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Lake Kariba Fisheries –Zimbabwe








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    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
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    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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    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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    This document provides a global overview of beach seine fisheries and identifies key issues relevant for the responsible use of beach seines and the sustainable livelihoods of beach seine fishers. It also gives guidelines for fisheries managers and other stakeholders on how best to address the issues of management processes and measures, which have the mutually beneficial goals of restoring and conserving the health of fishery resources and their habitats and safeguarding the livelihoo ds of fishers and their communities. The document draws on the findings of case studies coordinated and funded by the Food and Agriculture Organization of the United Nations (FAO) Fisheries and Aquaculture Department in the Gambia, India, Kenya, Mozambique, Peru and Sri Lanka, and by the FAO/United Kingdom Department for International Development (DFID) Sustainable Fisheries Livelihoods Programme (SFLP) in Benin, Ghana and Togo. In addition to the findings of the case studies, other studies and publications on beach seines were reviewed and used for the preparation of this document.
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    The State of Food Security and Nutrition in the World 2021
    Transforming food systems for food security, improved nutrition and affordable healthy diets for all
    2021
    In recent years, several major drivers have put the world off track to ending world hunger and malnutrition in all its forms by 2030. The challenges have grown with the COVID-19 pandemic and related containment measures. This report presents the first global assessment of food insecurity and malnutrition for 2020 and offers some indication of what hunger might look like by 2030 in a scenario further complicated by the enduring effects of the COVID-19 pandemic. It also includes new estimates of the cost and affordability of healthy diets, which provide an important link between the food security and nutrition indicators and the analysis of their trends. Altogether, the report highlights the need for a deeper reflection on how to better address the global food security and nutrition situation.To understand how hunger and malnutrition have reached these critical levels, this report draws on the analyses of the past four editions, which have produced a vast, evidence-based body of knowledge of the major drivers behind the recent changes in food security and nutrition. These drivers, which are increasing in frequency and intensity, include conflicts, climate variability and extremes, and economic slowdowns and downturns – all exacerbated by the underlying causes of poverty and very high and persistent levels of inequality. In addition, millions of people around the world suffer from food insecurity and different forms of malnutrition because they cannot afford the cost of healthy diets. From a synthesized understanding of this knowledge, updates and additional analyses are generated to create a holistic view of the combined effects of these drivers, both on each other and on food systems, and how they negatively affect food security and nutrition around the world.In turn, the evidence informs an in-depth look at how to move from silo solutions to integrated food systems solutions. In this regard, the report proposes transformative pathways that specifically address the challenges posed by the major drivers, also highlighting the types of policy and investment portfolios required to transform food systems for food security, improved nutrition, and affordable healthy diets for all. The report observes that, while the pandemic has caused major setbacks, there is much to be learned from the vulnerabilities and inequalities it has laid bare. If taken to heart, these new insights and wisdom can help get the world back on track towards the goal of ending hunger, food insecurity, and malnutrition in all its forms.
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    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.