因素及山火後的微生物對動物群落的影響亦會在此硏究中詳细分析。 / 在亞熱帶地區，地棲無脊椎動物群落的復原速度相對為慢，例如螞蟻群落需要12年的時間才能復原，但人工種植於火燒地能成功地加快其復原速度。 / 無脊椎動物群落與植被結構、山火之後的時間及生境發展都有一定的關係。山火發生兩年後火燒地的鳥類和無脊椎動物的數量、種或科的豐富度、單一性、多樣性及所有無脊椎動物的生物量都比參考樣地低，這意味著山火對動物群落有著長遠的影響。Pheidole spp. 及Tapinoma sp. 1 屬的螞蟻、隠翅甲科及小蠹科的甲蟲、管巢蛛科及狼蛛科的蜘蛛，牠們的數量，以及數量與生物量之比 (ABC plot) 都能用作反映火燒地的生態復原及演替進度的指標。 / 人工種植能夠使生態系統得到長遠的持續建立，對於動物群落的恢復非常重要。是次研究結果顯示人工種植能促進本地無脊椎動物的建群，其數量和群落亦會隨時間增加而增加。這很可能是由於山火後人工種植能為無脊椎動物創造較好的生存條件。其中，相對於原生樹種，外來樹種更有利於無脊椎動物的建群。在外來品種的人工種植區，微生物的數量較低，枯枝落葉的被分解速度較慢，加上生長速度快的外來品種能製造大量的枯枝落葉，這些都顯著增加了枯葉層的深度。較深的枯葉層為無脊椎動物提供了適宜的微生境，有利於其建群。 / 總的來說，在火燒地進行人工植樹能加快動物在火燒地的復原速度，這種方法是有效且成功的。人工種植時採用適當的品種能夠促進及預測早期的植被演替。根據此次硏究結果，我們建議在火燒地上種植生長快速的外來樹種，以加快無脊椎動物的建群。植被蓋度對動物的建群很重要，但植物和結構的多樣性及枯枝落葉層對無脊椎動物的建群更為重要。 / Hill fire in Hong Kong is mainly caused by a combination of weather and human activities. Fire is a major threat to terrestrial animal communities especially in shrublands and woodlands which have a rich faunal diversity. Since research done on hill fire ecology in southern China, especially on faunal colonization after fire, is very scarce, this research attempted to investigate the recovery of fauna after fire disturbance, and the difference in recovery between natural regeneration and artificial planting. Besides, the effects of litter and physical parameters on fauna community as well as the effect of fire on soil microbial community structure were studied. / The recolonization of ground-dwelling invertebrates was relatively slow in the study area, while proactive planting has been successful because they have considerably accelerated the return of fauna at the fire-affected sites. Ground-dwelling invertebrate communities appeared to be less resilient to fire in subtropical environment; the ant composition in the experimental plots needed 12 years to recover. / The composition of the ground-dwelling communities differed among study sites and was correlated with vegetation structure and time since last fire. They showed the trends in the development of invertebrate community composition in association with habitat development. Abundance, species/family richness, evenness, diversity of birds and ground-dwelling invertebrates, and biomass of total invertebrates were lower on the burned site than the reference site even 2 years after fire, implying that fire had longer-term impacts on the faunal communities. Ants such as Pheidole spp., Tapinoma sp. 1, beetles such as Staphylinidae, Scolytidae, and spiders such as Clubionidae, Lycosidae, as well as the abundance biomass comparison (ABC plot) can be chosen to reflect the situation or the recovery process and succession of the fire-affected sites. / The establishment of fauna in proactive planting is vital if ecosystem functions are to be reestablished and restorations to be sustained in the long term. In general the invertebrate data suggest that restoration plantings facilitated the reestablishment of indigenous invertebrate species and invertebrate community changed with time. Proactive plantings created better conditions for ground-dwelling invertebrates after fire, and exotic species with faster growth rate seem to be better than the natives. In exotic plantations, lower decomposition rate of litter provided by the lower microbial population together with higher productivity of exotic species of plants caused a higher litter depth, which provided more microhabitats for ground-dwelling and litter-dwelling invertebrates than the native plantations. / Correct species selection in proactive planting is essential to facilitate and determine the early stages of plant succession. The present study suggests that initial floristic composition is significant in proactive plantings and exotic species with fast growth rate is an effective planting species for invertebrate recolonization. Although plant cover is of importance to developing fauna, the provision of adequate floristic and structural diversity and the presence of logs and litter are important for the full range of native invertebrate recolonization. / Detailed summary in vernacular field only. / Detailed summary in vernacular field only. / Detailed summary in vernacular field only. / Detailed summary in vernacular field only. / Detailed summary in vernacular field only. / Cheung, Kwok Leung. / Thesis (Ph.D.)--Chinese University of Hong Kong, 2012. / Includes bibliographical references (leaves 192-219). / Electronic reproduction. Hong Kong : Chinese University of Hong Kong, [2012] System requirements: Adobe Acrobat Reader. Available via World Wide Web. / Abstract also in Chinese; some appendixes also in Chinese. / Abstract --- p.i / Acknowledgements --- p.vi / Table of contents --- p.vii / List of figures --- p.x / List of plates --- p.xvi / List of appendices --- p.xvii / Chapter Chapter 1 --- General Introduction --- p.1 / Chapter 1.1 --- Ecology of Fire --- p.1 / Chapter 1.2 --- Effects of Hill Fire on Soil --- p.3 / Chapter 1.3 --- Effects of Hill Fire on Microbial Communities --- p.7 / Chapter 1.4 --- Effects of Hill Fire on Vegetation --- p.10 / Chapter 1.5 --- Effects of Hill Fire on Fauna Communities --- p.14 / Chapter 1.6 --- The Use of Bioindicators on Restoration Ecology --- p.19 / Chapter 1.7 --- Hill Fire Situation and Research in Hong Kong --- p.23 / Chapter 1.8 --- Study Objectives --- p.28 / Chapter Chapter 2 --- Faunal Colonization after Fire Disturbance --- p.30 / Chapter 2.1 --- Introduction --- p.30 / Chapter 2.2 --- Materials and Methods --- p.32 / Chapter 2.2.1 --- Study sites --- p.32 / Chapter 2.2.2 --- Measurements of soil physicochemical parameters --- p.35 / Chapter 2.2.3 --- Determination of vegetation parameters --- p.36 / Chapter 2.2.4 --- Monitoring of vertebrate communities --- p.36 / Chapter 2.2.5 --- Sampling, sorting and identification of invertebrates --- p.37 / Chapter 2.2.6 --- Data analysis --- p.38 / Chapter 2.3 --- Results --- p.41 / Chapter 2.3.1 --- Soil physicochemical characteristics --- p.41 / Chapter 2.3.2 --- Vegetation parameters --- p.42 / Chapter 2.3.3 --- Vertebrate communities --- p.44 / Chapter 2.3.4 --- Invertebrate communities --- p.47 / Chapter 2.4 --- Discussion --- p.58 / Chapter 2.5 --- Conclusions --- p.66 / Chapter Chapter 3 --- Effect of Different Planting Approaches on Invertebrates --- p.68 / Chapter 3.1 --- Introduction --- p.68 / Chapter 3.2 --- Materials and Methods --- p.70 / Chapter 3.2.1 --- Study sites --- p.70 / Chapter 3.2.2 --- Proactive planting --- p.71 / Chapter 3.2.3 --- Measurement of soil, vegetation, and faunal parameters, and data analysis --- p.73 / Chapter 3.3 --- Results --- p.75 / Chapter 3.3.1 --- Soil physicochemical parameters --- p.75 / Chapter 3.3.2 --- Vegetation parameters --- p.77 / Chapter 3.3.3 --- Invertebrate communities --- p.78 / Chapter 3.4 --- Discussion --- p.92 / Chapter 3.5 --- Conclusions --- p.98 / Chapter Chapter 4 --- Long-term Changes of Invertebrate Community after Hill Fire by a Retrospective Approach --- p.100 / Chapter 4.1 --- Introduction --- p.100 / Chapter 4.2 --- Materials and Methods --- p.102 / Chapter 4.2.1 --- Study sites --- p.102 / Chapter 4.2.2 --- Measurement of soil physicochemical parameters --- p.102 / Chapter 4.2.3 --- Determination of vegetation parameters --- p.103 / Chapter 4.2.4 --- Collection, sorting and identification of invertebrates --- p.104 / Chapter 4.2.5 --- Data analysis --- p.104 / Chapter 4.3 --- Results --- p.105 / Chapter 4.3.1 --- Soil physicochemical characteristics --- p.105 / Chapter 4.3.2 --- Vegetation parameters --- p.106 / Chapter 4.3.3 --- Invertebrate communities --- p.110 / Chapter 4.4 --- Discussion --- p.123 / Chapter 4.5 --- Conclusions --- p.133 / Chapter Chapter 5 --- Relationship of Microbial Community with Recolonization of Invertebrates --- p.135 / Chapter 5.1 --- Introduction --- p.135 / Chapter 5.2 --- Materials and Methods --- p.139 / Chapter 5.2.1 --- Study sites --- p.139 / Chapter 5.2.2 --- Microbial biomass carbon (C[subscript mic]) and nitrogen (N[subscript mic]) --- p.139 / Chapter 5.2.3 --- Fatty acid methyl esters (FAME) extraction --- p.140 / Chapter 5.2.4 --- Data analysis --- p.141 / Chapter 5.3 --- Results --- p.142 / Chapter 5.3.1 --- Fumigation-extraction --- p.142 / Chapter 5.3.2 --- Fatty acid methyl esters --- p.144 / Chapter 5.3.3 --- Relationship of microbial communities with physicochemical, vegetation and invertebrate parameters --- p.145 / Chapter 5.4 --- Discussion --- p.152 / Chapter 5.5 --- Conclusions --- p.159 / Chapter Chapter 6 --- Effects of Critical Factors on Invertebrate Communities --- p.160 / Chapter 6.1 --- Introduction --- p.160 / Chapter 6.2 --- Materials and Methods --- p.162 / Chapter 6.2.1 --- Experimental sites --- p.162 / Chapter 6.2.2 --- Critical factors selection and simulation --- p.163 / Chapter 6.2.3 --- Measurement of microclimatic characteristics --- p.165 / Chapter 6.2.4 --- Collection, sorting and identification of invertebrates --- p.166 / Chapter 6.2.5 --- Data analysis --- p.166 / Chapter 6.3 --- Results --- p.167 / Chapter 6.3.1 --- Microclimatic characteristics --- p.167 / Chapter 6.3.2 --- Invertebrate communities --- p.168 / Chapter 6.4 --- Discussion --- p.173 / Chapter 6.5 --- Conclusions --- p.178 / Chapter Chapter 7 --- General Conclusions --- p.180 / Chapter 7.1 --- Overall Discussion --- p.180 / Chapter 7.2 --- Limitation of the Present Study and Future Research --- p.184 / Chapter 7.3 --- Contributions to Our Knowledge --- p.188 / Reference --- p.192 / Appendices --- p.220

Habitat loss and fragmentation is a crisis affecting wildlife worldwide. In Tanzania, East Africa, a dramatic and recent (<80 years) expansion in human settlement and agriculture threatens to reduce gene flow among protected areas for many species of large mammals. Wildlife linkages can mitigate population isolation, but linkage designs lacking empirical justification may be controversial and ineffective. Connectivity conservation requires an understanding of how biogeographic factors shaped gene flow prior to habitat loss or fragmentation, however the history of interaction among populations is rarely known. The goal of my study was to provide context for connectivity conservation in central and southern Tanzania by identifying landscape features that have shaped gene flow for three ungulate species with different dispersal capabilities. I investigated historical patterns of connectivity for Maasai giraffe (Giraffa camelopardalis tippelskirchi), impala (Aepyceros melampus), and eland (Tragelaphus oryx) by estimating genetic structure among four to eight protected areas per species. Genetic structure changes very slowly among large populations and thus is likely to reflect historical processes instead of recent anthropogenic influences. I collected noninvasive DNA samples and generated microsatellite genotypes at 8 to 15 loci per species, then estimated genetic diversity metrics (allelic richness, AR, and expected heterozygosity, H[subscript E]) for each population (defined by reserve). I also calculated genetic distance (F[subscript ST] and Nei's unbiased genetic distance, D[subscript hat]) and an estimate of gene flow (Nm) between all population pairs for each species. To elucidate the possible causes of genetic structure between these populations, I tested for isolation by distance and isolation by resistance based on a suite of biogeographic factors hypothesized to affect gene flow. To do this, I created GIS-based resistance surfaces that assigned different costs of movement to landscape features. I created one or more resistance surfaces for each hypothesis of landscape effect. I used circuit theory to estimate the cumulative resistance between each pair of reserves for each weighting scheme, and then performed Mantel tests to calculate the correlation between these resistances and the observed population pairwise genetic distances (D[subscript hat]). I chose the optimal resistance model for each species as the model that was most highly correlated with observed genetic patterns. To verify that the correlation of resistance models with genetic distance was not an artefact of geographic distance, I performed partial Mantel tests to calculate correlation while controlling for the effect of geographic distance. Finally, I compared historical gene flow patterns to the distribution of contemporary human activity to predict areas that are at risk of a loss of connectivity. Indices of genetic diversity were moderate for all three species and comparable to previously reported values for other savannah ungulates. Diversity (both H[subscript E] and A[subscript R]) was highest in eland and lowest in giraffe for these populations, and was not consistently correlated with reserve size as has been reported for other species in East Africa. Although patterns in genetic distance were broadly similar across all three species there were also striking differences in connectivity, highlighting the importance of cross-species comparisons in connectivity conservation. At this scale, resistance models based on slope strongly predicted population structure for all three species; distance to water was also highly correlated with genetic distance in eland. For all three species, the greatest genetic distances occurred between populations separated by the Eastern Arc Mountains, suggesting that the topography of this area has long acted as a barrier to gene flow, but this effect is present in varying degrees for each species. I observed high levels of historical gene flow between centrally located populations (Ruaha National Park and Rungwa Game Reserve) and those in the southwest (Katavi National Park and Rukwa Game Reserve). Although human settlement in this area has been low relative to other areas, the connection between the Katavi/Rukwa and Ruaha ecosystems may be threatened by increased human activity and warrants conservation. High levels of historical gene flow were also seen between reserves in the northeast (Tarangire National Park, Swagaswaga Game Reserve) and the central and southwest populations. These connections appear highly threatened due to current land use practices, and may have already suffered a loss of gene flow. Field surveys in the lands surrounding the northeastern reserves are needed to quantify current levels of connectivity and determine whether corridors could be established to maintain or restore gene flow with other reserves. / Graduation date: 2012

Please read the abstract in the section 00front of this document / Thesis (DPhil (Zoology))--University of Pretoria, 2005. / Zoology and Entomology / unrestricted

Thesis (M.Sc. (Geography)) -- University of Limpopo, 2020 / This work aimed at assessing the implications of involving local communities in biodiversity conservation in Blouberg Nature Reserve (BNR) in Limpopo Province, South Africa. To achieve this objective, firstly biodiversity status before and after involving local communities in conservation initiatives was assessed using multi-temporal medium-resolution Landsat series data and species diversity indices. The results showed that there were significant variations (α = 0.05) in tree species diversity in BNR for before and after involving local communities. For example, tree species diversity was low after involving communities particularly for the years 1996 and 2019. Secondly, benefits and costs of involving local communities in biodiversity conservation as well as their investigate views, perceptions and attitudes BNR management were assessed. The study demonstrated local communities do not obtain sufficient benefits or incur numerous costs from the nature reserve. Despite this, there was considerable support for biodiversity conservation (84.2%) since household respondents still held positive attitudes towards biodiversity conservation in the reserve. For, example most of them indicated that they would report illegal activities to the authorities. However, despite lack of participation by the majority of the household respondents (89.6%) in biodiversity conservation, they demonstrated understanding of the relevance of nature conservation. In contrary, the BNR Manager stated that the local communities received benefits in the form of fuel-wood for special occasions such as funerals and bush meat sold at treasury approved tariffs during culling. However, illegal activities like poaching are still experienced in the nature reserve. Thus, the study underscores the relevance the integrating satellite data and qualitative information in assessing the ecological condition of PAs. Such information can help in biodiversity monitoring and decision-making on conservation of biodiversity. Keywords: biodiversity conservation; community-based natural resource management approach; ecological status; mapping; satellite data; spatial characterisation; species diversity; statistical analysis.

La connaissance de la dynamique des écosystèmes forestiers face à l’anthropisation est plus qu’indispensable à l’établissement de bases satisfaisantes pour leur utilisation durable et rationnelle. Ces perturbations anthropiques sont à la base de la fragmentation des forêts et de l’augmentation des lisières. Ainsi, depuis plus de trois-quarts de siècle la notion de « lisière » préoccupe la communauté scientifique. La grande diversité des espèces qui lui est associée est connue comme le principe de « l’effet de lisière » et est largement considéré comme un concept fondamental de l’écologie. Après l’énonciation de ce principe, les gestionnaires de la faune avaient estimé créer autant de lisières que possible du fait que la plus grande diversité de la faune y était observée. Paradoxalement, en accordant plus l’accent sur la faune au cours des deux dernières décennies, nombreuses caractéristiques des lisières, désormais considérées comme néfastes, ont été mises en évidences. C’est ainsi que des études sur la compréhension des réponses écologiques de la faune face aux lisières se sont multipliées afin de parvenir aux recommandations adéquates pour une meilleure conservation. La présente étude a pour but de tester si les Rongeurs peuvent servir comme bioindicateurs des effets de lisière dans la forêt de Masako. Les captures ont été faites durant 38 mois à l’intérieur de 4 grilles d’échantillonnage (1 ha/grille/habitat) installées dans une forêt à Gilbertiodendron dewevrei, une forêt secondaire vieille, une jachère d’au moins 5 ans et une lisière jachère/forêt secondaire. Les espèces ont été identifiées à l’aide de données morphométriques et d’analyses moléculaires (ADN du Cyt b). La richesse, la diversité, la densité, les abondances, le sex-ratio et la structure d’âges des espèces capturées ont été analysés. Une richesse et une diversité élevées sont observées dans la lisière probablement suite à son hétérogénéité et à la présence d’une diversité de niches sur une surface réduite. Les abondances de différentes espèces y sont en général faibles mais quelques fois intermédiaires ou similaires à celles des milieux adjacents. Quatre groupes d’espèces ont été distingués :(i) les généralistes ;(ii) celles qui évitent la lisière (faibles abondances dans la lisière) ;(iii) celles ayant des abondances distinctes selon les habitats ;(iv) celles ayant des abondances intermédiaires dans la lisière. L’étude a montré que les Rongeurs pourraient bien servir comme bioindicateurs des effets de lisière. Leur diversité et abondance étant des paramètres prioritaires à analyser. / Doctorat en Sciences agronomiques et ingénierie biologique / info:eu-repo/semantics/nonPublished