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Lake Kariba Fisheries –Zimbabwe








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    Meeting
    Meeting document
    Lake Kariba Fishery –Zambia 2014
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    Technical report
    Report of the second Technical Consultation on the Development and Management of the Fisheries of Lake Kariba. Kariba, Zimbabwe, 30 November-1 December 2004. 2005
    This document is the final report of the second Technical Consultation on the Development and Management of the Fisheries of Lake Kariba. The major topics discussed were an overview on the importance of co-management as a tool for sustainable fisheries management and development in Zambia and Zimbabwe; fishers’ views on the importance of the kapenta fishery and the artisanal fishery; status of fisheries on the Zambia and Zimbabwe side of Lake Kariba; and an overview on the management and develop ment of the fisheries of Lake Kariba. The summary of the main recommendations and decisions is shown in Appendix D.
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    Book (series)
    Technical report
    Bioeconomic Analysis of the Kapenta Fisheries. Lake Kariba, Zimbabwe and Zambia
    GCP/RAF/466/EC SmartFish Project
    2012
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    FAO supports a joint management process and the development of fisheries on Lake Kariba between Zimbabwe and Zambia. The 4th Technical Consultation Meeting, held in Kariba in 2010, recommended the development of bioeconomic modelling of Kapenta fishery (Limnothrissa miodon). In support of this recommendation, a first field mission was conducted in November 2012 with the support of the SmartFish project. The objective of this mission was to meet with key stakeholders in the public and private sec tors involved in the Kapenta fishery in the two countries in order to:  inform them about the bioeconomic assessment exercise to be carried out on the Kapenta fishery;  underline the importance of their collaboration, in particular the provision of reliable data to fit the model;  find out more about the Kapenta fishery and current challenges;  gather key documents and information required for the bioeconomic modelling;  assess the quality of information requested for the bioeconomic modell ing and identify any gaps;  draft the Terms of Reference for National Consultants who will be responsible for the collection of additional information after the mission. Based on meetings with key officials in charge of the management of the fisheries and with leaders of fishing enterprises in the two countries, the main results of the mission indicate that:  The fishing capacities in the Kapenta fishery have greatly increased since the early 2000s, from approximately 600 rigs allowed on the l ake in 1999 to 1,098 in 2012 (5th Technical Consultation Meeting, 2012). There are also an unknown number of unregistered and unlicensed rigs (illegal, unreported and unregulated fishing);  The fishing effort, reported by the fishing companies, has subsequently increased dramatically (40 percent increase between 2000 and 2011);  The management system in the two countries is based on a licensing system and the payment of an annual fee for access to the fishery, as well as several technical mana gement measures (mesh size, zoning, and brief closures based on the lunar calendar). The industry is also obliged to record and transfer to the management authorities monthly data on their catch and fishing effort. In practice, it seems that there are no real access controls and poor enforcement of regulations. Thus, the fishery currently appears to be open and free for all.  4  The harvesting systems and the technical productivity of fleets in the two countries are relatively homogeneous. C atches per unit of effort have fallen by 35 to 50 percent since 2005;  Qualitative indicators based on the situation of fishing enterprises show that the Kapenta fishery is overfished and revenue from resources is widely dissipated;  Statistical data available on effort, catch and CPUE, as well as scientific knowledge on biological parameters of the Kapenta stock suggest that only a biological modelling based on a surplus production model (such as Schaeffer, Fox, etc.) is possible;  There is an important shortage of economic data on time series concerning ex- vessel prices, costs related to the activities of fishing enterprises, their investment, and their profitability. Consequently, the work of two national consultants to support this process will mainly be focused on the collection of economic data in order to estimate an average cost per unit of effort (night fished per rig) in each country and for each fishing zone. Key documents for the bioeconomic modelling were collected bef ore and during the mission (or just after). A complete list of these documents can be found in Annex C. These key documents and references will form the basis of bibliographical references for the modelling exercise. A questionnaire was developed to collect missing information for the bioeconomic modelling exercise (Annex E). This information was obtained from a field survey and from a sample of fishing companies of different sizes and operating in different fishing areas (Basin/Stratum) in the two countries. A sampling plan was made on the basis of data from the frame survey undertaken with FAO support in 2011. However, it is strongly suggested that this economic fieldwork will be conducted in close cooperation with those responsible for the Kapenta producer organizations in Zambia and Zimbabwe; on one hand for the selection of those companies to be interviewed and to facilitate contacts, and on the other hand, to ensure the quality of data to be collected and transmitted. Forthcoming steps for the continuation of the process leading to the bio economic modeling workshop were also defined, as well the format of the workshop.

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    Technical report
    Report of the Africa Regional Consultative Meeting on Securing sustainable small-scale fisheries: bringing together responsible fisheries and social development, Maputo, Mozambique, 12-14 October 2010. / Rapport de l’atelier consultatif régional africain sur les pêches artisanales pour une pêche artisanale durable: associer la pêche responsable au développement social, Maputo, Mozambique, 12-14 octobre 2010. 2011
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    The African workshop was one of three regional consultative workshops carried out as a follow-up to the 2009 inception workshop of the FAO Extra-Budgetary Programme on Fisheries and Aquaculture for Poverty Alleviation and Food Security. The workshops built on the outcomes of the Global Conference on Small-Scale Fisheries held in Bangkok in October 2008 and referred to the recommendations made by the 26th Session of the FAO Committee on Fisheries (COFI) in March 2009 with regard to the potential development of an international instrument and programme for small-scale fisheries. The purpose of the workshops was to provide guidance on the scope and contents of such an international small-scale fisheries instrument and on the possible priorities and implementation modalities for a global assistance programme. It was organised around plenary presentations on key subjects and working group discussions. The workshop agreed that an international instrument on small-scale fisheries and a rela ted programme would be important tools for securing sustainable small-scale fisheries. It recommended that a small-scale fisheries international instrument and assistance programme should be informed by human rights principles and existing instruments relevant to good governance and sustainable development, comprise the ecosystem approach to fisheries (EAF) as a guiding principle for resource management and development and incorporate Disaster Risk Management (DRM) and Climate Change Adaption (C CA) as an integral part considering that DRM is a continuum process, before, during and after a disaster. The workshop recognised the value and worldwide acceptance of the Code of Conduct for Responsible Fisheries and strongly felt that a small-scale fisheries instrument should be closely aligned to the Code. The instrument should build on what already exists and use a similar language to the Code. In developing the instrument, reference should be made not only to States but also to other sta keholders, recognizing the shared responsibility with regard to resource sustainability and livelihood security. Local, national and regional ownership should be ensured. Implementation aspects should be considered already at the design stage, including the need for technical guidance and supportive mechanisms. Results monitoring should be based on well-defined impact indicators and be an integral part of the implementation modalities.
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    Guideline
    Développement de l’aquaculture. 4. Une approche écosystémique de l’aquaculture. 2011
    Les dimensions sociales et biophysiques des écosystèmes sont inextricablement liées de telle manière qu’un changement dans une seule dimension est très susceptible de générer un changement dans une autre. Bien que le changement est une conséquence naturelle des interactions complexes, il doit être surveillé et même géré si le taux et la direction du changement risquent de compromettre la résilience du système. “Une approche écosystémique de l’aquaculture (AEA) est une stratégie pou r l’intégration de l’activité dans l’écosystème élargi de telle sorte qu’elle favorise le développement durable, l’équité et la résilience de l’interconnexion des systèmes socio-écologiques.” Etant une stratégie, l’approche écosystémique de l’aquaculture (AEA) n’est pas ce qu’on a fait, mais plutôt comment on l’a fait. La participation des parties intéressées est à la base de la stratégie. L’AEA exige un cadre politique approprié dans lequel la stratégie se développe en plusieurs é tapes: (i) la portée et la définition des limites des écosystèmes et l’identification de la partie intéressée; (ii) l’identification des problèmes principaux; (iii) la hiérarchisation des problèmes; (iv) la définition des objectifs opérationnels; (v) l’élaboration d’un plan de mise en oeuvre; (vi) le processus de mise en oeuvre correspondant qui comprend le renforcement, le suivi et l’évaluation, et (vii) un critique des politiques à long terme. Toutes ces étapes sont informées par les meilleures connaissances disponibles. La mise en oeuvre de l’AEA exigera le renforcement des institutions et des systèmes de gestion associés de sorte qu’une approche intégrée du développement de l’aquaculture peut être mise en oeuvre et compte entièrement des besoins et des impacts d’autres secteurs. La clé sera de développer des institutions capables d’intégration, notamment en fonction des objectifs et des normes convenus. L’adoption généralisée d’une AEA exigera un couplag e plus étroit de la science, la politique et la gestion. Elle exige aussi que les gouvernements incluent l’AEA dans leurs politiques de développement de l’aquaculture, stratégies et plans de développement.
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    Booklet
    Corporate general interest
    Emissions due to agriculture
    Global, regional and country trends 2000–2018
    2021
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    The FAOSTAT emissions database is composed of several data domains covering the categories of the IPCC Agriculture, Forestry and Other Land Use (AFOLU) sector of the national GHG inventory. Energy use in agriculture is additionally included as relevant to emissions from agriculture as an economic production sector under the ISIC A statistical classification, though recognizing that, in terms of IPCC, they are instead part of the Energy sector of the national GHG inventory. FAO emissions estimates are available over the period 1961–2018 for agriculture production processes from crop and livestock activities. Land use emissions and removals are generally available only for the period 1990–2019. This analytical brief focuses on overall trends over the period 2000–2018.