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Book (stand-alone)Assessment of IUU activities on Lake Victoria 2012
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No results found.Fishing all over the world is a major source of food for humanity and a provider of employment and economic benefits to those engaged in the activity. However, with increased knowledge and the dynamic development of fisheries, it should be known that world living aquatic resources, although renewable, are not infinite and need proper management, if their continued contribution to the nutritional, economic and social well-being of the growing world’s population is to be sustained. Lake Victoria i s Africa’s largest and most important inland water body with a total water surface area of 68,800km2. Lake Victoria contributes significantly through its fishery and generation of electricity to the economic benefits of not only the riparian states, Kenya, Tanzania and Uganda, but also to the neighboring countries and the world at large. Lake Victoria is arguably the most important single source of freshwater fish on the African continent, contributing significantly to national and regional econ omies and livelihoods of the regions inhabitants. Although not often associated with inland fisheries, Illegal, Unreported and Unregulated (IUU) fishing and the trade of illegal fish has threatened the biological, social, financial and cultural integrity of the lakes resources and those that depend on them. Given that Lake Victoria’s living resources are shared amongst the three riparian states, a regional fisheries body, the Lake Victoria Fisheries Organization (LVFO) was formed in 1994 though the technical assistance of the FAO to manage the fisheries resources in Lake Victoria as a single ecological entity. Within the LVFO mandate, the identified areas of IUU fishing are considered in the form of: Illegal or misuse of fishing gears; illegal fishing, fish landing, processing and trading; unregulated fishing number of boats, fishers and gears (capacity); unregulated, unreported or undocumented domestic and regional fish trade; fishing and landing undersize fish in undesignated landing sites; and fishing during closed seasons or in the closed breeding areas or critical habitats. The decline of Nile perch stocks suggest that fisheries management and compliance structures within the three riparian states and at LVFO at the moment are at various levels of disarray, hence allowing IUU fishing to continue thriving unabated. Since the introduction of Nile perch into Lake Victoria in the 1950’s it has been the focus of an intensifying commercial fishery. In 1980, a total of 4 439 to ns of Nile perch were harvested, a decade later over 338 115 tons of Nile perch were landed annually. From 2000 to 2010, and average of 253 404 tons of Nile perch are caught. Despite relatively consistent landings reported by the LVFO, total biomass of Nile perch decreased from 1.4 million tons (92% of total biomass in Lake Victoria) in 1999 to it lowest recorded estimate of 298 394 tons in 2008 (14.9% of total biomass in Lake Victoria). Currently, as of 2010, the Nile perch biomass was estimate d at 18% of total biomass in Lake Victoria, which equates to 367 800 tons. Although a slight increase in biomass between 2008 and 2010 was observed, Nile perch biological indicators suggest that the fish is in a critical survival state. The average size of Nile perch has decreased from 51.7 cm TL to 26.6 cm TL, according to hydro acoustic surveys suggesting that a significant portion of total Nile perch biomass is less than 50 cm TL (legal size for export). It was reported by the LVFO stock asse ssment team that in 2006 and 2008, less than 2% of the Nile perch biomass was in fact greater than 50 cm TL. The size at first maturity of male and female Nile perch is also decreasing, this common amongst fish populations that are stressed (or overexploited). Despite the biological indicators, which suggest legal size Nile perch are less than 2% of total Nile perch biomass, the average number of fishermen increased by 33% between 2000 and 2008. During the same period, Frame survey and MCS compl iance missions noted a marked increase in the number of illegal gears being deployed to target undersize Nile perch. The number of vessels increased by 37% and the use of outboard engines increased by approximately 50%. It has been reported that motorized boats are more efficient, catching about 25 kg of fish per day, compared to 10 kg caught by non-motorized vessels. The increase in use of illegal gears, motorized vessels and fishermen suggests that fishing for Nile perch is still profitable. P reviously driven by lucrative export prices for Nile perch, fishers now target undersize illegal Nile perch for the lucrative domestic and regional trade, which is estimated to exceed the export trade by volume and value. This shift in fishing for undersize Nile perch will effect government revenues earned from the export fishery. The Nile perch fishery over the last decade contributed 0.6% less to the Tanzanian GDP, similarly, a decrease in export trade of Nile perch from Uganda of 14% occurred between 2007 and 2008, resulting in a 0.1% decrease in GDP contribution. By not controlling fishing effort targeting illegal, undersized and immature Nile perch, economic and social hardships will worsen. Current fisheries management both regionally through the LVFO, and nationally amongst the riparian states is inadequate, with respect to Monitoring, Control and Surveillance (MCS). MCS is a collection of activities and tools intended to support fisheries management in fighting IUU fishing, and forms the framework on which accurate, informative and dynamic fisheries management decisions can be made. MCS is critical at all levels of fisheries management. Within the Lake Victoria region, co-management has been implemented through the establishment of Beach Management Units (BMU’s). A BMU is a community-based organization, which is legally accepted as a representative of a fishing community and is mandated on a voluntary basis to engage in MCS initiatives. Lake Victoria has 1 087 registe red BMU’s according to the harmonized BMU guidelines, agreed upon amongst the member states and the LFVO. Although the inclusion of community based management and MCS is critical in contributing to effective management of Lake Victoria’s fisheries resources, many challenges exist, including amongst others; geographical isolation of fishing communities, social issues (families of BMU members may partake in illicit activities), political interference (revenue collections, or election voting), corr uption, conflict of interests (BMU members are often fishmongers and fish traders) and lack of representation in higher management committees. Although advances in MCS technology have revolutionized fisheries management amongst many ESA-IO countries, the sharing of regional resources and capacity is fragmented and not effectively harnessed by the LVFO. Database management systems are not working effectively, data collecting, analyzing and dissemination are unreliable and time inefficient, respec tively and appropriate MCS tools for example net gauges are not available. The RWG-MCS reported that between 2004 and the end of 2008, a total of 4 605 suspects were apprehended, 12 126 beach seines, 9 550 small seine nets, 27 703 monofilament nets, 248 843 kilograms of immature Nile perch (249 tons) and 254 589 illegal gillnets were confiscated. These data are unreliable; furthermore they were not quantified in terms of definition of the item (how long were the nets that were confiscated 80 met er, or one kilometer, this has a profound effect on CPUE), of financial loss to fishers and traders versus the opportunity costs of MCS. The valve of court fines are insignificant especially if one considers the amount of uncontrolled fishing effort, uncontrolled illegal gears used in Lake Victoria, and the increasing value in the trade of immature fish on domestic markets. Also, there is no indication as to whether the court penalties and fines imposed on the same offences in the three partner states have any reference to the same severity across the region, or are recycled back into MCS initiatives. It is therefore difficult to determine whether the RWG-MCS interventions from 2004 to the end of 2008 were beneficial, as little to no comparative data exists. The LVFO depends highly on donor funds to support MCS and management initiatives, including training, capacity building and technical expertise. When donor funds are not available, regional MCS stagnates, which is a major concern. Operation Save the Nile perch is one such example. The EAC Council of Ministers in 2009 launched the ‘Operation Save the Nile Perch’ (OSNP), which required each of the three member states to contribute US$ 600 000. The goal of the initiative was to target illegal fishing and to curb the trade in undersize Nile perch currently threatening the economic integrity of Lake Victoria. The target of OSNP, as ratified by the Council of Ministers was to have fisheries illegalities in the lake, based on th e 2008 frame survey data as bench mark, reduced by 50% in June and 100% by December 2009. Currently as of 2011, Kenya has paid the required funds, with Tanzania only contributing 31% and Uganda zero resulting in less than half of the required funds paid in by from the member states. This undermines the legitimacy of ‘Operation Save the Nile Perch’ and political will and MCS operational capacity. The aim of this report was to assess the state of IUU in Lake Victoria, and to support the SMARTFISH programme in assisting the LVFO and established MCS committees to implement joint regional MCS trainings, by conducting a short cost benefit analysis of enhancing existing regional MCS initiatives and by evaluating past and present regional action plans to deter IUU fishing on Lake Victoria. An action plan was developed through a participatory workshop between the LVFO, national states and the MCS-RWG, held in Jinja, Uganda from the 5th to the 7th of October 2011. -
Book (stand-alone)Inland small-pelagic fisheries utilization options, marketing and opportunities for support 2012
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No results found.The fisheries sector contributes greatly to the economies of the eastern, central and southern regions of Africa (ECSA) in terms of income, employment and export revenue. Until recently, only large-sized fish were exploited for human consumption but small-sized pelagic fish were used for animal feed production. However, in the last decade, concerted efforts have been made in various African countries to reverse the trend. For example in 2005, an FAO led study assessed post-harvest losses in one of the abundant small-sized pelagic fisheries (Rastrineobola argentea), in the East Africa states of Kenya, Uganda and Tanzania. In 2011, Uganda through the Department of Fisheries Resources (DFR), requested FAO under the Technical Corporation Programme (TCP) to address the question of high post-harvest losses in the fishery and improvement of upstream handling against a backdrop of declining per capita consumption trends. Under this programme, several products were developed to increase Rastrin eobola argentea, locally called Mukene, for human consumption. The SMARTFISH Programme, with funding from the European Union (EU) built on previous efforts by initiation of the present study that has been designed to look at increased utilization options to enhance cross-border trade in small pelagics. As a test case, products from Brycinus nurse (Ragoge) and Neobola bredoi (Musiri) commonly found in Lake Albert of Uganda were developed together with potential Ugandan processors and the economic ally viable products were marketed in neighbouring Kenya and Rwanda to gauge their marketability. Using a structured questionnaire with some input from the Trade Event Specialist, some potential regional traders tasked to evaluate their prospects. Prior to product development, information was gathered on all aspects of the Musiri and Ragoge fishery, including the sanitary status of fishing vessels, time of capture, daily catches, drying surfaces, storage facilities, packaging, wholesale operatio ns as well as markets and transportation. The sand-free sundried products, powdered and fried products were promoted for regional markets. As a complementary study, the nutrient content of products from both fish species was determined for purposes of backstopping the three up-graded processors who were at different levels of development. The regional market opportunities surveyed indicated that there was an insatiable demand for all products made from small-sized pelagics ranging from sun-dried to powdered. The large quantities demanded by the regional markets could not be met by processors using traditional processing methods and operating at a small-scale. It was also evident that product quality was a determinant factor in product pricing. The cost of sand-free products was one and a half times more than adulterated products which underscore the influence of consumers in the market place. There were other external drivers that are likely to enhance regional trade of the identified value-added products from Uganda. They included population increases, regional geo-economic and political blocks, carbohydrate-based diets, nutritional properties of fish and civil strife or wars. During the implementation of the present study, there were two major challenges namely; seasonality of the two species under scrutiny and the competence of local processors to be up-graded to standards required by the regional as well as international markets. Both factors slowed down the implementatio n process because unplanned exposure visits and training had to be conducted to improve the competence of potential processors under the up-grading SMARTFISH scheme. In conclusion, there was an insatiable demand in the region for all products made from small-sized pelagic fishes from Uganda and trade in such products can be enhanced in the region with concerted effort from all key actors along the value-chain, improved upstream handling, broadened utilization base, consumption campaigns and enfo rcement of quality and safety standards. However, implementation of some intervention measures cited would require harmonized policies across national borders, substantial investment in the sector, sensitization of key actors with regard to market requirements and goodwill among policy enforcers at border crossings. -
ProjectExtension Approaches to Coastal Fisherfolk Development in Bangladesh; Guidelines for Trainers and Field Level Fishery Extension Workers - BOBP/MAG/8 1992
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No results found.This manual is intended to facilitate a learning process which will arm field level fishery extension officers with knowledge and skills to assist fisherfolk communities in their efforts to collectively address their needs and problems. It is designed to be used in two ways: Firstly, as a trainer’s manual: the document begins with participatory rapid rural analysis to understand the status and dynamics of communities. moves on to needs analysis and identification. problem analysis. generating solution option, planning activities, group formation and management, savings and credit management and finally project planning, implementation and management. It also includes training approaches and tips and provides examples of work that results from putting the training into praxis. Secondly, for motivated and commited field workers, the manual could provide a self-instruction aid which helps them to think through and put various approaches into practise. The approach is aimed at addressi ng the needs of the whole fishing community either directly through action or indirectly through facilitating action by other agencies and workers.
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