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Review on the current status of fisheries/aquaculture and policies of Cambodia relevant to RFLP

Regional Fisheries Livelihoods Programme for South and Southeast Asia. (GCP/RAS/237/SPA)








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    Book (stand-alone)
    Sustainable management of Miombo woodlands
    Food security, nutrition and wood energy
    2018
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    The Miombo woodland is a vast African dryland forest ecosystem covering close to 2.7 million km2 across southern Africa (Angola, Democratic Republic of the Congo, Malawi, Mozambique, Tanzania, Zambia and Zimbabwe). The woodlands are characterized by the dominance of Brachystegia species, either alone or in association with Julbernardia and Isoberlinia species. It is estimated that the woodlands – through their numerous goods and services which include various non-wood forest products (NWFPs) (e.g. insects, mushrooms, fruits, tubers, medicine, fodder, honey, seeds) and woodfuels, which, for simplicity, will be referred to as non-timber forest products, or NTFPs, throughout the publication – sustain the livelihoods of more than 100 million rural poor and 50 million urban people. The charcoal sector alone employs vast numbers of rural people and offers additional income to many poor rural families. Communities moreover rely directly on the woodlands for food and nutrition. NWFPs add vital micro- and macronutrients to local diets and contribute to diversified food systems, while woodfuel is essential for cooking and sterilizing, thus ensuring proper nutrient absorption and providing clean water for drinking. Forests and trees, if managed sustainably, are an important source of resilience for rural people in the Miombo woodlands, supporting households to absorb and recover from climatic or economic calamities and contributing to resolving the underlying causes of food insecurity, undernutrition and poverty by providing nutritious edible products and woodfuel for cooking in addition to conserving biodiversity and water resources, buffering extreme weather conditions and preventing land degradation and desertification. Generally speaking, it is now accepted that forests managed for both timber and NTFPs retain more biodiversity and resilience than forests managed solely for one aspect, e.g. timber and exotic timber plantations. However, a growing population in high need of agricultural land and unsustainable use and overharvesting of natural resources in parts of the Miombo woodlands, combined with climate change impacts (e.g. drought, fires), leave insufficient time for many trees and associated species to regenerate naturally, posing a serious threat to the products and services of the woodlands, and to the livelihoods depending on them. Compounding the problem and hindering development of the Miombo ecosystem, are: i) lack of an enabling policy environment; ii) unsustainable management; iii) limited willingness and ability to pay for and access to energy-efficiency technologies; iv) inadequate awareness and information, including technical capacity; v) high poverty levels; and vi) limited access to microcredit facilities. With the Committee on World Food Security’s endorsement of the recommendations presented in the High Level Panel of Experts Report on Sustainable Forestry for Food Security and Nutrition in late 2017 – which include promoting multifunctional landscapes, integrated food-forestry systems, and research on associated linkages, among other things – forests and trees are expected to play a greater role in future land-use decisions and related policies. This paper provides an overview of these linkages in the context of the Miombo woodlands, in the hope that future land use, policy decisions and financial investments are shaped to support the contributions of forests and trees to the health and livelihoods of communities in the ecoregion. The following key messages were formulated: • Forests and trees, if managed sustainably, are an important source of resilience for rural people in the Miombo woodlands, supporting households to absorb and recover from climatic or economic calamities and contributing to resolving the underlying causes of food insecurity, undernutrition and poverty by providing nutritious edible products and woodfuel for cooking in addition to conserving biodiversity and water resources, buffering extreme weather conditions and preventing land degradation and desertification. • Current data bases referring to the value of the Miombo must be analysed and used as evidence to improve policy-making. • Miombo woodlands may be dominant (spatially), but they have not been addressed as a single unit but as part of the region’s forests. They form part of the overall forestry strategies and no specific mention in the conventions does not suggest that their importance is underplayed. • The management of Miombo will require some changes in management structures, especially in providing benefits emerging from trade in forest products to local managers. • Local forest managers should play a greater role in allocating resources for feedstock for charcoal production.
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    Book (stand-alone)
    Assessment of IUU activities on Lake Victoria 2012
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    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.
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    Brochure, flyer, fact-sheet
    Cambodia country fact sheet on food and agriculture policy trends
    Food and Agriculture Policy Decision Analysis (FAPDA) - FAO
    2014
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    Cambodia is a low income country in the Southeast Asia region. Agriculture contributed 37 percent to the GDP and employed about 67 percent of the workforce in 2012. Most Cambodian farmers are smallholders with less than two hectares per household. The country’s agricultural resources consist primarily of 3.7 million hectares of cultivated land, of which 75 percent is devoted to rice, primary commodity and source of income for the majority of farmers and 25 percent to other food and industrial cr ops, primarily rubber. Freshwater and marine fisheries and aquatic resources provide employment to over three million people. Fish is also a major source of protein in the domestic diet. On average, agricultural GDP growth in Cambodia has lagged behind the industrial and service sectors but maintained a sustained annual rate between 4 and 5 percent during the last decade. In 2013, agricultural production increased by 4.3 percent with a paddy harvest at record levels (about 9.3 million tonnes). R ice production has registered significant productivity improvements in terms of both labour and land. Paddy is also a key commodity for exports: in 2013, Cambodia exported a record level of 1.2 million tonnes of rice, accounting for more than 3 percent of the total worldwide rice exports. The country has experienced rapid economic growth since 1993, with an annual GDP growth of 7.3 percent in 2012. The poverty rate has decreased by more than half since 2007, but one-fifth of the population is st ill living below the poverty line and income inequality has increased. Despite good success in reducing undernourishment over the last two decades (proportion of undernourished in total population declined from 39 percent in 1990/92 to 15 percent in 2011/13), the country seems unlikely to meet the 4th Millennium Development Goal of reducing child mortality rate by two thirds by 2015.

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