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

Draft Environmental Profile of Zambia

Speece, Mark W., University of Arizona. Arid Lands Information Center. 03 1900 (has links)
Prepared by the Arid Lands Information Center, Office of Arid Lands Studies, University of Arizona ; Mark W. Speece, compiler.
2

A systemic approach for assessing community-based natural resource management : a case study of the Kafue Flats, Zambia.

Nkhata, Bimo Abraham. January 2002 (has links)
This dissertation seeks to expose through a systemic approach the complexity and centrality of governance in community-based natural resource management (CBNRM). This is premised on the hypothesis that an appreciation of this complexity and of drawing analytic distinctions between governance and management is necessary for successful interventions. The study adopts community-based environmental governance (CBEG) as the core heuristic variable in a conceptual framework for analysing CBNRM. The application of this framework generates empirical evidence concerning CBNRM processes adopted in the Kafue Flats socio-biophysical system. It is illustrated that CBNRM processes are established and implemented in a complex context. It is observed that social actors on the Kafue Flats usually do not constructively understand and appreciate this complexity. Several examples are demonstrated in which the thinking and actions of these actors reflect a limited conceptual framework of systems thinking and the inherent complexity in CBNRM. It is illustrated that these actors do not appreciate that CBNRM is a significant component of the governance of natural resource utilisation. This lack of appreciation is essentially identified as a contributing factor to poor performance. Ultimately, CBNRM processes are not only about sustainable use of natural resources; but also the nature and quality of relationships amongst social actors in CBEG. By drawing attention to these relationships, this study broadens our understanding of what goes into CBNRM processes. The implications of ignoring these relationships can be detrimental to the success of CBNRM. Accordingly, the establishment of productive CBNRM systems depends on how firmly CBEG issues and concerns are incorporated into CBNRM analyses and operations. Evidently, CBNRM cannot be pragmatically pursued in rigid socio-biophysical settings. It requires systemic and structural changes in the socio-political, economic and cultural mechanisms of CBEG. Thus, all cooperating partners, governments included, should accept that CBEG and CBNRM are inseparable. This understanding necessitates them to spearhead CBEG capacity building schemes at international, national and local levels. / Thesis (M.Env.Dev.)-University of Natal, Pietermaritzburg, 2002.
3

An assessment of the implementation of the community environmental management programme in Zambia : a case study of Luansobe Settlement - Mufulira district.

January 2004 (has links)
This dissertation comprises two components. Component A consists of background to the research and includes the problem statement, aim and objectives. It also includes the literature review, which provides details on the concept of community-based natural resources management (CBNRM) and its benefits as a participatory approach adopted in the management of natural resources. Component B is presented as a research paper that complies with the requirements of the selected journal for purposes of publication shown in appendix I. Relevant information on the purpose of the study and background to the concept of CBNRM from component A is included in component B for purposes of the research paper. It also includes research findings, analysis and conclusions of the study. CBNRM has been identified as a feasible participatory approach to natural resources management based on community needs and priorities. This research reviews the implementation of the Community Environmental Management Programme (CEMP) as a participatory approach adopted by the Zambian Government to address growing environmental concerns, with particular reference to deforestation, as a result of human activities. This study focuses on Luansobe settlement in Mufulira district, one of eight districts in which the CEMP is being implemented as a pilot project. Luansobe is located in the peri-urban area of Mufulira. The majority of the people living in the area are unemployed and live below the poverty datum line. These people are largely dependent on natural resources for their livelihoods. Unfortunately, some of the activities people are engaged in are having adverse impacts on the resources, in particular forest resources. The main sources of livelihoods are charcoal production and subsistence farming, which are contributing greatly to the deforestation of the surrounding Nsato Forest Reserve. The CEMP is intended to set up institutional structures at national, district and community levels to address the problem of deforestation and the related poverty levels. This is under the premise that this situation can be improved with good management and community involvement. The study reviewed literature on the concept of CBNRM with particular reference to co-management as one form of a participatory approach with shared responsibility on the management of natural resources between government and local communities. The significance of community involvement in the use and management of forest resources is highlighted. The factors necessary for the effective implementation of joint management programmes are also highlighted and their importance in achieving conservation, community development and good governance. A case study was reviewed to show the importance of these indicators to the successful implementation of such participatory programmes. A list of indicators was compiled as the basis for the assessment of the implementation of the CEMP. A review of government documents provided background information on the establishment of the CEMP, the need for its implementation in Luansobe and the structures put in place at national, district and community levels to implement the programme. These data were supplemented by information gathered through semi-structured interviews with purposively selected key informants and workshops with local community members. Information obtained showed that the institutional structures implementing the CEMP on the ground are different from those set out in documents and are deficient of communication links among the stakeholders, especially community members. This has had negative effects on the representativeness of decisions made regarding the implementation of the programme and accountability of leaders to community members. This has further affected the implementation of projects under the CEMP intended to improve people's livelihoods through alternative sources of income that promote the sustainable use of forest resources. / Thesis (M.Sc.)- University of KwaZulu-Natal, Pietermaritzburg, 2004.
4

Fish and fisheries of Bangweulu wetlands, Zambia

Huchzermeyer, Carl Friedrich January 2013 (has links)
Bangweulu Wetlands is a 6000 km² public-private-partnership conservation area in northeastern Zambia, lying on the south-eastern margins of the Bangweulu Swamps, Congo River system. The area is important for wildlife conservation, tourism and as a fishing ground for the local inhabitants. This study provides a baseline of the fish and fisheries of this area. The conservation area is situated on the transition zone between woodland, floodplain and swamp. A total of 42 fish species representing 12 taxonomic families were collected. The fish fauna of the area was characterised by a diversity of small cyprinids (14 species), cichlids (9 species), clariid catfishes (4 species) and mormyrids (4 species). Species such as Clarias gariepinus, C. ngamensis, Marcusenius macrolepidotus, Tilapia rendali, T. sparrmanii and several small Barbus species were shared with adjacent floodplain systems such as the upper Zambezi and Kafue rivers. Fishing was undertaken by fishing groups consisting of a fisherman and his family, or a group of men fishing together. Access to the fishing grounds was controlled by traditional fishing leaders, who collected tribute from fishermen. Fishing groups utilised fixed, distinct fishing areas determined by ancestry. The most important time for fishing was during the drawdown phase of the floodplains, from March until June. During the dry season fewer groups were engaged in fishing, with many having returned to farming activities. The main fishing methods of the floodplain fishery were basket traps and mosquito-mesh funnel nets set into earth fish barriers (fish weirs) constructed on the plains, various mesh sizes of gillnets, hook longlines and seine nets. The use of fish spears, drag baskets and piscicides was of lesser importance. Most fishing gears were constructed of a variety of natural and modern, manufactured materials. The fishery was multi-species and 23 fish species were recorded from in catch. The three most important species in the catches were C. gariepinus, T. rendalli and M. macrolepidotus. Together these contributed 67% by weight to the catch. Catch-per-unit-effort (CPUE) for the different gears was 0.4 ± 0.3 kg.trap.night⁻¹ for basket traps, 2.7 ± 4.6 kg.net.night⁻¹ for funnel nets, 0.3 ± 0.5 kg.50 m net.night⁻¹ for gill nets, 3.5 ± 6.3 kg.100 hooks.night⁻¹ for longlines, 1.79 ± 1.11 kg.haul⁻¹ for mosquito-mesh seine nets and 6.87 ± 6.27 kg.haul⁻¹ for larger-mesh seine nets. The weight of average daily landings of fishing groups, using a variety of gears was 7.8 ± 7.4 kg. Fishermen were able to maintain the same catch rate between dry and wet seasons, with no significant differences (p < 0.05) in daily landings between seasons. Yield per fisherman for a seven month season, which required 2-3 relocations due to falling water level, was 1.64 t based on catch assessment, and 1.9 t from a socio-economic survey. A tentative yield per area estimate for the area was 2I7 kg.ha⁻¹ over the three month shallow-floodplain fishing season. Most fish landed in the fishery were processed into sundried or smoke-dried products. These were used for 1) home consumption, 2) trade with village farmers (from up to 70 km inland of the fishing grounds) in exchange for staple starch meal, and 3) sold to urban fish traders, reaching markets as distant as Lubumbashi in Democratic Republic of Congo. Fish traders toured fishing camps to buy fish, supporting auxiliary industries such as transport and accommodation services. The price for dried fish at source was 3.14 ± 1.34 USDlkg and the market price reported for the Zambian Copperbelt was 6.14 ± 2.54 USD/kg. Typical returns on investment in fish trading were estimated as 68-77%. The fishery was considered to be biologically and socially sustainable. By harvesting a seasonally transient assemblage of species with high productivity and biological turnover rates and with life histories adapted to high mortality, fishermen were able to maintain a stable and viable livelihood. Management recommendations for the area were that a fisheries management plan be developed that would seek to strengthen the traditional system of rights-allocation, address problems between fishing and tourism activities, and enhance communication between fisheries and conservation stakeholders. To do this it was recommended that: 1) conservation authorities recognise the importance of the fishery, 2) no changes to current effort levels and fishing methods were necessary, 3) points 1 and 2 above be used to improve communication and trust between conservation authorities and fishermen, 4) customary resource-access mechanisms be understood and strengthened so that local inhabitants' rights to the resource are protected, 5) fishermen help formulate and accept conservation and tourism rules, 6) tourists and guides be made aware of the function of the fishery, 7) a fisheries management forum of key community, government and conservation stakeholders be formed to shape and implement the fisheries management plan, 8) locally-adapted bylaws be created to legitimise crucial floodplain gears currently considered illegal (e.g. mosquito-net gears, fish weirs), 9) no intervention to formalise fish trading be made, and 10) a trained person with a fisheries background be hired oversee the implementation of the recommendations.

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