ISSN 0041-6436

Food and Agriculture An international journal Vol. 64 Organization of and of the United Nations industries 2013/2 241

Forests for food security and nutrition Committee on World Food Security Food security exists when all people, at all times, have physical, social and economic access to sufficient safe and nutritious food that meets their dietary needs and food preferences for an active and healthy life.

The Committee on World Food Security (CFS) was set up in 1974 as an intergovernmental body to serve as a forum for the review and follow-up of food-security policies. Its vision is to be the most inclusive international and intergovernmental platform for all stakeholders to work together in a coordinated way to ensure food security and nutrition for all.

The CFS holds annual sessions in which members, participants and observers discuss and make recommendations on important issues related to food security and nutrition at the global, regional and national levels. It also convenes multistakeholder consultations to arrive at guidelines and agendas for action on, for example, land tenure, responsible agricultural investment and engagement in protracted crisis contexts. The CFS is setting up mechanisms to enable stakeholders to monitor the implementation of its recommendations and guidelines.

The CFS reports annually to the United Nations Economic and Social Council. For more information visit www.fao.org/cfs/en ISSN 0041-6436

Food and Agriculture An international journal Vol. 64 Organization of forestry and of the United Nations forest industries 2013/2 241

Editor: A. Sarre Editorial Advisory Board: P. Csoka, L. Flejzor, T. Hofer, F. Kafeero, W. Kollert, Contents E. Rametsteiner, S. Rose, A. Sarre, J. Tissari, P. van Lierop, P. Vantomme, M.L. Wilkie Editorial 2 Emeritus Advisers: J. Ball, I.J. Bourke, C. Palmberg-Lerche, L. Russo Regional Advisers: F. Bojang, P. Durst, M. Saket C. Padoch and T. Sunderland Managing landscapes for greater food security and Unasylva is published in English, French improved livelihoods 3 and Spanish. Free subscriptions can be obtained by sending an e-mail to [email protected]. J.C. Mohamed-Katerere and M. Smith Subscription requests from institutions (e.g. libraries, companies, organizations, universities) The role of ecosystems in food security 14 rather than individuals are preferred to make the journal accessible to more readers. R. Jamnadass, F. Place, E. Torquebiau, E. Malézieux, M. Iiyama, All issues of Unasylva are available online free G.W. Sileshi, K. Kehlenbeck, E. Masters, S. McMullin and I.K. Dawson of charge at www.fao.org/forestry/unasylva. Comments and queries are welcome: for food and nutritional security 23 [email protected]. Reproduction and dissemination of material A. Bertrand, G.A. Agbahungba and S. Fandohan in this publication for educational or other Urbanization and forest foods in Benin 30 non-commercial purposes are authorized without prior written permission from the copyright L. Stloukal, C. Holding, S. Kaaria, F. Guarascio and holders provided the source is fully acknowledged. Reproduction of material in this publication for N. Gunewardena resale or other commercial purposes is prohibited , food security and gender 37 without written permission of the Chief, Publishing Policy and Support Branch, Office of Knowledge P. Dewees Exchange, Research and Extension, FAO. Articles express the views of their authors, Forests, and resilient households 46 not necessarily those of FAO. The designations employed and the presentation B. Vinceti, A. Ickowitz, B. Powell, K. Kehlenbeck, C. Termote, of material in this information product do not B. Cogill and D. Hunter imply the expression of any opinion whatsoever on the part of FAO concerning the legal or The contributions of forest foods to sustainable diets 54 development status of any country, territory, city or area or of its authorities, or concerning the Summary of the International Conference on Forests for delimitation of its frontiers or boundaries. The Food Security and Nutrition mention of specific companies or products of manufacturers, whether or not these have been Forests and trees outside forests are essential for global food patented, does not imply that these have been security and nutrition 65 endorsed or recommended by FAO in preference to others of a similar that are not mentioned. FAO Forestry 72 To order the FAO publications reviewed in Unasylva, contact the Sales and Marketing Group, World of Forestry 75 Office of Knowledge Exchange, Research and Extension, FAO, Viale delle Terme di Caracalla, Books 77 00153 Rome, Italy. Tel.: (+39) 06 57051; Fax: (+39) 06 5705 3360; Telex: 625852/625853/610181 FAO I; E-mail: [email protected]

Cover: Two farmers stand in their agroforestry plot in Kenya, the woman holding a papaya fruit. Forests and trees outside forests are increasingly recognized as essential for global food security. This image by Alana Holmberg won the UN-REDD Programme photo contest, “REDD+ for food security” editorial

Forests for food security and nutrition

nsuring food security and nutrition has always been at opportunity for entrepreneurs and rural producers, but there is an the heart of FAO’s work. The Organization’s constitution urgent need for a new legal and administrative framework that asserts that FAO’s member nations are determined, among promotes sustainable and the domestication Eother things, to ensure “humanity’s freedom from hunger”. FAO’s of forest animals for meat production. Director-General, José Graziano da Silva, wrote recently that L. Stloukal and co-authors examine the role of gender in the “ending extreme poverty and hunger is not merely desirable; it food security (or insecurity) of rural people. The disadvantages is the indispensable foundation of a new global society that is faced by women in developing countries in their access to forests both open and fair”. have huge implications for the food security. The authors argue Food security requires healthy, diverse ecosystems, and forests that empowering women in the forest sector can create significant and trees outside forests therefore have an important role to play. development opportunities and improve food security and nutri- To explore this role, FAO and its partners brought together, in tion among rural people. May 2013, more than 400 experts from governments, civil- In his article, P. Dewees looks at how forests and trees can help society organizations, indigenous and other local communities, households withstand tough times – that is, to be resilient in the donors and international organizations from over 100 countries face of economic and environmental hardship. He sets out some for the first global conference to specifically address the role of policy responses that would encourage the integration of forests forests and trees outside forests in food security and nutrition – and trees in agricultural systems to increase this resilience, and the International Conference on Forests for Food Security and he advocates interventions at a landscape scale. Nutrition. This edition of Unasylva presents articles arising B. Vinceti and her co-authors discuss the concept of “sustainable from that conference. diets”, which are diets that conserve biodiversity, are culturally Several articles stress the need to approach food security inter- acceptable, provide adequate nutrition and optimize the use of sectorally and at the landscape scale. T. Padoch and C. Sunderland, natural and human resources. The authors find that forests and trees for example, say that more research is needed into ways of better make substantial contributions to the nutritional quality of the diets integrating forests, trees and agricultural production in land- of many rural people, and they, too, advocate the management of scapes. While diverse, integrated landscapes (“land-sharing”) heterogeneous landscapes to ensure that food-production systems are the norm in smallholder farming systems, they are being are nutrition-sensitive and minimize their ecological footprint. replaced by methods that segregate (and simplify) landscapes The final article in this edition comprises the summary statement into “conservation” and “production”, called “land-sparing”. The issued by organizers at the end of the International Conference authors argue that replacing land-sharing with land-sparing risks on Forests for Food Security and Nutrition; it includes a number the loss of valuable traditional knowledge and could also reduce of recommendations arising from the papers presented at the the resilience of smallholders to change. conference and the ensuing discussions. According to J. Mohamed-Katerere and M. Smith, ecosystems, There is no doubt that forests and trees are essential components including forests, provide many goods and services that underpin of most sustainable food-production systems, as both producers of food production. The authors advocate an “ecosystem-aware” foods and providers of ecosystem services. Achieving an optimal approach to food-security policy-making that aims not only to mix of forests and trees in landscapes, however, requires more alleviate hunger in the short term but also to ensure the capacity research, development and extension, and much more interaction of ecosystems to support food production in the face of shocks between the various sectors – such as forestry, agriculture, water, and stresses. Diversity – of ecosystems, biota and livelihoods – is energy and land-use planning. By combining forces, the sectors one of the keys here. can make best use of existing knowledge and experience, includ- R. Jamnadass and his co-authors explore the role of agroforestry – ing traditional knowledge, with the ultimate goal of building an the integration of trees with annual crop cultivation, livestock open and fair global society and thereby ensuring food security production and other farm activities – in food security and nutri- and adequate nutrition for all. tion. More than 1.2 billion people practise agroforestry worldwide, but its role in supporting the food and nutritional security of the rural poor is still poorly documented. More research is needed to Reader survey better target interventions, and more attention is needed on the We want your views on Unasylva. Please help us increase domestication of forest food species to harness their huge potential. the journal’s impact on forest policy and practice by An article by A. Bertrand and co-authors looks at the increasing participating in a short Web-based survey. demand for forest foods, especially wild meat, in urban centres www.fao.org/forestry/unasylva in Benin. This increasing demand, say the authors, represents an 3 V. GUTIERREZV. VELEZ, IMAGE COURTESY GOOGLE EARTH Managing landscapes for greater food security and improved livelihoods

C. Padoch and T. Sunderland

The research and development he “sustainable intensification” of The interpretation of sustainable community should focus more agriculture is being advocated as intensification appears to differ consid- effort on reintegrating food the optimum means to advance erably depending on the programme, but production and conservation in Tand reconcile two pressing global issues: invariably it involves the goal of producing smallholder-managed landscapes. the need to protect ever-decreasing more food without clearing new areas of forest lands, and the imperative to feed natural vegetation or further degrading the the growing human population. The environment. At first glance this goal seems sustainable-intensification paradigm laudable and compelling, yet a number has come to dominate the discourse of of important issues arise concerning the many institutions devoted to economic assumptions and meaning of sustainable and agricultural development, including intensification (Rudelet al., 2009; Collins the research centres of the CGIAR1 and Chandrasekaran, 2012). In this article (Pretty, 2009).

Above: A diverse smallholder landscape 1 CGIAR, of which CIFOR is a member, is a in the Amazon, Brazil. Approaches that global partnership aiming to unite organizations maintain or increase the diversity of land engaged in research for a food-secure future. uses and land users in landscapes offer an Christine Padoch and Terry Sunderland The name CGIAR comes from the acronym alternative to “sustainable intensification” are at the Center for International Forestry for the Consultative Group on International in achieving food security, but they need Research (CIFOR) in Bogor, Indonesia. Agricultural Research. more attention from researchers

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A farmer inspects the foliage of we ask why the intensification of agricul- (Evenson and Gollin, 2003). The use of a cassava plant in an intensive agricultural approach in Niamy, Chad. tural production – or, for that matter, any these technologies have greatly boosted In many parts of the world, large single solution – is being championed as food supplies in many – but not all – increases in production have been the only pathway to meeting sustainable regions of the world, but it has also led to a achieved per unit area using a suite of modern technologies and tools, production goals for agriculture. And we broad range of environmental ills, such as but there are doubts about a sole explore an alternative paradigm that could reduced biodiversity and increased carbon focus on this approach in efforts to lead to improved outcomes. and nitrogen pollution (Godfray et al., achieve global food security 2010; Collins and Chandrasekaran, 2012). QUESTIONS ON SUSTAINABLE Some important questions about sustain- ecosystems, including forests, from further INTENSIFICATION able intensification remain to be answered. encroachment and conversion (Pinstrup- The intensification of production is hardly Will the same technologies and approaches Andersen, 2013). On the contrary, more a new idea; it has been an important – employed in the previous intensification production per unit area sometimes appears indeed dominant – trend in agricultural era continue to be used in “new” efforts to lead to more areas being cleared for development for many decades (Tilman to achieve sustainable intensification? Is production, due to lower labour inputs and et al., 2002). Large increases in grain pro- it possible to deploy them in more envi- greater yields and the associated increase duction per unit area have been achieved ronmentally benign and effective ways? in profitability (Angelsen and Kaimowitz, using a suite of technologies and tools, Doubts about an overemphasis on sustain- 2001; Barretto et al., 2013; Chappell et al., such as high-yielding planting materials, able intensification are fuelled by empirical 2009; Perfecto and Vandermeer, 2010). increased irrigation, and large quantities evidence that does not always support the There are also questions about those of synthetic fertilizers and pesticides – the seemingly logical notion that increased regions in which intensification technolo- very essence of the Green Revolution production per unit area will spare natural gies have until now led to few benefits.

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Solutions to the apparently complex and produced, as well as reducing waste, are LAND-SPARING VERSUS multiple reasons why the Green Revolution equally or more important (Tscharntke LAND-SHARING bypassed some of the poorest regions of, et al., 2012). We also need to know whether The way in which most proponents of for example, sub-Saharan Africa continue the estimated 842 million people who suf- sustainable intensification have presented to confound those who have attempted to fered from chronic hunger in 2011–2013 their plans conforms to what has been raise yields and benefits for local producers (FAO, IFAD and WFP, 2013) did so mainly labelled a “land-sparing” approach to in such areas. Producers continue to be because of inadequate quantities of food reconciling production and conservation challenged by the high costs and unreliable or because they could not access the priorities, in which a greater yield is availability of the inputs required and the food that was actually produced (Rocha, achieved on a smaller area of land, thus limited capacity of government extension 2007). If the problem is largely one of “sparing” the conversion of natural systems. agencies (Evensen and Gollin, 2003). access to, rather than the total supply of, There are alternatives, however (e.g. Many of the questions being asked food, how will sustainable intensification, Phalan et al., 2007), such as land-sharing about sustainable intensification, however, and a focus on production, resolve that? approaches in which environmental and address the fundamental assumption that it Moreover, the quality of food may be just production functions are more closely is the production of more food, especially as important as its quantity: in the view of more calorie-rich grains, that should be our many nutritionists and others, the provision Behind these huts in Song Thanh, Viet Nam, major focus in achieving global food secu- of more nutritious food rather than simply the hills show the complex mosaic landscape rity (Sayer and Cassman, 2013). Arguably, more calories is the most pressing global typically created by in a land-sharing approach, with fields under the objectives of obtaining more equitable challenge (Welch and Graham, 1999; active annual cropping interspersed with access and distribution of what is already Brinkman et al., 2010). areas in various stages of regrowth and with older forest on the hilltops © L. PREECE

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integrated at the landscape scale. Using and conservation. In addition to arguing LANDSCAPE APPROACHES both ecological theory and empirical that integrating production and conserva- Landscape-scale approaches that embrace data, a number of researchers have sug- tion can improve the outcomes of both, a land-sharing philosophy have recently gested that land-sharing may generate Perfecto and Vandermeer (2010) pointed gained traction in debates as an alternative better food-production and conservation out that land-sharing often allows for a to the more conventionally imagined outcomes than approaches that aim to greater diversity of both land uses and sustainable-intensification pathway (Sayer isolate and intensify both production land users. et al., 2013). Producing food in diverse, multifunctional landscapes challenges dominant agricultural development paradigms, but it also presents issues and difficulties. For example, many types of integrated landscape approach have not been studied by scientists, and the existing research and policy framework may be insufficiently integrated to improve either agricultural production or environmental protection in such diverse landscapes (Tilman et al., 2011). The lack of rigorous research is con- cerning and needs to be addressed. A central problem for advancing landscape approaches may be that they combine agricultural production and environmental conservation in ways that are unfamiliar to specialized scientists, who have made many of the recent advances in agronomy and conservation; the unfamiliar is rejected or, more likely, ignored (Sunderland, Ehringhaus and Campbell, 2008). But the farming of diverse landscapes has long been the dominant smallholder paradigm. There is much practical experience to build on, therefore, in both management practice and governance.

Addressing access and diversity Even if landscape approaches are less of a sure thing for directly increasing the global supply of familiar commodity crops, they have great potential for resolving other issues that are central to the food security of some of the world’s most vulnerable people. Landscape approaches are already known by many of the people who tend to

A farmer collects leaves of the kibembeni to make an organic insecticide in the village of Msewe, the United Republic of Tanzania. Diverse, locally adapted production and resource management systems tend to increase

FAO/G. BIZZARRI the resilience of rural households

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A mosaic of more and less traditional land be the targets of development programmes, panoply of environmental, demographic, uses in a landscape in northern Thailand. Realizing the promise of integrated landscape especially those who have benefited little social, political and economic changes approaches requires the willingness and from previous initiatives. They offer prom- that is sweeping across much of the less- ability of researchers to work across sectoral, ise for solving some food-related problems developed world. Diverse, locally adapted academic and ideological boundaries that have proved to be more intractable production and resource management than the basic task of producing more systems tend to increase the resilience community will require a reorientation of calories – such as improving access to of rural households in the face of such research ideas, ideologies and priorities. food and nutrition through the provision of changes (Scherr and McNeely, 2008). While the challenge is undoubtedly com- a diversity of products, and thus improving plex, making use of existing experience diets (Scherr and McNeely, 2008). Reorienting research will help. It is estimated that 40 percent of Realizing the promise of integrated land- all food in the less-developed world origi- More effective in marginal lands scape approaches, however, requires the nates from smallholder systems, and many Landscape approaches, especially those willingness and ability of researchers to of these depend essentially on diverse land- that are developed locally, are often work across difficult sectoral, academic scapes (Godfray et al., 2010). Smallholder more suitable for lands where previous and ideological boundaries. Working farmers worldwide and throughout history agricultural intensification has been to improve existing locally developed have managed landscapes for food and unsuccessful, for example on sloping lands and locally adapted production systems other livelihood needs. Forests, woodlots, and in other areas that are marginal for to increase incomes and improve nutri- parklands, swidden-fallows and other tree- conventional approaches. The diverse tion rather than “reinventing” landscape dominated areas are integral parts of many production activities that such systems approaches to fit the constructs and precon- smallholder landscapes and household comprise are often well adapted to the ceptions of the research and development economies (Agrawal et al., 2013).

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Smallholder-managed landscapes are, of to increased levels of connectivity and SHIFTING CULTIVATION course, variable in spatial extent, complex- mobility within forest–field landscapes In most discussions of successful land- ity and management, among other things. (Pinedo-Vasquez et al., 2001). Farmers, scape approaches, however, there is a One of the few generalizations that can be who simultaneously are also , conspicuous omission. Shifting cultivation, made about them is that they tend to be fishers and hunters, transform and manage also known as swidden or slash-and-burn diverse, complex and dynamic, which is these landscapes, often making them more agriculture, is an integral part of many, the main source of their strengths and also ecologically diverse and thus providing if not most, tropical forest landscapes of their weaknesses (van Vliet et al., 2012). favourable habitats for fish (Goulding, crucial for biodiversity conservation and Smith and Mahar, 1995), wildlife (Bodmer watershed protection, including those in Amazonian floodplain farmers and Pezo Lozano, 2001), trees (Pinedo- the Amazon Basin, Borneo and Central On the Amazonian floodplains, small- Vasquez et al., 2002) and fruit trees Africa (Ickowitz, 2006; Padoch et al. 2007; holder farmers have created heterogeneous, (Hiraoka, 1992). Mertz et al., 2009; Schmidt-Vogt et al., mosaic landscapes characterized by high The diverse patches of smallholder 2009). But this manner of managing forests levels of ecosystem and species diversity mosaics provide ecosystem services in and landscapes for food and other human at different spatial scales (Padoch and ways that are poorly understood. Such needs has been criticized, condemned and Pinedo-Vasquez, 2000; Sears and Pinedo- services may include, for example, micro- in some cases criminalized (Fox et al., Vasquez, 2004). To manage the natural climatic effects that make agricultural 2009; Mertz et al., 2009). variation of complex floodplain environ- production possible or more profitable in Few of the features of shifting cultivation ments, farmers in these agro-ecological times when extremes in temperature or seem to fit into any conventional category landscapes integrate strategies of pro- humidity would otherwise prevent farm of sustainable production or landscape duction, use and conservation to serve production. Among the many ecosystem management. The cutting of trees, the multiple objectives, and they adapt their services that small forest stands supply to burning of fields, the comparatively low management to seasonal or even diurnal agricultural fields and the families who production of staple crops and the appar- (in the estuary) fluctuations in water level. manage and share the space are a reli- ent abandonment of fields after a year Their plots are not randomly arranged, and able supply of water, shade and forage for or two of cropping – all highly visible nor are they “primitive” or “unproductive” livestock; refuges, food and breeding sites features of many such systems – are largely versions of modern or industrial-scale for fish; and a variety of valuable forest regarded worldwide as primitive, waste- farm fields. Smallholder strategies of land products to support farmer families in ful and destructive. Efforts to eliminate use and resource management are often times of climatic stress. such practices have been central to many based on the concurrence of intensive The effects of diverse patches on seed national and international conservation and extensive activities that simultane- availability for the restoration of forest and development programmes (Cramb ously minimize risk and maximize species and hence of soil fertility may et al., 2009; Fox et al., 2009). labour opportunities while allowing for often also be among the crucial but hidden But beyond the smoke and the prejudices adaptation to opportunities and problems benefits of diverse, smallholder-developed inherent in a term like “slash-and-burn”, as they emerge. and -managed landscape mosaics. it is clear that many shifting cultivation The adaptive management practised by Typically, several of the patches in a given systems could be valuable components Amazonian floodplain farmers results in human-modified landscape on the Amazon of a landscape approach to agricultural multifunctional farming systems in which floodplain will comprise highly diverse production in forested regions. Including the production of a diversity of goods and agroforests that include timber trees and them would require a willingness to reject services is integrated and the particulars other economically valuable trees and the lure of simplicity that alternative of the system are attuned to biophysical, herbaceous species. There will also be solutions offer. social and economic conditions that vary, multistoried and fruit-rich homegardens Shifting cultivation is complex on several often dramatically, over time and space. in and around human settlements, levels (van Noordwijk et al., 2008; Padoch This multipurpose management is one of which are particularly valuable for food et al., 2007). The biodiversity of some the characteristics that best distinguishes security and nutrition. Institutions and of these systems is almost legendary. smallholder systems from the simplified non-governmental organizations devoted When the shifting cultivation systems of practices of large-scale agriculture and to landscape approaches to agricultural the Hanunoo people of Mindoro island industrial farming and forestry. development often promote agroforests in the Philippines were studied more Transformations resulting from farming and homegardens as being particularly than half a century ago (Conklin, 1957), and other resource-use activities often lead valuable (Sayer et al., 2013; Scherr and they were found to involve more than to increased habitat diversity as well as McNeely, 2008). 280 types of food crop and 92 recognized

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rice varieties, with several dozen of these The above figures are only for crops products, including such nutritionally usually showing up in any one field. More in farm fields: the landscapes of the valuable products as wild meat. Forest recently, research in the upland rice fields Hanunoo shifting cultivators also included fallows also often provide ecosystem of Southeast Asian farmers has commonly extensive areas of forest of various ages services that are less easily perceived identified some 30 species of staple crops, and with significant levels of biodiversity and measured, such as pollination and 30–40 species of vegetables and 25 spe- (Rerkasem et al., 2009). Although such the maintenance of water quality and cies of herbs and spices (Anderson, 1993; areas in these landscapes are commonly supply. Recent research has determined Sutthi, 1995; Dove, 1985; Colfer, Peluso referred to as fallows, many are managed that forest–field mosaics such as those of and Chung, 1997). intensively for economic and other the Hanunoo often sequester high levels

Hillside swiddens in Nam-Et Phou Louey, northern Lao People’s

© T. SUNDERLAND© T. Democratic Republic

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A hillside subject to shifting of carbon, especially in the soil (Zeigler Can shifting cultivation be sustainable if cultivation in the Lao People’s Democratic Republic et al., 2012). This may surprise many it includes slashing and burning woody researchers and policy-makers because vegetation? slash-and-burn is widely condemned as Many shifting cultivation systems cultivation systems emerges when it is a particularly environmentally damaging worldwide have adapted successfully to seen at broader spatial and longer temporal form of agriculture. larger human populations, new economic scales: shifting cultivation, in common The greatest obstacle to including demands and the directives of anti-slash- with many smallholder-influenced land- shifting cultivation in the new landscape and-burn policies and conservation scapes, is constantly mutable. paradigm, in the eyes of both development prohibitions. Such adaptation has taken professionals and conservationists, is not, a large number of pathways, of which Negative impacts of replacing shifting we suspect, the illegibility of its patchy the more active management of fallows cultivation landscapes (see below) or the complexity of has perhaps been the most important. An important new study (Castella et al., its management, but its inherent dynamism. Examples include the management of 2013) analysed changes in the patterns Change is what defines a system as shifting rich mixtures of marketable fruits and of forest–field landscapes that occurred cultivation: annual crops are moved from fast-growing timbers in Amazonia and as environmental and socio-economic plot to plot every year or two; and as forests the production of rubber and rattans in change transformed the territories of seven regrow in one sector, they are felled in Southeast Asia (Sears and Pinedo-Vasquez, villages in the northern uplands of the another. Can so much dynamic change 2004; Cairns, 2007). These adaptations Lao People’s Democratic Republic over a be tolerated in a “sustainable” landscape? suggest that the sustainability of shifting period of 40 years. In this region, where a

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tradition of shifting cultivation had created TRADITIONAL APPROACHES ARE A planning and design processes grounded intricately patterned landscapes of forests, VALUABLE RESOURCE in improved multistakeholder negotiation fallows and farms, such landscapes are We do not suggest that existing smallholder mechanisms to enhance landscape multi- now being radically altered by policies practices, no matter how diverse, complex functionality and thereby increase the aimed at increasing forest cover and and dynamic, are invariably ideal or well- capacity to respond to unforeseen change”. promoting intensive commercial farming. adapted to rapidly changing conditions. The challenge to improve food security in Shifting cultivation, with its complex We do suggest, however, that this potential the face of great global uncertainty is too landscapes, is deliberately being replaced resource of knowledge, practice and big for the resource offered by traditional with a land-sparing model of agriculture. products should not be ignored. systems to be ignored by research institu- This is because the segregation of land Efforts at agricultural development and tions (Opdam et al., 2013), including the uses is perceived as most efficient for biodiversity conservation (e.g. “social centres of the CGIAR. The challenge achieving multiple objectives in the context forestry”) have often failed to take is also too complex to be met solely by of a growing population, and shifting advantage of the resource that existing following the pathway of sustainable cultivation is widely viewed as “primitive” patterns and practices offers. There are intensification. u by government and other institutions. many reasons for this failure, including Based on extensive field research, a misunderstanding of the diversity that however, Castella et al. (2013) found that characterizes such patterns and practices, by imposing strict boundaries between and their dynamism. Public policies tend to agricultural and forest areas, interven- be sector-oriented and unsuited to manag- tions in the name of land-use planning ing integrated systems. Such systems are have had significant negative impacts essentially “illegible” to outsiders (Scott, on the well-being of rural communities 1998), and local landscape management References and especially on their ability to adapt systems are therefore often ignored, to change. Farm and forest products that denigrated or criminalized by government Anderson, E.F. 1993. Plants and people of previously were “intricately linked at both actors and policies. As in the Lao People’s the Golden Triangle: ethnobotany of the landscape and livelihood levels, are now Democratic Republic, development efforts hill tribes of northern Thailand. Bangkok, found in specialized places, managed by have led to specialization that often limits Silkworm Books. specialized households” (i.e. the domes- the capacity of smallholders to cope with Angelsen, A. & Kaimowitz, D. eds. 2001. tication of non- forest products) and risk and uncertainty. Agricultural technologies and tropical are collected by specialized traders. The . Wallingford, UK, CABI authors argued that “this trend may have Landscape research should build in Publishing. negative consequences for the resilience traditional systems Agrawal, A., Cashore, B., Hardin, R., of the overall landscape as it reduces its What is urgently needed is research that Shepherd, G., Benson, C. & Miller, D. 2013. biological and socio-economic diversity builds on these traditional systems, that Economic contributions of forests. United and therefore increases vulnerability to values what these patterns and practices Nations Forum on Forests background external shocks” (Castella et al., 2013). provide and achieve, and that succeeds in paper no. 1 (available at: www.un.org/esa/ Productive, complex and dynamic improving them to provide the additional forests/pdf/session_documents/unff10/ landscapes in the Lao People’s Democratic food, feed, shelter, income and resilience EcoContrForests.pdf). Republic and elsewhere lend flexibility that smallholders need in a rapidly Barretto, A.G.O.P., Berndes, G., Sparovek, to household economies and contribute changing world and to which they have an G. & Wirsenius, S. 2013. Agricultural to appropriate responses to climatic and intrinsic right. It remains to be seen whether intensification in Brazil and its effects on economic perturbations. Programmes agricultural and forest research institutions land-use patterns: an analysis of the 1975– of directed change, such as the one can respond successfully to this challenge. 2006 period. Global Change Biology, 19: promoted by the Lao Government, attempt Reforms to landscape governance are 1804–1815. DOI: 10.1111/gcb.12174. to create distinct zones for agricultural also imperative to allow systems that Bodmer, R.E. & Pezo Lozano, E. 2001. Rural intensification and forest conservation. Up embrace landscape complexity, dynamism development and sustainable wildlife use in to now, however, they have not led to more and multiple objectives and engage all Peru. Conservation Biology, 15: 1163–1170. sustainable resource management, and stakeholder groups in collectively managing Brinkman, H.J., Pee, S., Sanogo, I., Subran, L. the simplified, intensified agro-ecological diverse, multifunctional landscapes. & Bloem, M. 2010. High food prices and the systems that have been advocated have not We echo the conclusions of Castella et al. global financial crisis have reduced access benefited local people. (2013) in calling for “more integrative to nutritious food and worsened nutritional

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status and health. Journal of Nutrition, 140: Pretty, J., Robinson, S., Thomas, S. & Perfecto, I. & Vandermeer, J. 2010. The 1535–1615. Toulmin, C. 2010. Food security: the agroecological matrix as alternative to the Cairns, M. ed. 2007. Voices from the forest: challenge of feeding 9 billion people. land-sparing/agriculture intensification integrating indigenous knowledge into Science, 327(5967): 812–818. model. Proceedings of the National sustainable upland farming. Washington, Goulding, M., Smith, N.J.H. & Mahar, D.J. Academy of Sciences USA, 107: 5786–5791. DC, Resources for the Future. 1995. Floods of fortune: ecology and Phalan, B., Onial, M., Balmford, A. & Castella, J-C., Lestrelin, G., Hett, C., economy along the Amazon. New York, Green, R. 2011. Reconciling food Bourgoin, J., Fitriana, Y.R., Heinimann, A. USA, Columbia University Press. production and biodiversity conservation: & Pfund, J-L. 2013. Effects of landscape Hiraoka, M. 1992. Caboclo resource land sharing and land sparing compared. segregation on livelihood vulnerability: management: a review. In K. Redford & Science, 333(6047): 1289–1291. moving from extensive shifting cultivation C. Padoch, eds. Conservation of neotropical Pinedo-Vasquez, M., Padoch, C., McGrath, D. to rotational agriculture and natural forests forests: working from traditional resource & Ximenes-Ponte, T. 2002. Biodiversity as in northern Laos. Human Ecology, 41: 63–76. use. New York, USA, Columbia University a product of smallholder response to change Chappell, M.J., Vandermeer, J.H., Press. in Amazonia. In H. Brookfield, C. Padoch, Badgley, C. & Perfecto, I. 2009. Wildlife- Ickowitz, A. 2006. Shifting cultivation and H. Parsons & M. Stocking, eds. Cultivating friendly farming vs. land sparing. Frontiers deforestation in tropical Africa: critical biodiversity, pp. 167–178. London, ITDG in Ecology and the Environment, 7: 183–184. reflections. Development and Change, 37: Publishing. Colfer, C.J.P., Peluso, N.L. & Chung, C.S. 599–626. Pinedo-Vasquez, M., Zarin, D., Coffey, K., 1997. Beyond slash and burn: building Lynam, J. & Herdt, R. 1989. Sense and Padoch, C. & Rabelo, F. 2001. Post-boom on indigenous management of Borneo’s sustainability: sustainability as an objective timber production in Amazonia. Human tropical rain forests. New York, USA, New in agricultural research. Agricultural Ecology, 29: 219–239. York Botanical Garden. Economics, 3: 381–398. Pinstrup-Andersen, P. 2013. Can agriculture Collins, E.D. & Chandrasekaran, K. 2012. Mertz, O., Padoch, C., Fox, J., Cramb, meet future nutrition challenges? Special A wolf in sheep’s clothing? An analysis of the R.A., Leisz, S., Lam, N.T. & Vien, T.D. debate section. European Journal of ‘sustainable intensification’ of agriculture. 2009. Swidden change in Southeast Asia: Development Research, 25(1): 5–12. Friends of the Earth International (available understanding causes and consequences. Pretty, J. 2009. Sustainable intensification at: www.foei.org/en/wolf-in-sheeps-clothing). Human Ecology, 37: 259–264. of agriculture. Natural Resources Forum, Conklin, H.C. 1957. Hanunoo agriculture: Opdam, P., Nassauer, J.I., Wang, Z., 21: 247–256. a report on an integral system of shifting Albert,C., Bentrup, G., Castella, J.C., Rerkasem, K., Lawrence, D., Padoch, C., cultivation on the Philippines. Rome, FAO. McAlpine, C., Liu, J., Sheppard, S. & Schmidt-Vogt, D., Ziegler, A.D. & Bruun, Cramb, R.A., Colfer, C.J.P., Dressler, Swaffield, S.2013. Science for action at the T.B. 2009. Consequences of swidden W., Laungaramsri, P., Trung, L.Q., local landscape scale. Landscape Ecology, transitions for crop and fallow biodiversity Mulyoutami, E., Peluso, N.L. & Wadley, 28(8): 1439–1445. in Southeast Asia. Human Ecology, 37(3): R.L. 2009. Swidden transformations and Padoch, C. & Pinedo-Vasquez, M. 2000. 347–360. rural livelihoods in Southeast Asia. Human Farming above the flood in the várzea of Rocha, C. 2007. Food insecurity as market Ecology, 37: 323–346. Amapa: some preliminary results of the failure: a contribution from economics. Dove, M.R. 1985. Swidden agriculture in Projeto Várzea. In C. Padoch, J.M. Ayres, Journal of Hunger & Environmental Indonesia. Berlin, Mouton. M. Pinedo-Vasquez & A. Henderson, Nutrition, 1(4): 5–22. Evenson, R. & Gollin, D. 2003. Assessing eds. Varzea: diversity, development, and Rudel, T., Schneider, L., Uriarte, M., the impact of the Green Revolution, 1960 to conservation of Amazonia’s Whitewater Turner II, B., DeFries, R., Lawrence, D., 2000. Science, 300(5620): 758–762. Floodplain, pp. 345–354. New York, USA, Geoghegan, J., Hecht, S., Ickowitz, A., FAO, IFAD & WFP. 2013. The state of food New York Botanical Garden Press. Lambin, E., Birkenholtz, T., Baptista, S. & insecurity in the world 2013. The multiple Padoch, C., Coffey, K., Mertz, O., Leisz, S., Grau, R. 2009. Agricultural intensification dimensions of food security. Rome, FAO. Fox, J. & Wadley, R.L. 2007. The demise and changes in cultivated areas, 1970–2005. Fox, J., Fujita, Y., Ngidang, D., Peluso, N.L., of swidden in Southeast Asia? Local realities Proceedings of the National Academy of Potter, L., Sakuntaladewi, N., Sturgeon, J. and regional ambiguities. Geografisk Sciences, 106(49): 20675–20680. & Thomas, D. 2009. Policies, political- Tidsskrift – Danish Journal of Geography, Sayer, J., Sunderland, T., Ghazoul, J., economy, and swidden, in Southeast Asia. 107: 29–41. Pfund, J-L., Sheil, D., Meijaard, E., Human Ecology, 37: 305–322. Padoch, C. & Pinedo-Vasquez, M. 2010. Venter, M., Boedhihartono, A.K., Godfray, C., Beddington, J., Crute, I., Saving slash-and-burn to save biodiversity. Day, M., Garcia, C., van Oosten, C. & Haddad, L., Lawrence, D., Muir, J., Biotropica, 42: 550–552. Buck. L. 2013. The landscape approach: ten

Unasylva 241, Vol. 64, 2013/2 13

principles to apply at the nexus of agriculture, 2012. Global food security, biodiversity conservation and other competing land-uses. conservation and the future of agricultural Proceedings of the National Academy of intensification. Biological Conservation, Sciences, 110(21): 8349–8356 (available 151: 5351g. at: www.pnas.org/content/110/21/8349.full. Van Vliet, N., Mertz, O., Heinimann, A., pdf+html). Langanke, T., Pascual, U., Schmook, B., Sayer, J. & Cassman, K. 2013. Agricultural Adams, C., Schmidt-Vogt, D., Messerli, P., innovations to protect the environment. Leisz, S.J., Castella, J.C., Jørgensen, L., Proceedings of the National Academy of Birch-Thomsen, T., Hett, C., Bech-Bruun, Sciences, 110(21): 8345–8348 (available T., Ickowitz, A., Vu, K.C., Yasuyuki, at: www.pnas.org/content/110/21/8345.full. K., Fox, J., Padoch, C., Dressler, W. & pdf+html). Ziegler, A.D. 2012. Trends, drivers and Scherr, S. & McNeely, J.A. 2008. Biodiversity impacts of changes in swidden cultivation conservation and agricultural sustainability: in tropical forest-agriculture frontiers: a towards a new paradigm of “eco-agriculture” global assessment. Global Environmental landscapes. Philosophical Transactions of Change, 22: 418–429. DOI: 10.1016/ the Royal Society B, 363: 477–494. j.gloenvcha.2011.10.009. Schmidt-Vogt, D., Leisz, S., Mertz, O., Van Noordwijk, M., Mulyoutami, E., Heinimann, A., Thiha, T., Messerli, P., Sakuntaladewi, N. & Agus, F. 2008. Epprecht, M., Cu, P.V., Vu, K.C., Hardiono, Swiddens in transition: shifted perceptions M. & Truong, D.M. 2009. An assessment of on shifting cultivators in Indonesia. trends in the extent of swidden in Southeast Occasional Paper No. 9. Bogor, Indonesia, Asia. Human Ecology, 37: 269–280. World Agroforestry Centre. Scott, J. 1998. Seeing like a state: how certain Welch, R. & Graham, R. 1999. A new schemes to improve the human condition paradigm for world agriculture: meeting have failed. New Haven, USA, Yale human needs: productive, sustainable, University Press. nutritious. Field Crops Research, 60: 160d Sears, R.R. & Pinedo-Vasquez, M. 2004. (available at: http://dx.doi.org/10.1016/ Axing the trees, growing the forest: S0378-4290(98)00129-4). smallholder timber production on the Ziegler, A., Phelps, J., QI Yuen, J., Webb, E., Amazon varzea. In D. Zarin, J. Alavalapatti, Lawrence, D., Fox, J., Bruun, T., Leisz, F.E. Putz & M.C. Schmink, eds. Working S., Ryan, C., Dressler, W., Mertz, O., forests in the American tropics: conservation Pascual, U., Padoch, C. & Pin Koh, L. through sustainable management? pp. 258– 2012. Carbon outcomes of major land-cover 275. New York, USA, Columbia University transitions in SE Asia: great uncertainties Press. and REDD+ policy implications. Global Sunderland, T.C.H., Ehringhaus, C. & Change Biology, 3087–3099. u Campbell, B.M. 2008. Conservation and development in tropical forest landscapes: a time to face the trade-offs? Environmental Conservation, 34(4): 276–279. Sutthi, C. 1995. Swidden crop germplasm in the highlands of Thailand. Chiang Mai, Thailand, Tribal Research Institute. Tilman, D., Cassman, K., Matson, P., Naylor, R. & Polasky, S. 2002. Agricultural sustainability and intensive production practices. Nature, 418: 671–677. Tscharntke, T., Clough, Y., Wanger, T., Jackson, L., Motzke, I., Perfecto, I., Vandermeer, J. & Whitbread, A.

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The role of ecosystems in food security

J.C. Mohamed-Katerere and M. Smith FAO/I. KODIKARA

A farmer tends a water buffalo calf in Padukka, Sri Lanka. Ecosystems provide Food-security policies should be gricultural production cannot be essential services for global food security “ecosystem-aware” by encouraging sustained without ecosystem resil- diversity at different scales, ience and integrity. Ecosystems are maintaining natural infrastructure, Acommunities of plants, animals and other and ensuring social justice. organisms that live, feed, reproduce and Ecosystem governance interact in an area or environment. They underpin agricultural production by, for Ecosystem governance can be defined example, protecting soil and water, helping as the interaction of laws and other to maintain soil fertility, and providing norms, institutions and processes habitat for wild pollinators and the through which a society exercises predators of agricultural pests. Ecosystem powers and responsibilities to make degradation, coupled with weak ecosystem and implement decisions affecting eco- governance (see box), compromises the system services and to distribute benefits ability of people to farm, access and use and duties. Governance of ecosystem food effectively and, in so doing, under- services emerges from the interplay mines the effectiveness of food-security of governmental, intergovernmental policies. Poor people and other vulnerable and non-governmental institutions, the groups, including women and children and private sector and civil society, based particularly those in rural areas, are most on rules and policies established by Jennifer Mohamed-Katerere is at the International Union for Conservation of Nature at risk from any erosion of food security. statutory and customary law as well as (IUCN) Commission on Environmental, This article examines the many roles of through practice. Economic and Social Policy and the IUCN ecosystems in food security and argues the Natural Resource Governance Framework, and Mark Smith is at the IUCN Global Water case for an “ecosystem-aware” approach Source: Greiber and Schiele, 2011 Programme. to food-security policy-making.

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AN ECOSYSTEM-AWARE APPROACH An ecosystem-aware approach to food secu- Ecosystem restoration, social inclusion and diversity enhance food rity aims not only to alleviate hunger in the security in the Tacaná Volcano area in Guatamala and Mexico short term but also to build long-term “food resilience” – defined here as the capacity In the high-altitude upper watersheds of the Suchiate River and the Coatán in Guatemala of ecosystems to support food production and Mexico, the IUCN Water and Nature Initiative has co-executed projects that combine and the ability of people to produce, harvest the rehabilitation of ecosystems with the development of social capital through income or buy food in the face of environmental, generation. Activities such as aquaculture, honey production and agro-ecology (community economic and social shocks and stresses. gardens); and mangrove conservation; solid waste recycling and earthworm An example of such a shock was the 2012 production; and septic tank initiatives have helped reduce soil erosion and the risk of drought in the United States of America, flooding and increase food security. Reforestation activities, including the establishment which reduced maize production and sent of forest nurseries and the planting of 45 000 plants to reforest 45 hectares of land with global prices soaring (Da Silva, 2012); native tree species threatened with extinction, have contributed to slope stabilization and another example was the 2004–05 locust watershed protection. To help increase household income, women and the young received invasions in the Sahel, which decimated training on how to start new businesses. Gender and age-dependent skills’ training was crops and contributed to a major food crisis vital for curbing unemployment and migration. Households have gained more access there (IFRC, 2005). Stresses are slower- to food and higher nutrition as a result of greenhouse production, mushroom-growing, onset changes such as increasing aridity or crop diversification and agroforestry, as well as the restoration of the irrigation system. temperature changes, the intensification of conflicts, discrimination, a lack of access Source: M. Smith, personal communication, 2013 to resources, debt, and inflation. In theory, stresses are easier to respond to because they have a higher level of predictability; policy measures and from collaborating Only when all four dimensions are for poor people and developing countries, with other sectoral policy-making initia- fulfilled simultaneously does an individual, however, low levels of social and economic tives to ensure that all such initiatives household, community or nation achieve well-being make coping with stresses a support food security. Effective policies food security. considerable challenge. will also address the social aspects of an Preparing better for shocks and stresses ecosystem-aware approach to food security ECOSYSTEM CONTRIBUTIONS TO can help boost food production. A study of by strengthening land tenure, access rights FOOD SECURITY 73 countries, for example, found that those to natural resources, local organizations, Ecosystems, including forests, contribute countries with more equitable initial land and gender equality. to all four dimensions of food security, as distribution achieved economic growth illustrated in Figure 1. For example: rates 2–3 times higher than those without THE FOUR DIMENSIONS OF FOOD • Forests contribute to soil processes, (Deininger, 2003). FAO (2011) found that if SECURITY including the maintenance (and women had the same access to productive Food security can be thought of as com- sometimes increase) of fertility, and resources as men they could increase yields prising four dimensions (FAO, 2008): reduce soil erosion, and they provide on their farms by 20–30 percent and total • availability – the supply of sufficient habitat for wild pollinators and the agricultural output in developing countries quantities of food of appropriate qual- predators of agricultural pests. by 2.5–4 percent. This would reduce the ity, from both natural and cultivated • Forests provide access to food both number of hungry people in the world by systems; directly (through the edible wild 12–17 percent and lift 100–150 million • access – the ability of individuals to plants and animals found there, and people out of hunger. IUCN experience obtain food at all times through their as a source of genetic material for in the Tacaná Volcano area in Central own production or from markets or domestication) and indirectly (via America shows that ecosystem restora- other sources; forest-product income that can be tion, greater agricultural and ecosystem • utilization – the means by which indi- used to buy food). diversity, and investment can boost food viduals are able to gain energy and • Medicinal plants obtained from forests security (see box). nutrition from food; contribute to people’s health, increas- Food-security policy-makers in all • stability – the availability of sufficient ing the efficiency of, and benefits countries have much to gain from and adequate food that is accessible obtained from, food consumption. integrating ecosystem management and and usable on a reliable, sustainable • Mangrove and other coastal forests good ecosystem governance in their basis. help protect coastal areas from

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1 Ecosystem contributions to the four dimensions of food security Utilization ••Water resources flooding, thereby increasing the stabil- ••Energy resources for cooking ity of food production in nearby fields and fish ponds. ••Health-related ecosystem goods and services (e.g. medicinal plants, water WHY SHOULD FOOD SECURITY purification, diverse and POLICY-MAKERS WORRY ABOUT nutrition-rich wild foods) ECOSYSTEMS? Ecosystem degradation can undermine the effectiveness and impacts of food-security policies, while inappropriate policies can Availability Access damage ecosystems and their ability to ••Edible wild plants and animals ••Access to natural resources support food systems. Some of the con- ••Freshwater for food production sequences of ecosystem degradation for ••Soil processes ••Direct sources of food and food security are described below. freshwater ••Wild pollinators ••Income from ecosystem- ••Predator–prey regulation Availability of food based livelihoods (farming, ••Grazing/fodder fishing, forestry, mining, Food availability depends on the pro- ••Climate and water regulation tourism) and payment for ductivity of both cultivated and natural ecosystem services systems. Globally, poor rural people are most severely affected by food insecurity, with 80 percent of these communities being food insecure (compared with 20 percent of poor urban populations), STABILity and they rely heavily on natural resources ••Sustainable provision of ecosystem goods and services to maintain their livelihoods. About ••Biodiversity, including agrobiodiversity half of all food-insecure people live in ••Natural infrastructure for stability and disaster risk reduction (e.g. flood regulation, drought mitigation, soil retention, coastal protection) smallholder farming households and roughly one-fifth are landless (Sanchez et al., 2005). In poor rural communities, therefore, resource degradation can make fisheries and aquaculture – which, in turn, Use of food the difference between having food and often have a significant dependence on Rural and urban poor people in develop- going hungry. Worldwide, almost half a forests – support the livelihoods of 8 per- ing countries depend on natural billion poor people are estimated to meet cent of the world’s population. Many poor (particularly wood) for cooking and a significant proportion of their food needs people rely on the sale of timber and non- certain forms of food preservation (e.g. from the harvesting of wild plants and timber forest products (such as wild meat, smoking and drying). Access to woodfuel animals (Sanchez et al., 2005). Ecosystem honey, medicinal plants and woodfuel) expands the choice and range of foods degradation and natural disasters that to buy food and meet other important that are consumed, including important reduce the availability of these food household expenses (Sunderland, 2011). protein sources such as beans and meat sources will also have a large impact on In general, ecosystem-based activities that require higher levels of energy for food security. (such as agriculture, forestry, fisheries and preparation. The loss of access to woodfuel tourism) are critically important sources through deforestation or resource-use Access to food of income for poor people, especially restrictions, therefore, can affect both Globally, about 1 billion people earn in rural areas. Threats to these income the quantity and quality of food. Insecure income from the use of wild natural sources – from, for example, ecosystem environmental conditions – caused, for resources (Pimentel et al., 1997). Marine, degradation, natural disasters, conflict and example, by high winds, floods, pests freshwater and forest resources are particu- the collapse of commodity prices – have and plant diseases – can reduce effective larly important: according to FAO (2010), severe knock-on effects on food security. food storage.

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STABILITY OF FOOD SUPPLY Unsustainable development development for coastal tourism (e.g. A stable food supply implies food systems Economic development that appropri- hotels, piers and recreational facilities), for that ensure sustainable food availability, ates resources and ecosystems and gives example, increases effluent discharges, dis- access and use. It also requires that food tighter control over them to the state or turbs coastal ecosystems such as mangrove systems are resilient to social, economic through them to private investors tends to forests, and reduces access to coastal flats and environmental shocks and stresses. restrict access by poor people to critical that, in many countries, serve as seaweed- Some such shocks and stresses, and their food-security assets such as forests, coasts and mollusk-harvesting grounds for local policy implications, are outlined below. and water resources. Infrastructure people. Rapid urbanization can also lead to reduced access to food because the poor people in urban areas are less connected to wild foods and therefore have less potential to earn income using natural resources. Unsustainable agricultural and industrial development is causing widespread dam- age to ecosystems through the pollution of land and water. UNEP (2006) reported that, globally, little or no progress had been achieved in preventing, reducing or controlling pollution of the marine environment. Fertilizer runoff, for example, damages marine and freshwater ecosystems, including coral reefs, and diminishes the availability of fish and molluscs, which are critical protein sources for many. The impact of nitrogen pollution has been particularly severe, resulting in a 50–90 percent decline in mangroves in most regions over the last four decades (UNEP, 2006). The number of coastal dead zones has increased dramatically in recent years. Of the 169 coastal dead zones worldwide, only 13 are recovering, and 415 coastal areas suffer from eutrophica- tion (UNEP, 2006). Around 80 percent of marine pollution is caused by land-based activities. Pollution, climate change and increased catches have contributed to an unprecedented deterioration in fish stocks in the last 20 years (Gaddis et al., 2012). Although catches more than quadrupled between the early 1950s and the mid-1990s, they have stabilized or diminished since then, despite increased fishing (Gaddis et al., 2012). Some 1 141 fish species are vulner- able to endangerment, 486 are endangered

Children play in clean water in a forest in Thailand. Ecosystems provide clean water for downstream agriculture and

FAO/S. TUNGSAGULGRAIT FAO/S. for human consumption

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These trees in central Sudan have been cut by refugees from a nearby camp who were in search of wood and fodder. Conflict and other shocks and stresses make it more difficult for affected populations to produce and access food and obtain the water and energy needed for food preparation

and 60 are extinct (FAO, 2010; IUCN Red Data List1). Coastal-zone degrada- tion has resulted in increased human health risks and agricultural losses and the reduced availability of highly valued wild-harvested foods.

Climate change FAO/F. MCDOUGALL A range of potential changes to climate, such as reduced rainfall, temperature extremes, rising sea-levels and more frequent floods and droughts, can affect food security. While the impacts of climate change on food production could be food production. The possibility of the injustice, inequity and poverty. Conflicts positive in some regions, overall they are state extending its claim to resources, such over land and water are expected to increase likely to be detrimental to food security as forest carbon as part of climate mitiga- as demand grows for these resources in the and nutrition. For example, it is estimated tion policies and medical plants as part of face of climate change, increasing popula- that climate change will cause a ten percent patent protection, remains a real threat tion pressure and restrictions on access. increase in the number of malnourished to land and natural-resource security for Conflicts can have profound impacts on children worldwide by 2050, relative to a rural communities. Tenure over water and food security by causing institutional “no climate change” future (Committee fishery resources is commonly claimed by decline, worsening social relations and on World Food Security, 2012). Climate the state, even when indigenous and other increasing violence, which tend to decrease change could also initiate spirals of local communities have customary rights. local food production and increase its cost ecosystem degradation, magnifying the A recent consequence of insecure, ineq- (Bora et al., 2010; Sayne, 2011; Schöninger, direct impacts of climate change on food uitable tenure regimes is the proliferation 2006; Teodosijević, 2003). Conflict makes security. Extreme weather events could of foreign investments in land. This it more difficult for affected populations damage food transportation and storage expansion – estimated to amount to up to to produce and access food and obtain the infrastructure, reduce state capacity to 134 million hectares in Africa and 203 mil- water and energy needed for food prepara- respond to crises, increase food prices and lion hectares worldwide between 2000 and tion. Food insecurity is often compounded yield fluctuations and lead to a deteriora- 2010 (Anseeuw et al., 2012) – reduces the by the destruction of rural infrastructure, tion in social cohesion, all of which are availability of, and access to, both wild and the loss of livestock, deforestation, the likely to increase food insecurity. farmed food for marginalized communi- widespread use of landmines, the poison- ties. Many foreign investments in land are ing of wells, and large-scale population Inequitable tenure for biofuels, minerals, timber and food movements caused by conflict. Where land tenure is insecure or unclear, exports. The rapid expansion of biofuel or where the state claims legal title, agri- production is expected to contribute to an FOOD SECURITY POLICIES: cultural development tends to favour increase of up to 3 million undernourished WHAT’S MISSING? large-scale over smallholder production. preschool children in Africa and South Development and conservation efforts Insecure tenure also acts as a disincentive Asia by 2050 (FAO, 2009). contribute to food insecurity if they do not for local land users to make long-term take into account the strong connections investments – such as tree-planting – to Conflict between food security and ecosystems. maintain ecosystem functions and improve Weak ecosystem governance can heighten High levels of vulnerability to food inse- conflict and contribute to the primary curity among the poorest groups in society 1 www.iucnredlist.org causes of such conflict by exacerbating are generally linked to a heavy dependence

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on natural ecosystems that are undergoing Gaps in food-security policy-making nutrition in consistent ways. This lack rapid degradation and change and to the Food-security policies and practices have of coordination between sectors leads to ecosystem governance systems in place a number of shortcomings, some of which disconnected, sometimes contradictory and how they are implemented. When are discussed below. policies and the neglect of intersectoral either or both these factors – development Lack of a multisectoral approach. linkages and synergies (e.g. food–water– and conservation on the one hand and Food-security issues are too often dealt energy and food–health–nutrition). inequitable and exclusionary ecosystem with in “policy silos”, in which the relevant Lack of integration of ecosystem governance on the other – reduce the pro- institutions (e.g. on agriculture, forestry, factors. Few food-security policies ductivity or accessibility of, for example, trade and environment) rarely collaborate acknowledge the importance of maintain- wild foods, agricultural crops and water, to ensure that their various policies are ing and sustainably managing ecosystems, they undermine livelihoods as well as the coherent and address food security and with the common result that policies are social relations that hold communities together. The resulting food insecurity is often accompanied by conflict within and between communities and neglect of the most vulnerable groups, including women and children. Many food-security policies have improved in the last decade, including by increasingly acknowledging the right to adequate food and the importance of equitable and secure tenure. But the focus generally remains on agricultural produc- tivity, trade and macroeconomic policies, while the central role played by ecosystems in food security continues to be neglected. Knowledge of the importance of eco- systems to the various dimensions of food security has grown, but there continues to be insufficient investment in main- taining environmental quality, building positive social relationships around natu- ral-resource use (institutions, organizations and learning) and developing linkages between stakeholders and sectors. The idea that there is an inevitable trade-off between agricultural productivity and ecosystem conservation is outdated, given current understanding of the dependence of agriculture on wider ecosystems and the many options for sustainably managing productive ecosystems. There is no choice but to do both – otherwise, food security will remain a pipe dream.

A farmer works the land on the banks of FAO/G. NAPOLITANO FAO/G. Burera Lake, Rwanda. Few food-security policies acknowledge the importance of maintaining and sustainably managing ecosystems, with the common result that they lead to land degradation and therefore food insecurity

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ill-informed and ineffective and contribute (UNEP, 2012; Rockstrom et al., 2009) • the resilience of ecosystems to main- to ecosystem mismanagement and degra- but largely absent from policy debate tain their support for the production dation and therefore to food insecurity. about food. of both wild and farmed foods in the Lack of participatory decision-making. Recognition of wild resources. Food- face of shocks such as extreme weather Key actors are frequently left out of food- security and other natural-resource-related events and stresses such as pollution. security decision-making; consequently, policies still fail to acknowledge that wild Policy-making can best support food decisions do not always reflect the rights, resources are critical to the food security resilience by addressing three key issues: cultures and interests of local people. Even of a significant proportion of the world’s diversity, natural infrastructure and social where some degree of local participation poorest people. Without this recognition, justice. Each of these is described below. is sought, it is often limited to men. Poor such policies risk cutting off access to rural communities, smallholders, women foods such as wild meat and fish, thereby Diversity and other “front-line” stakeholders are depriving many rural people of vital The term diversity is used here to refer to often the primary custodians of ecosys- sources of protein. ecosystem, biological and livelihood diver- tems and are usually the most affected by sity. Diversity in the ecosystems present in food insecurity. Policies that ignore their HOW TO MAKE FOOD-SECURITY a landscape and the biological resources voices are unlikely to be effective. POLICIES MORE EFFECTIVE within these ecosystems can reduce the Commitment to climate-change action. Focus on food resilience sensitivity of local people to shocks and There has been little sign of commit- Ecosystem-aware food-security policies stresses (including price volatility) by sup- ment to redress the underlying drivers of aim not only to alleviate hunger in the porting diverse livelihood and adaptive climate change and in particular the pat- short term but also to build long-term food activities (e.g. agriculture and livestock terns of consumption and production that resilience, which is critical if food-security farming, fisheries, forestry, tourism and use energy unsustainably and generate objectives are to be achieved and sustained hunting). Together, the various aspects unmanageable amounts of pollution and in the long term. Ecosystem-aware food- of diversity can strengthen food security waste. The understanding that ecologi- security policies strengthen both: by reinforcing the resilience of local cal degradation will limit opportunities • the resilience of food-insecure com- food systems, and policies that maintain to ensure food security and develop- munities to manage uncertainties and or boost diversity will therefore support ment opportunities is well-established stresses such as food-price hikes and food-security objectives. For example, in the policy and academic literature climate change; policies that promote diversity within a

A forest ranger monitors wild bird FAO/G. NAPOLITANO FAO/G. populations in the Lake Ichkeul area in Tunisia. Wetlands help clean effluent, similar to water treatment facilities

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cropping system (e.g. crop diversity, soil By addressing social justice, food- Effective policies recognize that the biodiversity and pollinator diversity) can security policies can strengthen food services provided by ecosystems are not increase the capacity of agriculture to resilience. Critically, support is required limitless. This includes the capacity of adapt to fluctuations in growing conditions for local governance systems, par- ecosystems to absorb waste. Policies should by (Boelee, Chiramba and Khaka, 2011): ticularly locally managed resource use tackle land, water and air pollution to help • increasing water availability and thus and locally controlled production. For support human and ecosystem health and the resilience of rural livelihoods; example, policies that strengthen the wild food supplies (such as fish, fruit • providing nitrogen-fixing capacity organizations of smallholder producers and wild meat). For example, municipal through the incorporation of trees build local resilience by increasing the and industrial wastewater can be treated and leguminous crops; ability of farmers to set shared priorities, effectively with existing technologies, but • strengthening habitat connectivity for negotiate fair prices and make decisions such treatment requires strong regulatory pollinators through the incorporation on the distribution of resources necessary oversight and significant infrastructure of areas of natural habitat. to increase food production. investment and capacity-building, Other areas that are critical for food secu- especially in developing countries. Natural infrastructure rity are building good social relations and Effective policies link across sectors. The term natural infrastructure reflects the tackling inequalities, including widespread Food-security policy-making needs to be ability of ecosystems to deliver some of the discrimination against women. Policies based on better integration of the various same services that can also be provided by can help remove such discrimination by economic and development sectors. In engineered infrastructure. For example: formally recognizing gender equality and particular, the environment should be • Forests help provide clean drink- implementing specific policies to improve better integrated with the policies of ing water, similar to water filtration women’s food security and productivity. those sectors – such as trade, energy, facilities. These policies can be as simple as getting water, health and tourism – that affect the • Mangroves help protect shorelines potable water into villages: it has been ecosystem services underpinning food from storm damage, similar to sea estimated that, in the United Republic of security. Such integration will require walls. Tanzania (total population of 46 million giving environmental agencies a more • Natural floodplains help prevent flood- people), women collectively spend 8 billion central role in developing strategies for ing, similar to dikes and canals. hours of unpaid work per year in water achieving food security. • Wetlands help clean effluent, similar and fuel collection and food preparation, Effective policies see agricultural to water treatment facilities. which is equivalent to the hours required systems as agro-ecosystems. Agro- Natural infrastructure services contrib- for 4.6 million full-time jobs (Fontana ecosystems provide a wide variety of ute to the food resilience of communities, and Natali, 2008). Other policies that ecosystem services and are linked to for example by protecting farmland against improve productivity include those that other ecosystems. Taking this broader storm surges and safeguarding communi- secure tenure, increase knowledge, such as view of how agricultural systems fit within ties from contaminated drinking water. To by specifically targeting women in agricul- landscapes enables policies to identify and help maintain these ecosystem services, tural extension, and improve health (FAO, act on opportunities for synergies between food-security policies need to be better 2011). Social justice cannot be ignored by crop and livestock production, fisheries integrated with those of other economic food-security policy-makers. It is morally and forestry to achieve food security. sectors, such as environment, forestry, and ethically unacceptable that so many Effective policies value ecosystems as fisheries, tourism and energy. people still lack the opportunity to live productive assets. Food-security policies free from hunger. should recognize the need to maintain natu- Social justice ral assets on the grounds that they provide Social justice embodies the ideas of good WHAT DO EFFECTIVE FOOD- important safety nets for the food-insecure governance, economic fairness, human SECURITY POLICIES LOOK LIKE? and form the basis of diversified livelihoods. rights, solidarity, equality and equity. To be effective, food-security policies This recognition does not mean abandoning It is central to food security because it need to be ecosystem-aware and sup- the total protection of particularly fragile plays a large part in determining access portive of food resilience by addressing or threatened ecosystems, but it does mean to food within households, communities, issues of diversity in multiple systems at looking at protection as one tool in recover- societies and nations. Where social justice different scales, natural infrastructure ing and maintaining ecosystem services and is weak, there is a high risk of food inse- and social justice. Effective food-security considering interactions between protected curity, especially among vulnerable and policies will also adhere to the following areas, neighbouring agro-ecosystems and marginalized groups. principles. other sustainably managed ecosystems.

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Effective policies support increased Boelee, E., Chiramba, T. & Khaka, E. eds. future we want. Nairobi, United Nations investment in off-farm ecosystem assets. 2011. An ecosystem services approach to water Environment Programme. The rationale for such policies is that off- and food security. Nairobi, United Nations Greiber, T. & Schiele, S. eds. 2011. Governance farm ecosystem assets such as forests can Environment Programme, and Colombo, of ecosystem services. Gland, Switzerland, strengthen the resilience of smallholder International Water Management Institute. IUCN. farmers and pastoralists and support Bora, S., Ceccacci, I., Delgado, C. & Townsend, IFRC. 2005. World disaster report 2005. diversified livelihood options, including R. 2010. Food security and conflict. Geneva, Switzerland, International non-agricultural income sources. This Background paper for the World Development Federation of Red Cross and Red Crescent reduces the vulnerability of rural poor Report. Washington, DC, The World Bank. Societies. people to extreme weather events and Committee on World Food Security. 2012. Pimentel, D., McNair, M., Buck, L., price shocks. Ensuring that local people Food security and climate change. High Pimental, M. & Kamil, J. 1997. The value are able to use these off-farm opportunities Level Panel of Experts Report 3. Rome, of forests to world food security. Human requires financial and technical support FAO (available at:www.fao.org/fileadmin/ Ecology, 25: 91–120. for knowledge exchange and learning, as user_upload/hlpe/hlpe_documents/HLPE_ Rockström, J., Steffen, W., Noone, K., well as robust local organization. Reports/HLPE-Report-3-Food_security_ Persson, Å., Chapin III, F.S., Lambin, Effective policies strengthen local and_climate_change-June_2012.pdf). E., Lenton, T.M., Scheffer, M., Folke, organization and amplify the voices of Da Silva, J.G. 2012. The US must take biofuel C., Schellnhuber, H., Nykvist, B., De rural communities. Local communities action to prevent a food crisis. Financial Wit, C.A., Hughes, T., van der Leeuw, are often the custodians of ecosystems and Times, 9 August 2012 (available at: www. S., Rodhe, H., Sörlin, S., Snyder, P.K., the managers of food production from both ft.com/intl/cms/s/0/85a36b26-e22a-11e1- Costanza, R., Svedin, U., Falkenmark, wild and farmed resources and therefore b3ff-00144feab49a.html#axzz2392Moy8Z). M., Karlberg, L., Corell, R.W., Fabry, are critical actors in sustaining natural Deininger, K. 2003. Land policies for growth V.J., Hansen, J., Walker, B., Liverman, resources and managing conflict over them. and poverty reduction. World Bank Policy D., Richardson, K., Crutzen, P. & Foley, Supporting the inclusion of both women Research Report. Washington, DC, The J. 2009. Planetary boundaries: exploring the and men in local communities – farm- World Bank. safe operating space for humanity. Ecology ers, pastoralists, forest people, shifting FAO. 2008. An introduction to the basic and Society, 14(2): 32 (available at: www. cultivators, fisherfolk and other food concepts of food security. Food Security ecologyandsociety.org/vol14/iss2/art32/). harvesters and producers – in decision- Information for Action. Practical Guides. Sanchez, P., Swaminathan, P.D., Dobie, P. & making about food security can help Rome (available at: www.fao.org/docrep/013/ Yuksel, N. 2005. Halving hunger: it can be ensure more appropriate decisions and al936e/al936e00.pdf). done. New York, USA, Millennium Project. policies. Food-security policies need to FAO. 2009. How to feed the world in 2050. Sayne, A. 2011. Climate change adaptation help rural communities engage with other Background paper for the How to Feed the and conflict in Nigeria. Special report. stakeholders in defining solutions, and World in 2050 Forum, 12–13 October 2009, United States Institute of Peace. they should support the recognition of the Rome (available at: www.fao.org/fileadmin/ Schöninger, I. ed. 2006. The challenge rights of rural communities to information, templates/wsfs/docs/expert_paper/How_to_ of hunger: global hunger index: facts, transparency, accountability, participation Feed_the_World_in_2050.pdf). determinants, and trends. Washington, DC, and recourse to justice. u FAO. 2010. The state of the world’s fisheries International Food Policy Research Institute. and aquaculture 2010. Rome. Sunderland, T.C.H. 2011. Food security: why FAO. 2011. The state of food and agriculture biodiversity is important. International 2011: women in agriculture, closing the Forestry Review, 13(3): 265–274. gender gap. Rome. Teodosijevic, S. 2003. Armed conflicts and Fontana, M. & Natali, L. 2008. Gendered food security. ESA Working Paper No. 3-11. patterns of time use in Tanzania: public Rome, FAO. investments in infrastructure can help. Paper UNEP. 2006. The state of the marine References prepared for the IFPRI project “Evaluating environment: trends and processes. The the long-term impact of gender-focused Hague, United Nations Environment Anseeuw, W., Alden Wily, L., Cotula, L. & policy interventions”. Cited in FAO (2011). Programme. Taylor, M. 2012. Land rights and the rush Gaddis, E., Glennie, P.R., Huang, Y. & UNEP. 2012. GEO-5 global environment for land. Findings of the Global Commercial Rast, W. 2012. Water. In United Nations outlook: environment for the future we Pressures on Land Research Project. Rome, Environment Programme, GEO-5 global want. Nairobi, United Nations Environment International Land Coalition. environment outlook: environment for the Programme. u

Unasylva 241, Vol. 64, 2013/2 23 FAO/S. MAINA Agroforestry for food and nutritional security

R. Jamnadass, F. Place, E. Torquebiau, E. Malézieux, M. Iiyama, G.W. Sileshi, K. Kehlenbeck, E. Masters, S. McMullin and I.K. Dawson

More than 1.2 billion people groforestry is a set of approaches security. Many of the examples we present already practise agroforestry, to land management practised are from sub-Saharan Africa, where nine and continued adoption will by more than 1.2 billion people of the 20 nations with the highest burden improve global food security. Aworldwide involving the integration of of child undernutrition worldwide are trees with annual crop cultivation, live- located (Bryce et al., 2008). We discuss stock production and other farm activities. the challenges faced by agroforestry in Agroforestry systems range from open supporting food and nutritional security, parkland assemblages to dense imitations and we canvass opportunities to overcome of tropical rainforests such as homegar- these challenges. dens, to planted mixtures of only a few Ramni Jamnadass, Frank Place, species. These systems can increase farm Miyuki Iiyama, Gudeta Sileshi, productivity when their various compo- Katja Kehlenbeck, Eliot Masters, Stepha McMullin and Ian Dawson are at nents occupy complementary niches and Agroforesters in Kigoma, the United the World Agroforestry Centre (ICRAF), the associations between them are managed Republic of Tanzania, tend crops Nairobi, Kenya. Emmanuel Torquebiau effectively (Steffan-Dewenter et al., 2007). established as part of an FAO project and Eric Malézieux are at Agricultural to strengthen forest management Research and Development (CIRAD), In this article we assess the role of agro- and its contribution to sustainable Montpellier, France. forestry in supporting food and nutritional development, land use and livelihoods

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THE BENEFITS OF AGROFORESTRY wooded lands, which are often richer in SYSTEMS FOR FOOD AND micronutrients, fibre and protein than staple 1 NUTRITIONAL SECURITY crops (Malézieux, 2013). Traditionally, Developing domestic markets Agroforestry for food production such foods have been harvested in forests for tree foods in Solving the problem of food and nutritional and woodlands, but the availability of these sub-Saharan Africa security requires a range of intercon- resources is declining due to deforestation nected agricultural approaches, including and forest degradation (FAO, 2010), and Exotic and indigenous fruits cultivated improvements in the productivity of staple cultivation could provide an alternative and managed in agroforestry systems crops, the biofortification of staple foods, resource. The yield and quality of pro- are important in Africa. In Kenya, for and the cultivation of a wider variety of duction can be increased through genetic example, a 2004 survey found that over edible plants that provide fruits, nuts and improvement and on-farm management, 90 percent of the more than 900 house- vegetables for more diverse diets (Frison, making planting a potentially attractive holds surveyed grew fruits, with at least Cherfas and Hodgkin, 2011). There is huge option for growers. A combination of indig- one-quarter growing avocado (Persea potential for the diversification of crop pro- enous and exotic tree foods in agroforestry americana) and mango (Mangifera duction in the great range of lesser-used systems supports nutrition, the stability of indica). Over two-thirds of households indigenous foods found in forests and other production, and farmer income (Box 1). that reported fruit production harvested at least four fruit species, while over half sold some fruit. Nevertheless, the average consumption of fruit and vegetables in sub-Saharan Africa is significantly lower than the minimum recommended daily intake of 400 g per person. One reason for this is that poor households that have to buy food understandably focus on the purchase of staples such as maize and rice that provide relatively cheap sources of carbohydrate to meet basic energy needs, leaving only a small fraction of the family budget to spend on other, potentially more nutritious foods. Expenditure analysis shows, however, that as incomes increase, the purchase of fruit also increases. Domestic markets for fruit are predicted to grow in sub-Saharan Africa by about 5 percent per year over the next ten years. If production and delivery to consumers can be made more efficient, the potential is high for farmers to boost their incomes by meeting this demand.

Source: adapted from Jamnadass et al., 2011

A smallholder farmer harvests fruit from one of the trees he has planted near his homestead. Fruit consumption in sub-Saharan Africa is often below the recommended daily minimum, but homegardens and other agroforestry configurations can increase fruit consumption as well as

FAO/A. CONTI income for smallholders

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Maize grows under farmer-managed faidherbia natural regeneration ICRAF

As well as directly providing edible systems can also provide significant (from cacao, Theobroma cacao) and tea products, trees in agroforestry systems benefits for staple crop yields. Farmer- (primarily from Camellia sinensis). Each support food production by giving shade managed natural regeneration of faidherbia of these tree crops is grown to a significant and support to nutritious vegetable crops (Faidherbia albida) and other leguminous extent by smallholders; in Indonesia in (Maliki et al., 2012; Susila et al., 2012). trees in dryland agroforests (parklands) 2011, for example, the contribution of small Many tree species also assist staple crops in semi-arid and subhumid Africa, for farms to the country’s total production area through soil-fertility improvement. This example, has been encouraged in Niger was estimated at 42 percent for , was demonstrated in an analysis of more since 1985 by a policy shift that awarded 96 percent for coffee, 85 percent for rub- than 90 peer-reviewed studies on the tree tenure to farmers; it has led to the ber, 94 percent for cocoa and 46 percent planting of nitrogen-fixing green fertil- “re-greening” of approximately 5 mil- for tea (Government of Indonesia, 2013). izers, including trees and shrubs, which lion hectares (Sendzimir, Reij and Globally, the annual export value of these found consistent evidence of benefits to Magnuszewski, 2011). Farmer-managed five commodities combined is tens of bil- maize yields in Africa, although the level natural regeneration in the Sahel has led lions of United States dollars (FAO, 2013a) of response varied by soil type and the to improvements in sorghum and millet and there are opportunities to bring new technology used (Sileshi et al., 2008). yields, and positive relationships have been tree commodities into cultivation (Box 2). As well as increasing average yields, the observed with dietary diversity and house- Less clear is the proportion of commodity planting of trees as green fertilizers in hold income (Place and Binam, 2013). export value that accrues to smallholder southern Africa is able to stabilize crop cultivators, but production often consti- production in drought years and improve Agroforestry for incomes to support tutes a considerable proportion of farm the efficiency with which crops use rain- access to food takings and is used to support household water (Sileshi et al., 2011; Sileshi, Debusho Market data on tree products derived from food purchases. and Akinnifesi, 2012). This is important agroforestry systems are sparse, but infor- There is a danger that the planting of for food security in the context of climate mation on export value is quantified for commodities will result in the conver- change, which is increasing the incidence tree commodity crops such as palm oil sion of natural forest – which contains of drought in southern Africa. (derived from oil palm, Elaeis guineensis), important local foods – to agricultural Supporting the regeneration of natural coffee (primarily from Coffea arabica), land, and a risk that food crops will be tree and shrub vegetation in agroforestry rubber (from Hevea brasiliensis), cocoa displaced from farmland in a trend towards

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the growing of large areas of monocultural by combining tree commodities in diverse Agroforestry, fuel and food crops (e.g. oil palm; Danielsen et al., 2009). production systems with locally important Woodfuel, mostly comprising firewood Monocultures also reduce resilience to food trees, staple crops, vegetables and and , is crucial for the survival shocks such as droughts, floods and, edible fungi (Jagoret, Michel-Dounias and well-being of perhaps 2 billion people, often, the outbreak of pests and diseases. and Malézieux, 2011; Jagoret et al., 2012; enabling them to cook food to make it pal- In addition, buying food using the income Sustainable Cocoa Initiative, 2013) that atable and safe for consumption (FAO, received from a single commodity crop can increase or at least do not decrease com- 2008). In sub-Saharan Africa, the use of lead to food insecurity for farm households modity yields and profitability (Clough woodfuel is still increasing rapidly; the when payments are one-off, delayed or et al., 2009). Such systems have often been charcoal industry there was worth about unpredictable in value. practised traditionally and are now encour- US$8 billion in 2007 (World Bank, 2011). Mixed agroforestry regimes – such as aged by some international purchasers of The firewood and charcoal industries are shade-coffee and shade-cocoa systems – tree commodity crops through certification important for food and nutritional security can help avoid many such negative effects and other schemes (Millard, 2011). because they produce energy and generate

2 Integrating markets and cultivation: the case of allanblackia

The seeds of allanblackia (Allanblackia spp.), found wild in the humid forests of central, eastern and western Africa, yield an edible oil with a potential global market of more than 100 000 tonnes annually, especially as a “hardstock” for the production of healthy margarines that are low in trans-fats. A private–public partnership known as Novella Africa is developing a sustainable allanblackia oil business that could be worth hundreds of millions of United States dollars annually to local farmers. Supply chains for seed have been established in Ghana, Nigeria and the United Republic of Tanzania based on harvesting by local communities in natural forests and from trees remaining in farmland after forest clearance. Volumes are currently small (in the hundreds of tonnes) and oil is being exported for food product development. At the same time, more allanblackia trees are being brought into cultivation by improving seed- handling, developing vegetative propagation methods and selecting superior genotypes. Tens of thousands of seedlings and clones have been distributed to smallholders. The integration of allanblackia into small- scale cocoa farms is being promoted to support more biodiverse and resilient agricultural landscapes. As allanblackia trees grow, cocoa trees provide the shade they need; when they have grown, they in turn will act as shade for cocoa. Cocoa and allanblackia provide harvests at different times of the year, and when the allanblackia trees have matured they will help diversify farmer incomes and distribute them throughout the year.

ICRAF Source: adapted from Jamnadass et al., 2010 Women sort allanblackia seeds for sale in the United Republic of Tanzania

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income; their importance is likely to their farms – by payments for ecosystem species), laws to control germplasm flows remain high for some time, despite efforts services (Roshetko, Lasco and Delos internationally have also slowed small- to promote “more modern” energy sources. Angeles, 2007). holder access to appropriate planting In poor households, firewood and Appropriate combinations of crops, ani- material by, for example, limiting the charcoal are often burnt in open fires mals and trees in agroforestry systems can transfer to Africa of superior cultivars of or on poorly functioning stoves, with not only increase farm yields, they can fruit trees developed in other countries, in substantial emissions of pollutants that promote ecological and social resilience to this case notably in Asia. damage human health and may lead to the change because the various components of Third, many policy environments do not premature deaths of more than 1 million such systems, and the interactions between recognize agroforestry as an attractive people annually worldwide, the majority of them, will respond in differing ways to dis- investment in agriculture. For example, them women (Bailis, Ezzati and Kammen, turbances (Steffan-Dewenter et al., 2007). governments often subsidize the provi- 2005; see article by Stoukal et al. in this A diversity of species and functions within sion of artificial fertilizers to increase edition). Fuel quality depends on the tree integrated production systems is therefore staple crop yields, which discourages the species being burnt; poor families may a risk-reduction strategy, and agroforestry adoption of improved tree-based fallow be forced to use species that were tradi- can make important contributions to both technologies that could ultimately increase tionally avoided because of their harmful adaptation to, and the mitigation of, climate crop production more cost-effectively smoke or that were maintained for other change (Thorlakson and Neufeldt, 2012). and sustainably. Another problem is the products, such as fruit (Brouwer, Hoorweg lack of attention given to tree products and van Liere, 1997). CHALLENGES FOR AGROFORESTRY and services in data collection on farmer Reduced access and increased prices have IN SUPPORTING FOOD AND livelihoods and therefore the lack of prop- led to initiatives to promote the cultivation NUTRITIONAL SECURITY erly quantified information on the value of woodfuel-producing tree species in Policy constraints of trees grown in agroforestry systems in agroforestry systems. Where agroforestry Place et al. (2012) identified three key supporting food and nutritional security is practised by smallholders, less woodfuel policy areas in which constraints need (FAO, 2013b). needs to be purchased by them, there is less to be overcome for agroforestry to play a reliance on collecting from natural stands, greater role in food and nutritional security. Constraints in delivering tree and less time is involved in collection. This First, farmers need secure land and tree products to markets leaves more time for income-generating tenure. Where these are absent or con- For many tree products, markets are activities, especially for women, who are tested, farmer involvement in tree-planting poorly structured and lack coordination usually the major firewood collectors and management can be limited, but when (Roshetko et al., 2007). This results in low (Thorlakson and Neufeldt, 2012). Access they are assured, greater interest in agro- and unstable returns to farmers and high to cooking-fuel provides people with more forestry is stimulated. Land-tenure rights prices for buyers of tree foods, which limits flexibility in what they eat, including foods are particularly important for agroforestry access and consumption. Problems often with better nutritional profiles that require compared with other agricultural practices cited by producers include the absence of more energy to cook. The cultivation of because of the relatively long period that a collective bargaining system, poor trans- woodlots allows the production of wood may be required to realize benefits from port infrastructure, and the involvement of that is less harmful when burnt and has managing and cultivating trees. multiple intermediaries in the supply chain, higher energy content. Second, policies that determine how all of which act to reduce farm prices. For farmers obtain seeds, seedlings and clones perishable goods such as fruit, such barriers Agroforestry, ecosystem services, of a wide range of tree species suitable for also lead to high wastage along the supply climate change and food their various purposes are crucial (Lillesø chain and a failure to meet quality grades. Trees in agroforestry systems provide et al., 2011). Current policies often slow Prevailing low returns mean that farmers important ecosystem services, includ- the adoption of agroforestry: for example, struggle to afford inputs to improve their ing soil, spring, stream and watershed providing extension services with funds to suboptimal farm management practices. protection, animal and plant biodiversity give free seeds to farmers discriminates Traders also face many problems, such as conservation, and against small-scale entrepreneurial seed poor roads, corrupt officials and the high and storage, all of which ultimately and seedling suppliers (as well as reduc- cost of collecting from geographically scat- improve food and nutritional security ing the perceived importance to growers tered producers (Jamnadass et al., 2011). (Garrity, 2004). Individual farmers can of the seeds). Although well-intentioned There has been underinvestment in the be encouraged to preserve and reinforce (e.g. to protect intellectual property and characterization of tree foods and the these functions – which extend beyond stop the introduction of potentially invasive development of new tree cultivars that

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References

Bailis, R., Ezzati, M. & Kammen, D.M. 2005. Mortality and greenhouse gas impacts of biomass and petroleum energy future in Africa. Science, 308: 98–103. Brouwer, I.D., Hoorweg, J.C. & van Liere, M.J. 1997. When households run out of fuel: responses of rural households to decreasing fuelwood availability, Ntcheu District, Malawi. World Development, 25: 255–266. Bryce, J., Coitinho, D., Darnton-Hill, I., Pelletier, D. & Pinstrup-Andersen, P. 2008. Maternal and child under-nutrition:

ICRAF effective action at national level. The Lancet, Fruits of safou (Dacryodes edulis), 371: 510–526. a species undergoing participatory domestication in Cameroon, show some and land, greater support for how farm- Clough, Y., Barkmann, J., Juhrbandt, J., of the genetic variation that can be ers obtain tree-planting material, and Kessler, M., Wanger, T.C., Anshary, A., exploited to improve production wider acknowledgement of agroforestry Buchori, D., Cicuzza, D., Darrasi, K., as an agricultural investment option. Dwi Putrak, D., Erasmil, S., Pitopang, have high yields and provide high-quality • Intensified research into tree domes- R., Schmidt, C., Schulze, C.H., Seidel, products under smallholder production tication to provide planting material D., Steffan-Danielsen, F., Beukema, H., conditions. Until recently, for example, appropriate for smallholders, and Burgess, N.D., Parish, F., Brühl, C.A., scientists largely ignored the great further assessment of the complemen- Donald, P.F., Murdiyarso, D., Phalan, B., potential for the genetic improvement of tarity and resilience of agroforestry Reijnders, L., Struebig, M. & Fitzherbert, indigenous fruit trees (Jamnadass et al., systems in the face of climate change E.B. 2009. Biofuel on forested 2011). Insufficient work is being done to and other agricultural production lands: double jeopardy for biodiversity and bring these indigenous species into cultiva- challenges. climate. Conservation Biology, 23: 348–358. tion in the tropics. Dewenter, I., Stenchly, K., Vidal, S., Weist, M., ACKNOWLEDGEMENTS Wielgoss, A.C. & Tscharntke, T. 2011. RECOMMENDATIONS This article is adapted from: Agroforestry, Combining high biodiversity with high yields To strengthen the important and potentially food and nutritional security, a back- in tropical agroforests. Proceedings of the crucial role of agroforestry in food and ground paper prepared for the International National Academy of Sciences of the USA, nutritional security, we recommend the Conference on Forests for Food Security 108: 8311–8316. following: and Nutrition by Ian Dawson, Frank Place, FAO. 2008. The state of food and agriculture. • Better quantification of the role of the Emmanuel Torqueblau, Eric Malézieux, Biofuels: prospects, risks and opportunities. products and services from trees grown Miyuki Iiyama, Gudeta Sileshi, Katja Rome. in agroforestry systems in supporting Kehlenbeck, Eliot Masters, Stepha FAO. 2010. Global forest resources assessment the food and nutritional security of the McMullin and Ramni Jamnadass. 2010. FAO Forestry Paper No. 163. Rome. rural poor, to allow more appropri- The authors thank Flordeliza Bassiag, FAO. 2013a. FAOSTAT. Website (available at: ate targeting of intervention options. Timo Beiermann, Marie-Eve Ciparisse, faostat.fao.org). Where possible, quantification should Jonathan Cornelius, Zakayo Kimuge, FAO. 2013b. Advancing agroforestry on the be done separately for men, women Roger Leakey, Gunasingham Mikunthan, policy agenda: a guide for decision-makers. and children, small-scale farmers, the Henry Neufeldt, Sisay Nune, Jimena Agroforestry Working Paper No.1. Rome. landless poor and local traders. Rábago-Aguilar, Benjamin De Ridder, Frison, E.A., Cherfas, J. & Hodgkin, T. • Specific policies for the development of Jim Roshetko, Noemi Stadler-Kaulich, 2011. Agricultural biodiversity is essential agroforestry, including more attention Jennifer Schulz, Hesti Tata and Barbara for a sustainable improvement in food and to ensuring smallholder tenure of trees Vinceti for their inputs. u nutrition security. Sustainability, 3: 238–253.

Unasylva 241, Vol. 64, 2013/2 29

Garrity, D.P. 2004. Agroforestry and the by smallholders. Outlook on Agriculture, cropping systems in Southern Africa? achievement of the Millennium Development 41: 171–178. Agronomy Journal, 104: 1392–1398. Goals. Agroforestry Systems, 61: 5–17. Millard, E. 2011. Incorporating agroforestry Sileshi, G., Akinnifesi, F.K., Ajayi, O.C. & Government of Indonesia. 2013. Website approaches into commodity value chains. Place, F. 2008. Meta-analysis of maize yield (available at: http://ditjenbun.deptan.go.id/ Environmental Management, 48: 365–377. response to planted fallow and green manure cigraph/index.php/viewstat/komoditiutama). Place, F., Ajayi, O.C., Torquebiau, E., legumes in sub-Saharan Africa. Plant and Jagoret, P., Michel-Dounias, I. & Malézieux, Detlefsen, G., Gauthier, M. & Buttoud, G. Soil, 307: 1–19. E. 2011. Long-term dynamics of cocoa 2012. Improved policies for facilitating the Steffan-Dewenter, I., Kessler, M., Barkmann, agroforests: a case study in central Cameroon. adoption of agroforestry. In M. Kaonga, ed. J., Bos, M.M., Buchori, D., Erasmi, Agroforestry Systems, 81: 267–278. Agroforestry for biodiversity and ecosystem S., Faust, H., Gerold, G., Glenk, K., Jagoret, P., Michel-Dounias, I., Snoeck, D., services: science and practice, pp. 113–128. Gradstein, S.R., Guhardja, E., Harteveld, Todem Ngnogué, H. & Malézieux, E. Rijeka, Croatia, InTech. M., Hertel, D., Höhn, P., Kappas, M., 2012. of savannah with cocoa Place, F. & Binam, J.N. 2013. Economic Köhler, S., Leuschner, C., Maertens, agroforestry systems: a small-farm innovation impacts of farmer managed natural M., Marggraf, R., Migge-Kleian, S., in central Cameroon. Agroforestry Systems, regeneration in the Sahel. End of project Mogea, J., Pitopang, R., Schaefer, M., 86: 493–504. technical report for the Free University Schwarze, S., Sporn, S.G., Steingrebe, Jamnadass, R., Dawson, I.K., Anegbeh, P., Amsterdam and IFAD. Nairobi, World A., Tjitrosoedirdjo, S., Tjitrosoemito, Asaah, E., Atangana, A., Cordeiro, N., Agroforestry Centre. S., Twele, A., Weber, R., Woltmann, L., Hendrickx, H., Henneh, S., Ac Kadu, C., Roshetko, J.M., Lasco, R.D. & Delos Angeles, Zeller, M. & Tscharntke, T. 2007. Tradeoffs Kattah, C., Misbah, M., Muchugi, A., M.S. 2007. Smallholder agroforestry between income, biodiversity, and ecosystem Munjuga, M., Mwaura, L., Ndangalasi, systems for carbon storage. Mitigation and functioning during tropical rainforest H.J., Sirito Njau, C., Kofi Nyame, S., Adaptation Strategies for Global Change, conversion and agroforestry intensification. Ofori, D., Peprah, T., Russell, J., Rutatina, 12: 219–242. Proceedings of the National Academy of F., Sawe, C., Schmidt, L., Tchoundjeu, Z. Roshetko, J.M., Nugraha, E., Tukan, J.C.M., Sciences of the USA, 104: 4973–4978. & Simons, T. 2010. Allanblackia, a new tree Manurung, G., Fay, C. & van Noordwijk, Stloukal, L., Holding, C., Kaaria, S., crop in Africa for the global food industry: M. 2007. Agroforestry for livelihood Guarascio, F. & Gunewardena, N. 2013. market development, smallholder cultivation enhancement and enterprise development. In Forests, food security and gender. Unasylva, and biodiversity management. Forests, Trees S. Djoeroemana, B. Myers, J. Russell-Smith, 241: 37–45. and Livelihoods, 19: 251–268. M. Blyth & I.E.T. Salean, eds. Integrated Susila, A.D., Purwoko, B.S., Roshetko, J.M., Jamnadass, R.H., Dawson, I.K., Franzel, S., rural development in East Nusa Tenggara, Palada, M.C., Kartika, J.G., Dahlia, L., Leakey, R.R.B., Mithöfer, D., Akinnifesi, Indonesia. Proceedings of a workshop Wijaya, K., Rahmanulloh, A., Mahmud, F.K. & Tchoundjeu, Z. 2011. Improving to identify sustainable rural livelihoods, R., Koesoemaningtyas, T., Puspitawati, livelihoods and nutrition in sub-Saharan Kupang, Indonesia, 5 to 7 April 2006, pp. H., Prasetyo, T., Budidarsono, S., Africa through the promotion of indigenous 137–148. ACIAR Proceedings No. 126. Kurniawan, I., Reyes, M., Suthumchai, and exotic fruit production in smallholders’ Canberra, Australian Centre for International W., Kunta, K. & Sombatpanit, S. eds. agroforestry systems: a review. International Agricultural Research. 2012. Vegetable–agroforestry systems in Forest Review, 13: 338–354. Sendzimir, J., Reij, C.P. & Magnuszewski, P. Indonesia. Bangkok, World Association of Lillesø, J-P.B., Graudal, L., Moestrup, S., 2011. Rebuilding resilience in the Sahel: Soil and Water Conservation and Nairobi, Kjær, E.D., Kindt, R., Mbora, A., regreening in the Maradi and Zinder regions World Agroforestry Centre. Dawson, I., Muriuki, J., Ræbild, A. & of Niger. Ecology and Society, 16 (online) Sustainable Cocoa Initiative. 2013. Website Jamnadass, R. 2011. Innovation in input (available at: www.ecologyandsociety.org/ (available at: http://cocoasustainability.com/). supply systems in smallholder agroforestry: vol16/iss3/art1/). Thorlakson, T. & Neufeldt, H. 2012. Reducing seed sources, supply chains and support Sileshi, G.W., Akinnifesi, F.K., Ajayi, O.C. & subsistence farmers’ vulnerability to climate systems. Agroforestry Systems, 83: 347–359. Muys, B. 2011. Integration of legume trees change: evaluating the potential contributions Malézieux, E. 2013. Editorial. Underutilized in maize-based cropping systems improves of agroforestry in western Kenya. Agriculture fruit trees in Africa. Special issue. Revue rain-use efficiency and yield stability under & Food Security, 1: 15 (online) (available Fruits (in press). rain-fed agriculture. Agricultural Water at: www.agricultureandfoodsecurity.com/ Maliki, R., Cornet, D., Floquet, A. & Management, 98: 1364–1372. content/1/1/15). Sinsin, B. 2012. Agronomic and economic Sileshi, G.W., Debusho, L.K. & Akinnifesi, World Bank. 2011. Wood-based biomass performance of yam-based systems with F.K. 2012. Can integration of legume trees energy development for sub-Saharan Africa: shrubby and herbaceous legumes adapted increase yield stability in rainfed maize issues and approaches. Washington, DC. u

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Urbanization and The contribution of forests to the gross the middle of the century (United Nations domestic products of “non-forest” West Population Division, 2008). An urbanization forest foods in Benin African countries such as Benin is usually process is under way in Benin. This article considered to be very low, but this notion reviews the implications of that process for does not hold up to scrutiny. Many plant Benin’s forest sector and especially for the A. Bertrand, G.A. Agbahungba and animal forest products are used as role of forests in the provision of food. and S. Fandohan foodstuffs in Benin – but they often do not appear in national accounts because they Rapid urban development in Urbanization is driving demand are harvested and traded informally, either West Africa for forest foods, but a stronger illegal or semi-illegally. Figure 1 shows that, worldwide, the regulatory environment is Worldwide, the urban population is urbanization process is most dramatic in needed if this growing sector is expected to grow by over 3 billion people to less-developed countries. Sub-Saharan to be sustainable. 2050, primarily in less-developed countries, Africa has a large rural population and an with the result that over 70 percent of the emerging trend of urbanization. Figure 2 world’s population will be living in cities by shows the proportions of the total populations

A man displays the skin of an African rock python (Python sebae) on a rural road in Benin. Snake – caught wild or bred in captivity – is becoming a popular food in urbanizing Benin © Alain Bertrand is a forestry consultant in AGBAHUNGBA G.A. Tanger, Morocco, Georges A. Agbahunbga is an independent consultant in environment and development and professor at CIPMA, Cotonou, Benin, and Sylvestre Fandohan is the director of ProCGRN/GIZ, Cotonou, Benin.

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1 Urban and rural population 6 growth in developed and less-developed countries, 5 1950–2050 ) 4

in Francophone African countries that are 3 urban. Almost half (45 percent) of Benin’s population is urbanized, although Cotonou 2 (the country’s largest city) ranks only sixteenth Population (billions in size among West Africa’s urban areas. 1 The trend of rapid urbanization is also strong 0 in many of Benin’s neighbours, including

Nigeria, where about 50 percent of the 1950 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020 2025 2030 2035 2040 2045 2050 country’s 175 million people (Government of Urban population in less developed regions United States of America, 2013) is urbanized. Urban population in more developed regions Rural population in less developed regions Effects of urbanization Rural population in more developed regions on forests Source: United Nations Population Division, 2008 Urbanization implies a shift in lifestyles and diet patterns, and food acquisition becomes a matter of monetary economics. In the rural % areas of Benin, however, on-farm consump- 100 tion and subsistence farming still prevail. By creating market demand, urbanization can 90 revitalize the production and distribution of forest food products. It can also lead to social 80 diversification as new citydwellers act as distributors and consumers of these products. 70 An influx of urban consumers creates new

markets that can be exploited by dynamic 60 rural producers, enabling them to diversify their production and meet the demand for 50 multiple and increasingly processed forest products. Rural entrepreneurs have oppor- 40 tunities to market new products and activities that may previously have been restricted to 30 their family circles (Codjia, Assogbadjo and Mensah Ekué, 2003). Table 1 shows that, in 20 2008 (the latest year for which such data are available), a range of forest products were economically significant in Benin. 10 Some forest products that were once second- i l

0 r

ary, such as cashew and shea, have become e ogo Mali

major agricultural products for export (Gnimadi, T Niger Cha d Benin Congo Gabon Guine a Burund Rwanda 2008). Supply chains with no legal status, Senega Mauritania Cameroon

such as those supplying small bushmeat, are Madagasca Côte d’Ivoir of the Congo Burkina Faso now common and can no longer be ignored. African Republic Democratic Republic

2 Central Percentage urban of total population, Source: Government of United States of America, 2013 countries of Francophone Africa

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TABLE 1. Contribution of forests and trees to GDP in Benin, 2008 This is a major issue in forest policy. Also Product Notes Estimated total significant is woodfuel, a that annual value added (million FCFA) is used daily in most Benin households. Cashew (Anacardium occidentale) Export 53 000 Table 2 shows that, combined, plant and Bushmeat (various species) 28 000 animal forest and tree products used as Woodfuel Charcoal 27 886 food account for almost 35 percent of the Breadfruit (Artocarpus altilis) 12 430 forest sector’s value added, second only to Shea (Vitellaria paradoxa) Butter consumed in Benin 6 466 exported forest products and considerably Timber (natural forests) 2 923 more than woodfuel. The income derived Timber (, Tectona grandis) Export 2 753 from plant and animal forest products used Shea Almonds for export 2 237 for food represents over 54 percent of Woodcraft 1 898 income generated in rural areas by Benin’s Woodfuel Firewood 1 517 forest sector. Toothbrushes 1 404 This finding confirms the major part played Honey 1 281 by forests in people’s food security (Kadevi, Cashew National consumption 980 2001). Forests should no longer be considered Néré (Parkia biglobosa) 361 primarily for their wood-producing functions Palmyra palm (Borassus spp.) 293 (woodfuel, timber and service wood), but also Live reptiles 127 for their essential contributions to feeding Medicinal plants 109 communities, particularly disadvantaged Non-conventional farming 86 groups (Lebel, 2003). Such recognition will Irvingia spp. Fruit 54 require a profound shift in forest policy. Forest Mushrooms 43 food products and supply chains can add to Timber (teak) National consumption 31 forest productivity without diminishing existing Snails (Achatina achatina) 23 subsectors of the forest industry dealing with Baobab (Adansonia digitata) 21 wood and wood products (Assogba, 2007). Irvingia spp. Almonds 21 Service wood 15 Revenues stay within the rural Shea Butter for export 8 context Total forestry/trees on farms 143 967 Plant food products account for about half of GDP Benin, 2003–2005 2 169 000 rural forest incomes, followed by woodfuel Share of forestry in GDP (approx.) 6.6% and animal food products. Rural people con- Source: Bertrand, Agbahungba and Tonou, 2009 stantly seek alternative sources of revenue to complement their income from farming and livestock, and these alternatives often vary TABLE 2. Relative share of forest subsectors in GDP, Benin, 2008 according to the comparative advantages of Forest product group Forest product Annual Percentage value added of total particular areas (and thus certain activities (million FCFA) forest sector may become locally widespread). A little over Woodfuel Firewood, charcoal 29 403 20 one-third of revenues derived from forest Plant forest products Breadfruit, shea, honey, cashew, 21 950 15 products are retained in rural areas. used as food in Benin néré, palmyra palm, Irvingia spp. (fruit and almonds), mushrooms, baobab fruit Development of forest product chains Animal forest products Bushmeat, snails, non-conventional 28 109 19 Urban sprawl induces major social and used as food farming (agoutis, reptiles, etc.) economic changes in and around cities Export products Cashew, teakwood, shea (almonds 58 124 40 throughout the hinterland. In Benin, Cotonou’s and butter) hinterland extends across the entire national Wood products for use Timber (natural forests, teak), 4 867 3 in Benin service wood, craftwood territory and beyond the national borders into the Niger, Nigeria and Togo. Forest health products Medicinal plants, toothbrushes 1 513 1 Forest-food supply chains are developed in Total, forest sector 143 966 100* both formal and informal – including illegal – Source: Bertrand, Agbahungba and Tonou, 2009 * Does not tally to 100 due to rounding. ways (Igué, 1983). Those based on on-farm

Unasylva 241, Vol. 64, 2013/2 Unasylva 213, Vol. 55, 2003 33 G.A. AGBAHUNGBA © A man sets out baobab fruit for sale on a roadside in Benin. With increasing consumption (e.g. fruit such as Irvingia expand the spatial and sociological coverage urbanization, new enterprises are spp. and Saba senegalensis), conventional of traditional-food consumption. For example, helping to promote the remarkable rural trade (e.g. “miritchi” or palmyra palm sprouts of the palmyra palm essentially nutritional benefits of this food sprouts – Gschladt, 1972), traditional medici- cultivated in backyards in the north of Benin nal plants and snail-breeding are informal. (e.g. Collines, Atacora and Alibori depart- increasing number of neighbourhood con- Given their informality, obtaining economic ments) and the south of the Niger are now venience stores in Cotonou. Baobab juice is data on them, such as the volume and value transported all the way to Cotonou, where also served at coffee breaks and in cocktails. of outputs and the size of the workforce, is they are cooked (by boiling) for consumption. Other conventional sectors, such as difficult, and it is especially challenging in Therefore, consumption extends to urban beekeeping, are being upgraded with the the case of illegal value chains. areas and reaches new consumer groups. adoption of more efficient techniques to The baobab fruit is used as a supplemen- expand production and markets. The development, upgrading and tary food for infants in rural areas. With expansion of traditional chains urbanization, new enterprises are helping Small bushmeat, a major illegal Many neo-citydwellers feel nostalgic for to promote the remarkable nutritional benefits segment rural life after their urban migration, and this of this food. In Cotonou, some small-scale The term “small bushmeat” refers to products sense of nostalgia is fostering the spread of enterprises offer powdered infant formulas, derived from small-sized animals collected traditional foods into urban markets. In the while others sell energy drinks in pasteurized traditionally in the wild for food use. It past, such foods were restricted to market bottles. These enterprises have developed encompasses diverse species of birds, snails, villages in production areas (Delvaux and both innovative technologies and new rodents (such as grasscutters, Thryonomys Sinsin, 2003); thus, urbanization tends to products, which are marketed through an swinderianus, also known as cane rats),

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reptiles, amphibians, insects, shellfish and Urban migration and new citydwellers have 200 000 heads per year, equivalent to approx- molluscs (Sinsin and Sinadouwirou, 2003). extended the small-bushmeat market, and imately 500 tonnes of meat (Igué, 1991). The harvesting, sale and consumption of multiple supply channels have adapted to Although hunting supplies the majority of small bushmeat is illegal in Benin, but all combinations of resources (e.g. various grasscutters, Benin has been a pioneer in most Cotonou restaurants and food stalls wildlife species and geographical locations) grasscutter farming since 1985 (Kamoyedji, sell ready-cooked small-bushmeat dishes. and demand (e.g. short supply chains, cured 1999), and captive-breeding techniques were Although the consumption of small bushmeat meat and restaurants). developed several decades ago (Mensah, is widespread, the supply chain has no 2003). Grasscutter meat is marketed at legal status. It is not studied, documented, New production segments: sales points spread throughout urban areas. controlled, guided or administered by the grasscutter, reptile and Mensah (2006) underscored the lack of indus- official forestry authority. snail farming trial processing facilities, however. The small-bushmeat market, invisible New production modes based on small For other wild species, such as porcupines, but pervasive and known to all, thrives bushmeat are developing to meet urban the domestication process (especially the illegally, the result of centuries-old bans, demand. Specialized breeding farms have challenge of captive breeding) is ongoing. complacency and deficiencies in state been created with significant funding and Sales of reptiles are increasing rapidly – control. Since colonial times, Benin’s for- sophisticated technologies. not only farmed crocodiles (for both leather est authority has fought small-scale rural Grasscutter meat is highly prized and and meat) but also native snake species customary hunting. Repeated bans have popular in both urban and rural areas encouraged poaching and reinforced the (Sodjinou and Mensah, 2005). Rising Baskets of achatina snails are ready symbolic value of bushmeat consumption. demand exceeds supply, estimated at about for sale in a market in Cotonou, Benin © G.A. AGBAHUNGBA G.A.

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for meat production and live export. With involving rural communities (Bertrand et al., et mondialisations: les mutations urbanization, customary bans prohibiting 2006). There is an urgent need for a new legal des politiques forestières en Afrique consumption among ethnic groups are and administrative framework that promotes francophone et à Madagascar. Paris, disappearing, and the sale and consumption the sustainable management of the forest CIRAD, L’Harmattan éditeur. of snake meat is becoming commonplace resource, including the food products now in Codjia, J.T.C., Assogbadjo, A.E. & Mensah (Toudonou, Mensah and Sinsin, 2004). such high demand, and the domestication of Ekué, M.R. 2003. Diversité et valorisation The consumption of achatina snails certain bushmeat species. au niveau local des ressources végétales (Achatina achatina, also known as the giant The country cannot afford to overlook the forestières alimentaires du Bénin Cahiers Ghana snail) is also growing rapidly (Sodjinou, small-bushmeat industry and cannot continue d’études et de recherches francophones. Biaou and Codjia, 2003): snail skewers are to prohibit the industry if the ban remains Agricultures, 12(5): 321–331. popular at coffee breaks and cocktail events. unenforced. A top priority is to tackle issues Delvaux, C. & Sinsin, B. 2003. Gestion intégrée Snail farms can produce year-round, although surrounding the small-bushmeat industry des plantes médicinales dans la région des during the rainy season some sales come through the creation of local wildlife manage- Monts Kouffé. In N. Sokpon, B. Sinsin & from wild catches in southern Benin. The ment programmes and local regulation of O. Eyog-Matig, eds. Actes du IIè Séminaire supply chain is still limited largely to gathering hunting, with fiscal regulations applying to international sur l’Aménagement intégré des and rearing, but with rising demand, breeding the bushmeat supply chain. forêts naturelles des zones tropicales sèches farms are developing quickly. The annual The contribution of forest products to urban en Afrique de l’Ouest, Parakou, Bénin, supply of snails is estimated at 75.5 tonnes food supply should be viewed in the context 25–29 juin 2001, pp. 389–405. Cotonou, of meat, and the sale price is higher than that of food scarcity risks in large cities. What Benin, FSA. of fish, beef, sheep and kid goat. role can the rural, urban and peri-urban FAO. 1999. Document national de prospective: forest sectors play in nutrition and health? Bénin. Rome. Evolution of forest product This public-policy challenge requires much Gnimadi, A. 2008. Etude pour l’identification chains: domestication, more coordination between the forestry, des filières agroindustrielles prioritaires processing and marketing agriculture (food security) and health (nutri- (BENIN). No. de mission du consultant: Considerable change is being observed in tion) administrations. u TE/RAF/07/A01-1751-2008. forest-food supply chains in Benin today, Government of United States of America. driven largely by urban demand (Igué and 2013. The world fact book (available at: Puech, 2008): www.cia.gov/library/publications/the-world- • a transition from gathering to domes- factbook/). tication and farming (e.g. for palmyra Gschladt, W. 1972. Le Rônier au Dallol palm, mushrooms, snails, grasscutters, Maouri – Niger. Bois et Forêts des Tropiques, snakes and honey); 145, September–October. • the structuring of value chains, with References Igué, J.O. 1983. L’officiel, le parallèle et le well-defined marketing chains; clandestin: commerces et intégration en • the development of upstream process- Assogba, T. 2007. Evaluation de la diversité Afrique de l’Ouest. Politique Africaine ing activities between the production des arbres médicinaux épargnés dans No. 9. Paris. and marketing stages (e.g. for palmyra les terroirs agricoles et analyse de leurs Igué, J.O. 1991, Le commerce de l’aulacode palm, snails, grasscutters, Irvingia spp., circuits de commercialisation sur les et de sa viande au Bénin. Cotonou, Benin, néré and shea); grands marchés du Sud du Bénin. Cotonou, GTZ/PPEAu. • the diversification of sales and consump - Benin, FSA. Igué, J.O. & Puech, F. 2008. Plaidoyer pour la tion channels according to spatial and Bertrand, A., Agbahungba, G. & Tonou, P. structuration du secteur informel au Benin. sociological changes in the urban space. 2009. Contribution du secteur forestier à Cotonou, Benin, PASP Com. 2. l’économie du Bénin. Final report, volumes Kadevi, K. 2001. Statistiques sur les produits Conclusion 1, 2 & 3. Cotonou, Benin, Edenia Consult forestiers non ligneux (PFNL) dans Urbanization is inducing structural changes Tanja & Beged-Conseil. la République Togolaise. Programme in the demand for forest foods. The growing Bertrand, A., Montagne, P., Serre-Duhem, de partenariat CE-FAO (1998–2001). economic contribution of the forest sector in C. & Raharimaniraka, L. 2006. Nouvelles B7-6201/97-15/VIII/FOR/ROJET GCP/ Benin (FAO, 1999), and especially of forest politiques forestières et gestion économique INT/679/EC. Rome, FAO. foods, poses challenges for Benin’s forest publique des filières des produits forestiers Kamoyedji, I. 1999. Impact de l’élevage des administration in redefining public forest non ligneux. In A. Bertrand, P. Montagne aulacodes sur les revenus des éleveurs: cas policy through a participatory approach & A. Karsenty, eds. Forêts tropicales de la commune d’Abomey-Calavi. Mémoire

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présenté pour l’obtention du Diplôme de Sinsin, B. & Sinadouwirou, T. 2003. Toudonou, A.S.C., Mensah, G.A. & Sinsin, B. Formation Supérieure, Planification Valorisation socio-économique et pérennité 2004. Le serpent: une nouvelle ressource Régionale et Aménagement du Territoire, du Pentadesma butyracea Sabine en galeries alimentaire dans les départements du centre DFS/PRAT, Ouagadougou. forestières au Bénin Cahiers d’études et de et du sud du Bénin. Bulletin of Agricultural Lebel, F. 2003. L’importance des produits recherches francophones. Agricultures, Research of Benin, 45. forestiers non ligneux pour les ménages 12(2): 75–79. United Nations Population Division. 2008. An agricoles de la région de Thiès, Sénégal. Sodjinou, E., Biaou, G. & Codjia, J.T.C. 2003. overview of urbanization, internal migration, M.Sc. thesis. Québec, Canada, Université Commercialisation des escargots géants population distribution and development in de Laval. africains (achatines) dans les Départements the world. New York, USA. u Mensah, R.M.O.B.A.D-G. 2006. Contribution de l’atlantique et du littoral au Sud-Bénin. des institutions de micro finance au Annales des sciences agronomiques financement des exploitations aulacodicoles du Bénin. au Bénin: Cas du PADME. Mémoire de fin Sodjinou, E. & Mensah, G.A. 2005. Analyse d’études, ENEAM/UAC/Bénin. technico-économique de l’aulacodiculture Mensah, G.A. & Ekué, M-R.M. 2003. au Nord-Bénin: Déterminants d’adoption. L’essentiel en aulacodiculture. RéRE/ International Forum on Promoting Grass- KIT/IUCN/CBDD. République du Bénin/ cutter for Business in West Africa, Accra, Royaume des Pays-Bas. Ghana, December 2005.

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Forests, food security and gender

L. Stloukal, C. Holding, S. Kaaria, F. Guarascio and N. Gunewardena ZZARRI i FAO/G. B A woman and a girl harvest coffee beans in a homegarden in Lempira Sur, Forestry and agroforestry orests and trees on farms are a direct Guarita, Honduras. Women in developing systems are not gender-neutral. source of food, cash income and countries are frequently disadvantaged Empowering women could a range of subsistence benefits for in their access to economic opportunities in the forest sector create significant opportunities Fbillions of people worldwide, but there for greater food security in are major differences in the benefits developing countries. that accrue to women and men. Women • shoulder the burden of domestic and in developing countries are frequently childcare responsibilities; disadvantaged in their access to forests and • participate less in rural institutions, economic opportunities in the forest sector for example forest-user groups; because, compared with men, they usually: • face gender-differentiated behavioural • have lower levels of literacy, education, norms and social perceptions of wom- physical abilities and technical skills, en’s roles. less access to services such as exten- These disadvantages often result in sion and credit, greater constraints on gender disparities in, for example, access their time and mobility, and limited to and use of forest foods, woodfuel1 and Libor Stloukal, Susan Kaaria, Francesca access to markets and market-related fodder for livestock; forest management; Guarascio and Nandini Gunewardena information; 1 are in FAO’s Division of Gender, Equity and • face discrimination in conventional Woodfuel comprises unprocessed wood (firewood, Rural Employment, and Christine Holding called “fuelwood” here) and processed wood is in FAO’s Division of Forest Assessment, forest, tree and tree-product ownership products, such as charcoal and offcuts, Management and Conservation. regimes; used for fuel.

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and the marketing of forest and tree from these activities adds to the purchasing inputs. The review also showed that, in products. This article expands on some power of households and therefore their Africa, the extent of women’s involvement of these disparities and makes a case for food security. Men are more likely than relative to men in activities such as soil-fer- gender equity in increasing food security women to be responsible for collecting tility management, fodder production and and nutrition in poor rural communities. wild honey, birds’ eggs and insects, hunt- woodlot-growing is fairly high in terms of ing wild animals, and fishing (Shackleton the participation of female-headed house- GENDER DIMENSIONS OF THE et al., 2011; IFAD, 2008). In some places holds but low when measured by the area FOREST–FOOD SECURITY NEXUS (such as in parts of the Congo Basin and of land such households allocate to these Food from the forest the Peruvian Amazon), such activities pro- activities and the number of trees they Wan, Colfer and Powell (2011) demon- vide the primary sources of animal protein plant. In cases where women have low strated that the gender-based division of for rural people (FAO, 1992). involvement, this is due mostly to a scarcity agricultural labour and food production, of resources, especially land and labour combined with the fact that women often Agroforestry (partly because women tend to do more have fewer alternative income-earning There is evidence that agroforestry activi- household and care work than men), and to opportunities than men, means that women ties are often gender-differentiated: while differences in male and female opportunity tend to collect forest foods to supplement men are usually interested in trees (often sets. Some studies have also noted that, the nutrition of their households. Women of only one or two species) for commercial compared with men’s fields, women’s farm play a particularly important role in col- purposes, women are more inclined to plots tend to have a greater number of trees lecting and processing edible wild plants favour multipurpose trees of a number of and more species, possibly because women from forests, as well as in the preparation species for subsistence use, such as those like to have trees near the homestead as of household meals by using forest foods that provide food, fuelwood and fodder well as a diversity of species with which to cook (for example) soups, stews and rel- and help improve soil fertility. A review to maintain the health of their children ishes (Vinceti, Eyzaguirre and Johns, 2008; of 104 studies of gender and agroforestry and broaden the household food supply FAO, 2012). Women often have substantial in Africa (Kiptot and Franzel, 2011) con- (FAO, 1999). knowledge concerning the identification, firmed that women’s participation is very Tree tenure – the ownership and use collection and preparation of highly nutri- high in enterprises such as the production rights of trees – is often differentiated tious forest foods that can complement and and processing of indigenous fruit and along gender lines, and men usually have add flavour to the staples of family meals. vegetable products, apparently because overall authority over high-value tree In addition, income generated by women indigenous species require fewer labour products. However, the gendered nature of access to and control of trees, tree products and related resources is often highly com- Women and forest vegetables in East Usambara plex, depending on social and ecological conditions and factors such as landscape In the East Usambara Mountains in the northeast of the United Republic of Tanzania, niche, time, species, products and uses the consumption of traditional leafy vegetables is the best predictor of children’s overall (Rocheleau and Edmunds, 1997). In many micronutrient intake. The majority of leafy vegetables consumed in the area are wild- settings, women’s rights are substantial collected by women in fields, field margins, fallows and agroforests. Survey data show due to the informal (and often negotiable) that, in the wet season, 46 percent of children aged 2–5 years consume vegetables on nature of customary laws and, in some a daily basis, while in the dry season only 22 percent of children are able to do so. cases, the complementarity of women’s Proximity to the forest is a key determinant of vegetable consumption, particularly and men’s productive roles. Women’s in the dry season. Local women reported that those who were poor and lived far from rights, however, can easily become the forest had to spend a significant amount of time collecting vegetables. In addition, marginalized or may not be recognized, even though they had legal access rights, many women were hesitant about entering especially in the introduction of statutory reserved forests to collect vegetables for fear of being suspected of illegal activities or of laws and formal administrative procedures encountering others engaging in such activities (e.g. pit-sawing, mining and hunting). In at the local to central government level this setting, having areas with tree cover on the family farm and near the home supports (Quisumbing et al., 2001). year-round access to vegetables, with the potential to decrease women’s workloads and Although women often make significant improve the nutrition of their families. labour contributions to agroforestry (e.g. by planting, weeding and watering trees), Source: Powell, Hall and Johns (2012) their opportunities in the sector are often limited to low-return activities that are of

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A woman shows how to harvest mfumbwa leaves (Gnetum africanum), a popular wild food in central Africa, without destroying the plant. Women play an important role in collecting and processing edible wild plants from forests and preparing them for household meals

Rocheleau and Edmunds (1997) reported that, among the Akamba community of eastern Kenya, tree-planting and were primarily the domains of men, while women enjoyed use and access rights to fodder, fuelwood, fruits and mulch. Gender-differentiated rights and responsibilities in agroforestry are also an important determinant of the adoption of agroforestry technologies and the use of related services, and this differential uptake of technologies may (if other things remain the same) further perpetuate exist- ing gender inequalities.

Woodfuel and household energy Limited access to woodfuel – for example due to environmental degradation or local forest regulations – can cause households to change what they eat, potentially leading to malnutrition. Similarly, boiling water insufficiently to save fuel can contribute to the consumption of contaminated water and poorly prepared food, with potentially life-threatening consequences, especially for children, pregnant women, the mal- nourished and the sick. In many agrarian settings, women and girls have the primary responsibility for collecting fuelwood for household use and may have to walk for several hours, frequently in insecure conditions, to do so. In refugee and conflict situations,

FAO. G. NAPOLITANO G. FAO. women are particularly vulnerable to gender-based violence while collecting little or no interest to men, while men tend have the right to collect and use fruits but fuelwood (WFP, 2012). to control the production and marketing are restricted from harvesting high-value Shrinking access to fuelwood near the of high-value products as well as the use timber trees. On the other hand, species home – which is becoming a pressing of the income so generated (Rocheleau such as Sesbania sesban, which produces reality in many developing countries – and and Edmunds, 1997). Tree products such good fuelwood and can help improve soil the time taken to collect it often mean that as charcoal, logs, timber, large branches fertility, is considered a women’s tree, and women have less time for other activities and poles are typically considered male therefore women have the right to plant, (Wan, Colfer and Powell, 2011). Gbetnkom domains. Thus, in the Luo and Luhya manage and use it as they please (Franzel (2007) concluded that constraints on communities in western Kenya, women and Kiptot, 2012). women’s income-earning potential caused

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A woman carries fuelwood near Mbeya, the United Republic of Tanzania. Women and girls often have the primary responsibility for collecting fuelwood for household use and may have to walk for several hours, frequently in insecure conditions, to do so FAO/A. CONTI FAO/A.

by the scarcity of fuelwood may have With regard to the cooking environment, used for animal feed; they may be browsed significant impacts on household food the combustion of biomass (including directly by roaming livestock or collected security. The increased time spent gather- woodfuel) releases significant quantities and fed to livestock in stalls. It has been ing wood leaves less time for cash-earning of pollutants that damage the health of estimated, for example, that 75 percent of activities and for tasks to support the food those who do the cooking, the vast majority tree species in tropical Africa are used security and health of families, while of whom are women. Exposure to indoor as browse by domestic livestock such as the purchase of increasingly expensive smoke has been found to be responsible sheep, goats, cattle, camels and donkeys woodfuel leaves less money to buy food. for 39 percent of deaths due to chronic (FAO, 1991). Women (and children) Women are not always the main fuelwood pulmonary disease in women, compared play crucial roles in gathering animal collectors (Sunderland et al., 2012). For with 12 percent in men (Wan, Colfer and fodder (including from trees), feeding example, when the distances become too Powell, 2011; Rehfuess, 2006). Disease and grazing animals, cleaning animal great for fuelwood collection on foot, or and nutrition are linked: infections sheds, and composting animal waste. where there are naturally low densities of associated with wood-smoke exposure These activities contribute significantly fuelwood (e.g. in the Kalahari), men tend significantly increase women’s nutrient to domestic livestock production, which to assume the role of fuelwood collec- requirements (e.g. vitamin A), and those in turn influences milk and meat supply tion, making use of transportation such who are micronutrient-deficient are more and contributes to household income. as donkey carts and small trucks. Men likely to develop infections after exposure Tree-based fodder is also used to sustain are also the main collectors of woodfuel, to wood smoke. draught animals for ploughing and in the including charcoal, for sale (Zulu and production of manure – which increases Richardson, 2013). In Latin America, Fodder for livestock soil fertility and is used as cooking- men are overwhelmingly responsible for Many tree species found in forests, fuel (especially when woodfuel is in woodfuel collection. woodlands and parklands and on farms are short supply).

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Farmer Patricia Oduor and extension worker Gabriel Malowa chat in an agroforest in Siaya District, Kenya. Women and men often have highly specialized knowledge of forest flora and fauna, but it is not always acknowledged or used in modern systems FAO/C. DOWSETT FAO/C.

Forests and climate-change total amount of genetic diversity con- harvesting and hunting patterns, seasonal adaptation served and used, often working to counter availability, uses for various purposes, and Women may be more vulnerable than men decreases in biodiversity caused in part conservation practices. to the effects of climate change because by the favouring by men of cash-oriented Much of the existing literature, typically they are more likely to be poor and depen- monocultures (World Bank, FAO and based on case studies, paints a stylized dent on natural ecosystems threatened by IFAD, 2008). It follows that forest policies picture in which women derive their climate change (IPCC, 2007; Lambrou and programmes that aim to be socially knowledge from their specialized roles and Nelson, 2010). They are also effective responsive should take into account the in the collection and processing of forest actors and change agents for climate- gendered dimensions of resource use, products for direct household use and change mitigation and adaptation (Peach needs, access, knowledge and strategies limited sale in local markets, while men Brown, 2011). Women often have a strong for coping with climate change. tend to specialize in the harvesting of body of knowledge and expertise that can timber products and wild meat for cash be used in strategies for disaster reduc- GENDER DIFFERENCES IN income and marketing. However, the extent tion and climate-change mitigation and FOREST-RELATED KNOWLEDGE to which such findings can be general- adaptation. Moreover, women’s respon- Men’s forest-related knowledge is often ized is unclear. Data from 36 long-term sibility in households and communities regarded as knowledge that “counts”, studies of forest-proximate communities as stewards of forest foods and other and the knowledge held by women is in 25 countries in Africa, Asia and forest-related and tree-related resources not always properly recognized in forest Latin America, representing more than means they are well-placed to develop management plans and forest use. Both 8 000 households, confirm that women livelihood strategies adapted to changing women and men often have highly special- and men tend to collect different forest environmental conditions. As natural- ized knowledge of forest flora and fauna products (Sunderland, 2011). Contrary to resource managers, women influence the in terms of species diversity, location, conventional wisdom, however, the data

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show that both women and men collect importantly, are often able to decide how The gender roles in forestry value non-timber forest products (NTFPs, the income is used. Nevertheless, women’s chains are generally poorly understood which can include woodfuel) primarily participation in tree domestication has and not well supported by policy-makers for subsistence and that men’s sale share been hindered by limited access to and and service providers, especially those is generally higher than women’s, except control over land and trees, insufficient who focus on hi-tech operations or pay in Africa where the share is roughly equal information on the requirements and less attention to local markets. Gender- (Sunderland, 2011). This finding indicates advantages of tree domestication, and sensitive value-chain analyses can identify that while gender differences in forest- substantial periods of production inactivity less-visible gender-sensitive components at relevant knowledge exist (particularly due to their childbearing and childrear- various stages of value chains. These might about processing and marketing), they ing roles and their heavy workloads in include processing at home; informal may not be as clear as previously thought, the household (Degrande et al., 2007; trading in neighbourhood markets; and and a range of factors – such as marital Degrande, 2009). the collection, by men, of certain non- status, age, wealth and formal education – wood forest products such as gums and in addition to gender may co-determine GENDER DIFFERENCES IN honey if it requires physically taxing work how people use forests. FORESTRY VALUE CHAINS or is carried out in remote areas. Thus, Nevertheless, women’s knowledge tends As they are for most primary products analysing value chains from a gender to be linked more directly to household originating in developing countries, NTFP perspective can be useful in identifying food and nutrition needs as well as to value chains are highly gender-specific. practical opportunities for improving the health and culture, compared with men’s In many settings, women deal primarily livelihoods of the rural poor. knowledge (Daniggelis, 2003). A study with products of relatively low economic in Amazonia (Shanley and Gaia, 2001) value, engage in less lucrative informal GENDER BALANCE IN FOREST- found that, compared with men, women activities, and do not have the same USER GROUPS were able to identify a broader range of access to technology, credit, training and Strengthening gender equality in rural plant species (i.e. trees, vegetables, vines, decision-making as men. Unsurprisingly, societies is generally recognized as a bushes and herbs) and usable plant parts interactions between women and men and necessary prerequisite for increasing agri- (i.e. fruits, barks, leaves, seeds and roots). the division of labour between them at each cultural productivity, reducing poverty and Such knowledge is particularly important stage of a value chain depend heavily on hunger, and promoting economic growth. in natural disasters and food crises, when the environment in which they live, their The forest sector provides a broad range the collection and sale of forest products by livelihood preferences, and the available of opportunities to empower rural women. women often become critical for household technology. In general, women tend to Here, we discuss increasing the participa- survival. In many places, women’s famil- prefer flexible working conditions that do tion of women in forest-user groups. iarity with tree products such as fruits and not clash with their day-to-day household Women are generally under-represented nuts, medicinal materials and woodfuel responsibilities (CIFOR, 2012). in forest-user groups such as village forest plays a crucial role in coping with food Engagement in forestry value chains is committees and community forest asso- shortages. Moreover, the nutritive value often crucial for rural women’s livelihoods ciations (Coleman and Mwangi, 2012). In of wild foods is often substantial and and the well-being of their households. In many settings, rules allowing only one can be used as a substitute for purchased Ethiopia, for example, sorting and cleaning person per household to participate in such food items. gums and resins is the primary source groups tend to exclude women, and women Traditionally, women have been the of income for 96 percent of the women often become involved in decision-making primary domesticators of forest-based involved in the activity; in Burkino Faso, only after forest and tree resources have food and medicinal plants that are now women engaged in sorting gum arabic become degraded. As a result, community found in homegardens worldwide (Kumar reported that it was their most important forest groups sometimes enforce rules and Nair, 2004; Eyzaguirre and Linares, source of income for 3–4 months per year and regulations that do not fully reflect 2004). In humid western and southern (Shackleton et al., 2011). Many researchers women’s strategic interests and needs. Africa, rural women play a particularly have also noted that increases in women’s Female-dominated groups tend to important role in the cultivation of indig- incomes have greater impacts on food, have more property rights to trees and enous fruit trees (e.g. Irvingia gabonensis, health and education expenditure and bushes and to collect more woodfuel and Dacroydes edulis and Sclerocarya birrea) therefore on overall household well-being less timber than do male-dominated or (Campbell, 1987). While men may be the than increases in the incomes of men (e.g. gender-balanced groups (Sun, Mwangi and nominal owners of trees, women are often Blumberg, 1988; Hoddinott and Haddad, Meinzen-Dick, 2011). Gender-balanced responsible for the marketing of fruits and, 1991; Kabeer, 2003). groups, on the other hand, perform

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consistently better in all forestry functions compiled by Agarwal (2001, 2010), Sun, education levels of the women on those (e.g. the protection of plantings, forest Mwangi and Meinzen-Dick (2011) and councils significantly affected women’s regeneration, biodiversity conservation, Coleman and Mwangi (2012) suggests attendance at meetings and the likelihood watershed protection and the alloca- that when women constitute one-quarter they would speak up on critical issues. tion of forest-use permits). Pandolfelli, to one-third of the membership of local There is evidence that women’s par- Meinzen-Dick and Dohrn (2008) found forest management institutions, the ticipation in the decision-making of forest that gender-balanced groups capitalize on dynamic changes in favour not only of institutions such as forest-user groups the complementary roles of women and the consideration of women’s use of and reduces the level of gender-based conflict. men, mobilize people for collective action, access to forest resources but also towards This is because participation leads to new and enable better access to information more effective community forest manage- rules of access that take women’s needs and services from external agents. The ment decision-making and management into account, and therefore their activities greater involvement of women in forest as a whole. are less likely be criminalized or viewed governance may thus help ensure that The active and effective participation of as infringements. forest policies and planning are more women in forest institutions is governed sensitive to the food-security needs by a number of factors in addition to the of communities. proportion in which they are represented. Sun, Mwangi and Meinzen-Dick (2011) Agarwal (2010) and Coleman and Mwangi A woman cuts wood on a circular saw in a wood market in Ulaanbaatar, found that the relationship between the (2012) found that, in Honduras, India, Mongolia. The gender roles in forestry gender composition of groups and col- Nepal and Uganda, the gender composi- value chains are generally poorly lective outcomes is not linear. Evidence tion of forest councils and the age and understood and not well supported by policy-makers and service providers FAO/S. GALLAGHER

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CONCLUSION FAO. 1991. Household food security and Forestry and agroforestry systems are forestry: an analysis of socio-economic not gender-neutral. Compared with men, issues. Rome (available at: www.fao.org/ women are frequently disadvantaged – for References docrep/006/t6125e/t6125e00.htm). a range of interrelated cultural, socio- FAO. 1992. Forests, trees and food. Rome economic and institutional reasons – in Agarwal, B. 2001. Participatory exclusions, (available at: www.fao.org/docrep/006/ their access to and control over forest and gender: an analysis U5620E/U5620E00.HTM#TopOfPage). resources and in the availability of eco- for South Asia and a conceptual framework. FAO. 1999. Agroforestry parklands in sub- nomic opportunities. World Development, 29(10): 1623–1648. Saharan Africa. FAO Conservation Guide Empowering women in the forest sec- Agarwal, B. 2010. Does women’s proportional No. 34. Rome. tor can create significant development strength affect their participation? FAO. 2012. Forests for improved nutrition and opportunities for women (e.g. in terms of Governing local forest in South Asia. World food security. Rome (also available at: www. income, livelihood diversification, business Development, 38(1): 98–112. fao.org/docrep/014/i2011e/i2011e00.pdf). skills, independence and self-esteem) and Blumberg, R.L. 1988. Income under female Franzel, S. & Kiptot, E. 2012. Gender and can have important spillover benefits for versus male control: hypotheses from a theory agroforestry in Africa: who benefits? In their households and communities in terms of gender stratification and data from the third P.K.R. Nair & D. Garrity, eds. Agroforestry: of food security, health and education. world. Journal of Family Issues, 9(11): 51–84. the future of global land use. Springer. Women need to be adequately represented Campbell, B.M. 1987. The use of wild fruits in Gbetnkom, D. 2007. Forest management, in forest-related institutions, accepted as Zimbabwe. Economic Botany, 41(3): 375–385. gender and food security of the rural poor stakeholders with specific views and inter- CIFOR. 2012. Forests: gender and value in Africa. World Institute for Development ests, and empowered (e.g. through formal chains. CIFOR Info Brief No. 49. Center for Economics Research Paper No. 2007/86. education, training and support for income International Forestry Research (available United Nations University. generation) to have a say in transformative at: www.cifor.org/online-library/browse/ Hoddinott, J. & Haddad, L. 1991. Household decisions. Efforts to promote women’s view-publication/publication/3752.html). expenditure, child anthropometric status inclusion in forest-related institutions will Coleman, E. & Mwangi, E. 2012. Women’s and the intra-household division of income: help to maximize synergies between the participation in forest management: a cross evidence from Côte d’Ivoire. IFPRI forest sector and food security, for the country analysis. Global Environmental Discussion Paper #155. Washington, benefit of all. Change, in press. DC, International Food Policy Research Daniggelis, E. 2003. Women and ‘wild’ foods: Institute. Acknowledgements nutrition and household security among IFAD. 2008. Gender and non-timber forest This article is adapted from: Forests, Rai and Sherpa forager-farmers in eastern products: promoting food security and food security and gender, a background Nepal. In P.L. Howard, ed. Women & plants: economic empowerment (available at: paper for the International Conference on relations in biodiversity management and www.ifad.org/gender/pub/timber.pdf). Forests for Food Security and Nutrition, conservation. New York, USA, and London, Rome, International Fund for Agricultural by Francesca Guarascio, Nandini Zed Books and St. Martin’s Press. Development. Gunewardena, Christine Holding, Susan Degrande, A. 2009. Growing out of poverty: IPCC. 2007. Contribution of working groups Kaaria and Libor Stloukal. tree cultivation in West and Central Africa I, II and III to the fourth assessment The background paper was prepared for home use and markets. IFAD Technical report of the Intergovernmental Panel in close collaboration with Bimbika Advisory Note (TAN)-697. Yaounde, World on Climate Change. Geneva, Switzerland, Bassnet, Carol Colfer, Esther Mwangi, Agroforestry Centre and Rome, International Intergovernmental Panel on Climate Change. Bronwell Powell and Sheona Shackleton Fund for Agricultural Development. Kabeer, N. 2003. Gender mainstreaming in at the Center for International Forestry Degrande, A., Essomba, H., Bikoue Mekongo, poverty eradication and the Millennium Research and Anne Degrande at the World C. & Kamga, A. 2007. Domestication, genre Development Goals. Ottawa, International Agroforestry Centre. Comments on the et vulnérabilité. Participation des femmes, Development Research Centre. background paper by four anonymous des jeunes et des catégories les plus pauvres Kiptot, E. & Franzel, S. 2011 Gender reviewers in the FAO Forestry Department à la domestication des arbres agroforestiers and agroforestry in Africa: are women and by several colleagues in the Division au Cameroun. ICRAF Working Paper No. 48. participating? Occasional Paper No. 13. of Gender, Equity and Rural Employment Yaounde, ICRAF-WCA/HT. Nairobi, World Agroforestry Centre. are gratefully acknowledged. u Eyzaguirre, P.B. & Linares, O.F. 2004. Home Kumar, B.M. & Nair, P.K.R. 2004. The enigma gardens and agrobiodiversity. Washington, of tropical home gardens. Agroforestry DC, Smithsonian Books. Systems, 61(1–3): 135–152.

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Lambrou, Y. & Nelson, S. 2010. Farmers in Sunderland, T., Achdiawan, R., Angelsen, A., a changing climate: does gender matter? Babigumira, R., Ickowitz, A., Paumgarten, (available at: www.fao.org/docrep/013/ F., Reyes-García, V. & Shively, G. 2012. i1721e/i1721e00.htm). Myths and realities about men, women Pandolfelli, L., Meinzen-Dick, R. & and forest use: a global comparative study Dohrn, S. 2008. Introduction: gender and (available at: www.slideshare.net/CIFOR/ collective action: motivations, effectiveness myths-and-realities-about-men-women-and- and impacts. Journal of International forest-use). Development, 20(1): 1–11. Vinceti, B., Eyzaguirre, P. & Johns, T. 2008. Peach Brown, H.C. 2011. Gender, climate The nutritional role of forest plant foods change and REDD+ in the Congo Basin for rural communities. In C.J.P. Colfer, ed. forests of Central Africa. International Human health and forests: a global overview Forestry Review, 13(2): 163–176. of issues, practice and policy. London, Powell B., Hall, J. & Johns, T. 2011. Earthscan. Forest cover, use and dietary intake in Wan, M., Colfer, C.J.P. & Powell, B. 2011. the East Usambara Mountains, Tanzania. Forests, women and health: opportunities and International Forestry Review, 13(3): challenges for conservation. International 305–317. Forestry Review, 13(3): 369–387. Quisumbing, A.R., Otsuka, K., Suyanto, S., WFP. 2012. Handbook on safe access to Aidoo, J.B. & Payongayong, E. 2001. Land, firewood and alternative energy (SAFE) trees, and women: evolution of land tenure (available at: http://documents.wfp.org/ institutions in western Ghana and Sumatra. stellent/groups/public/documents/newsroom/ Washington, DC, International Food Policy wfp252989.pdf). Rome, World Food Research Institute. Programme. Rehfuess, E. 2006. Fuel for life: household World Bank, FAO & IFAD. 2008. Gender in energy and health (available at: www.who.int/ agriculture sourcebook (available at: http:// indoorair/publications/fuelforlife/en/). worldbank.org/genderinag). Rocheleau, D. & Edmunds, D. 1997. Women, Zulu, L.C. & Richardson, R.B. 2013. men and trees: gender, power and property Charcoal, livelihoods, and poverty reduction: in forest and agrarian landscapes. World evidence from sub-Saharan Africa. Energy Development, 25(8): 1351–1371. For Sustainable Development, 17(2): 127– Shackleton, S., Paumgarten, F., Kassa, 137. u H., Husseelman, M. & Zida, M. 2011. Opportunities for enhancing women’s economic empowerment in the value chains of three African non-timber forest products (NWFPs). International Forestry Review, 13(2): 136–151. Shanley, S. & Gaia, G.R. 2001. Equitable ecology: collaborative learning for local benefit in Amazonia. Agriculture Systems, 73: 83–97. Sun, Y., Mwangi, E. & Meinzen-Dick, R. 2011. Is gender an important factor influencing user groups’ property rights and forestry governance? Empirical analysis from East Africa and Latin America. International Forestry Review, 13(2): 205–219. Sunderland, T. 2011. In the management of forests, gender matters. CIFOR forest blog, 23 July 2011. Non-Wood News, 23.

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Forests, trees and resilient households

P. Dewees

Building greater economic ppreciation of the many ways in ways in which forests and trees contribute and ecological diversity into which forests and trees outside to the capacity of households to withstand landscapes is a key to increasing forests contribute to food security tough times, and it describes policy the resilience and therefore food Ais growing, but their role in increasing the responses to encourage the integration of security of rural households. resilience of households and ecosystems forests and trees in agricultural systems is less well known. Yet resilience is an to increase the resilience of both people important component of food security and and the environment. is likely to become more so as factors such People displaced by flooding in as climate change and global population Pakistan shelter their livestock among Peter Dewees is Forests Adviser, The World growth increase the likelihood of future trees. Forests and trees outside forests Bank, Washington, DC, USA. shocks. This article explores some of the can contribute to the capacity of households to withstand tough times ©FAO/A. HAFEEZ ©FAO/A.

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Chopped leaves of Gnetum spp., an NTFP, are offered for sale in a market. NTFPs are part of many coping strategies in which households increase their NTFP extraction to smooth out consumption levels when agricultural or other outputs fall

FOOD SECURITY AND RESILIENCE Hollings (1973) used the term “resilience” to mean the ability of ecological systems to respond to external forces and to persist in the face of those external forces. He distin- guished resilience from stability, which he defined as the ability of a system to return to an equilibrium state after a disturbance. He pointed out that ecological systems can be resilient and still fluctuate greatly. Walker et al. (2004) noted that the stabil- ©FAO/ J. MASUCH ity of human and natural systems depends on three complementary attributes: resil- ience, adaptability and transformability, where adaptability is the capacity to modify a system in ways that increase the capacity for resilience, and transform- THE ROLE OF FORESTS AND TREES become increasingly obscured; there is ability is the ability to make a radical IN RESILIENCE a trend to revert land-use systems from change when the existing system is no The roles of trees outside forests are well their often highly simplified states towards longer viable. known to farmers but tend to be poorly more ecologically complex systems.1 The Shocks at the household level – whether understood by technical specialists, plan- potential impact of this trend on food secu- from drought, illness, the loss of employ- ners and policy-makers and have mostly rity is profound. The resilience of complex ment, crop losses from disease, or fire, been overlooked in national statistics and land-use systems has analogues in eco- flooding and other natural disasters – economic accounts (Bellefontaine et al., logical science, where empirical evidence can undermine household food security. 2002). Farmers have been incorporating shows that complex ecosystems are far Longer-term stresses, such as those associ- trees into their farming systems – and more resilient than simple ones (although ated with population growth and climate increasing the resilience of those systems – arguably less productive, at least in the change, can interact with and exacerbate for thousands of years through intensive short term; see Hollings and Goldberg, short-term stresses. management strategies, such as in the 1971). Land-use systems that incorporate Time is an important variable in assessing sophisticated homegardens of Indonesia the use and management of forests and resilience, adaptability and transforma- (Michon, Mary and Bompard, 1986). They trees can increase resilience in a number of tion, and it is possible that adaptation that have also been retaining trees in less ways, some of which are discussed below. increases food security in one time period explicit processes of land-use change, for can have a negative effect on resilience example by ensuring that valuable indig- Trees and forests as safety nets in another (Carpenter et al., 2001). For enous trees for food production, like the The view that trees and forests can provide example, the advent of chainsaws and shea nut tree in western arid Africa, are important risk-reduction functions at the their incorporation into farming systems retained in farm fields as new agricultural household level is well-established in the helped agricultural societies by enabling lands are cleared (Wilson, 1989). literature. Looking at the problem of risk them to quickly clear large areas of forest There is growing awareness of the extent management, Delacote (2007) distinguished to create new agricultural land. However, of tree-involved farming practices and the extraction of non-timber forest products as the forest frontier became constrained their increasing prominence as a feature 1 and fallowing was no longer tenable for of agricultural land use. Even in modern In the European Union, for example, farmers are required to undertake actions to conserve critical maintaining soil fertility, the resilience of agricultural systems, the boundaries natural habitats in farmland in order to receive the system was compromised. between the forest and the farm have subsidies under the Common Agricultural Policy.

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TABLE 1. Coping strategies employed by households in response to anticipated (2008) documented the role that miombo and unanticipated risk, two villages in South Africa resources play when shocks hit household Coping strategy Percentage of households employing X2 Significance assets: households experiencing illness coping strategy shocks increased their consumption of Total Wealthiest Poorest environmental resources (including the Kinship 85 80 90 1.9 > 0.05 sale of NTFPs) by 42 percent. In their study Reduced spending 74 84 64 5.2 < 0.05 of rates of forest extraction in mountain- Changed diet 72 84 60 7.1 < 0.05 ous parts of Viet Nam, Volker and Waibel (2010) showed that households affected Saving/budgeting 72 88 56 12.7 < 0.05 by health shocks to economically active Sale of NTFPs 70 68 72 0.2 > 0.05 household members and severe weather Selling livestock 44 58 30 7.9 < 0.05 shocks were more likely to extract forest Savings clubs 41 64 18 21.9 < 0.05 products, especially woodfuel, than other Source: Paumgarten (2007) households. A common finding in many of these studies is that, during times of stress, (NTFPs)2 in two ways: as a diversification wealthy households were both likely to sell NTFPs are sold to generate income that strategy, in which households increase their NTFPs, this was an especially important can be used to purchase food, especially participation in a wide range of possible strategy for poor households because by the very poor. welfare-improving activities; and as a NTFPs were among the few marketable It seems clear, therefore, that forests coping strategy, where households increase assets at their disposal. and trees outside forests can act as cru- their extraction of NTFPs to smooth out These findings are echoed elsewhere. cial safety nets for food security and are consumption levels when agricultural or Shackleton (2006), Kayambazinthu often important components of coping other outputs fall. A number of studies et al. (2005), FAO (2005) and Barany et strategies for the very poor. However, have examined the role of NTFPs from a al. (2004) all pointed to the importance their use in short-term coping strategies diversification perspective (addressing the of NTFP sales to households afflicted may jeopardize their role in diversification question of the share of household income by HIV/AIDS. Tairo (2007) and Ngaga, strategies, as is explored below using the and consumption that is met by NTFPs), Munyanziza and Masalu (2006) showed case of woodfuel. but relatively few have reported findings the role of southern Africa’s miombo about how NTFPs contribute to smoothing woodlands as providers of “famine foods” Income, risk management and consumption as a coping strategy. and as natural insurance. Using seasonal woodfuel Paumgarten (2007) examined the safety- household data for rural Malawi, Fisher Reliance on woodfuel markets to generate net function of NTFPs in two rural villages and Shively (2005) found that households income during periods of stress has in South Africa by looking at how house- experiencing an income boost (e.g. from been widely observed but seldom well- holds coped with expected and unexpected remittances or a good harvest) depended documented. In his assessment of household crises over a two-year period (Table 1). less on forest product extraction than those responses to food shortages in Malawi The most important coping strategy used not receiving such a boost. Hegde and Bull in 2003, Zulu (2010) identified a range by all classes of household was a reliance on kinship groups and community support TABLE 2. Strategies to adapt to famine employed by households in southern networks to help compensate for income Malawi, 2003 losses. More generally, however, the study Strategy Percent (n = 381) showed that differences in how the wealthi- 1 Reduced number of meals per day 48.0 est and poorest households responded to stress were a function of differences in 2 Substituted maize with non-staple foods (e.g. pumpkins, potatoes and wild foods) 45.9 their access to assets: wealthier households 3 Engaged in piece-work to earn income to buy food 39.1 were more able to sell livestock or rely on 4 Used food grants from the government and other agencies 32.8 savings than were poorer households. The 5 Produced or sold charcoal to buy maize 29.7 study also showed that while poor and 6 Sold livestock to buy food or exchanged livestock for food 16.8 7 Sold other crops (e.g. vegetables, cassava and potatoes) to buy maize 16.0 8 Sold firewood to buy maize 11.8 2 NTFPs encompass all biological materials other than timber (but may include woodfuel) which Did not encounter a food deficit 14.2 are extracted from forests for human use. Source: Paumgarten (2007)

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A beneficiary of an FAO project of adaptation strategies (Table 2). More strategies are likely to be more forest- implemented in the wake of Hurricane Ivan in Grenada mills a tree trunk to be than 40 percent of surveyed households and tree-conserving (by raising the value used for local house-building. Forest- reported that, under famine conditions, of NTFPs and therefore the incentive to based employment can be important in they used income from the sale of charcoal conserve forests to ensure continued NTFP coping strategies in the face of disaster or firewood to purchase maize. production), we would expect to find cases There is a risk that reliance on woodfuel where woodfuel markets have stimulated The conventional wisdom in much of markets in hard times might mitigate the development of sustainable forest and Africa is that charcoal markets drive the short-term risk at a longer-term tree management systems. deforestation and forest degradation. environmental (and economic) cost. Thus, There are such examples. On the plains Mwampanda et al. (2013) pointed out, two questions emerge about the role of of the Gran Chaco in the Argentine however, that charcoal itself is seldom woodfuel in food security: do woodfuel province of Salta, management systems the culprit because deforestation tends to markets generate sufficient income to have been devised to bring large areas of be driven more by agricultural expansion, mitigate food insecurity, and what is the degraded woodland into production, with of which charcoal is a byproduct. The impact of this on the resource base? one objective being charcoal production capacity of dry woodlands to regenerate Woodfuel fits two risk-management niches (Bucher and Huszar, 1999). The system and recover is well known, for example in rural households – as a diversification relies on integrating livestock management in Senegal (Ribot, 1999) and Zambia strategy some of the time, and as a coping with woody biomass management, over (Chidumayo and Gumbo, 2013). In his strategy during times of environmental or a 20–40-year cycle, with the objective of assessment of forest degradation in other stress. The impacts and outcomes of landscape restoration. In the longer term, Senegal, Wurster (2010) found that forests woodfuel production and sale on poverty however, the system will need to better in areas managed for charcoal produc- and the resource base should be considered serve the interests of local farmers, who tion were equally degraded compared from both perspectives. If, as Delacote continue to depend on agricultural land with areas where charcoal production (2007) suggested, risk-diversification clearance to meet livelihood objectives. was absent.

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A man and a woman sell firewood in a wood market in Phnom Penh, Cambodia. There is a risk that reliance on woodfuel markets in hard times might mitigate the short- term risk at a longer- term environmental and economic cost ©FAO/J. KOELEN

Nevertheless, the most vulnerable may coincide with peak food production and increasing food security come from people, who may depend on burning periods, when food insecurity is less of these two dimensions: enabling more charcoal as a safety net during times of an issue. By the time of the next lean diverse and resilient farming ecosystems, environmental stress, often live in areas season, earlier income surpluses gained and creating greater economic diversity in that are ecologically highly fragile. It by the sale of NTFPs may have been terms of assets that can be used for income is this combination – low ecological disbursed among household members and consumption. resilience combined with high economic (Haglund et al., 2011). These observations Forests and trees undoubtedly act as vulnerability – that can bring the temporal point to the importance of incorporating food-security safety nets in times of dimension of risk management into play. detailed seasonal and other time-related crisis, especially for the very poor. In the As a coping strategy, risk management data into analyses of the extent to which long term, however, the value of forests that depends on cutting woodlands to the use of NTFPs form part of coping and trees in this role could diminish produce charcoal may simply shift the strategies at the household level. if the resource becomes degraded, for risk to a period in the future, before the example if social and environmental woodlands have had a chance to recover, BUILDING RESILIENT LANDSCAPES shocks become more frequent. So how and resilience in one period may be gained FOR IMPROVING FOOD SECURITY can farming ecosystems be made more at the expense of resilience in another. The analogues between ecological robust, and how can diversification be resilience and the role of diversification used to do this? Ambiguous relationship between strategies in food security are obvious: There is a clear need to take a broader income and food security more diverse ecosystems are more resilient perspective about how trees and forests are Higher income may not lead to improved to environmental and other shocks. Greater part of rural landscapes. The term “land- food security if households choose to economic diversity in terms of assets that scape” has permeated recent discussions spend the additional income in ways that can be used for income and consumption on rural development (see Rietbergen- do nothing to improve food security, such creates households that are more resilient McCracken, Maginnis and Sarre, 2007).3 as on social events or clothing. Moreover, to food insecurity. So the roles of forests markets for some NTFPs are seasonal and and trees in building household resilience 3 This section is derived from Dewees et al. (2011).

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A landscape is often defined as a geographi- help even out a household’s use of seasonal • have an impact on whole landscapes, cal construct that includes biophysical labour and create reserves of capital for not just individual sites; features of an area and also, potentially, new investment, and they can help clarify • stimulate grassroots economic devel- its cultural and institutional attributes. land tenure. Trees in landscapes can range opment that supports sustainable It describes a mosaic of land-cover and from contiguous, large tracts of forests livelihoods and thus diminishes some land-use types relevant to the processes used for multiple purposes, to mosaics of of the drivers of landscape degradation or services being considered or man- forests and blocks and other configurations and increases resilience; aged – a dynamic, complex patchwork of of trees and agroforestry systems within • involve people as central elements of overlapping political, economic, social and rural landscapes. landscapes and increase their involve- ecological systems that are individually A tree-oriented approach to landscape ment in decision-making. relatively homogeneous. restoration complements and enriches A landscape approach is a conceptual more narrowly defined approaches to Examples of landscape approaches framework that allows a structured view of afforestation, reforestation and land and Some countries are incorporating the broader effects of major interventions water conservation, with the central aim landscape strategies as a central part of in the rural sector. It describes such inter- of improving both human livelihoods and national development policies. In Rwanda, ventions at a spatial scale that encourages ecological integrity. Among other things, for example, the Land Husbandry, Water attempts to optimize interactions among a landscape restoration aims to: Harvesting and Hillside Irrigation range of land-cover types, institutions and • restore a balance of environmental, Project, supported by the World Bank, is human activities. The ideas of landscape social and economic benefits from for- using a landscape approach to address restoration, landscape planning and ests and trees within a broader pattern challenges created by uneven rainfall, eco-agriculture all build on landscape of land use; approaches and principles. • increase the functionality of land- A farm and forest landscape in the Trees in landscapes can increase the scapes and the supply of ecosystem Kiseny region in northeastern Rwanda. resilience of food-production systems and services across the range of land uses, Trees in landscapes can increase the therefore household resilience. They can not just maximize new forest cover; resilience of food-production systems and therefore household resilience ©FAO/A. ODOUL

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production variability, small landholdings, was largely regulatory, towards service A sound policy framework can help attract limited commercialization and land delivery aligned with poverty mitigation. responsible agro-investors and strengthen constraints due to population growth. Government- and donor-led initiatives food security. Legislation that recognizes It is providing infrastructure for land must go beyond the forest sector and farmers’ rights to the trees on their farms husbandry (e.g. terracing and downstream engage a wide range of public and private can provide incentives for land restoration reservoir protection), water harvesting stakeholders, including water, agriculture, and sustainable land management practices. (e.g. valley dams and reservoirs), and livestock, energy, land and environmental hillside irrigation (e.g piping, fittings and finance and planning authorities; producer Acknowledgement field application for basin and furrow groups; civil-society organizations, includ- This article is adapted from: Dewees, P.A. irrigation), all in a manner consistent with ing business associations; food companies; 2013. Bouncing back: forests, trees, and the principles of a landscape approach. and private investors. resilient households. Working paper In Albania, a project that integrates Landscape approaches work better prepared for the International Conference the management of forests, pastures and if rights to land and trees are secure. on Forests for Food Security and Nutrition, agriculture shows that with the strong Secure rights create incentives for individ- Rome, May 13 to 15, 2013. Washington, involvement of local communities, whole ual farmers, households and communities DC, Program on Forests. u landscapes can recover, with dramatic to invest in improved land and water results. Improved forest governance, local management and protect trees and forests. management, small-scale investments and Appropriate pricing regimes encourage the managed grazing measures have halted rational use of scarce resources. unsustainable land use, thereby reducing Improving value adding at the local carbon emissions and protecting key level can increase incentives for the watersheds. As a result, incomes from better management of landscapes and forestry and agriculture have increased trees in farming systems. Local value References by 50 percent in targeted microcatchment added can be boosted by simplifying the areas (The World Bank, 2012). regulatory regime to reduce transaction Barany, M., Hammett, A.L., Stadler, K. costs for poor producers and developing & Kengni, E. 2004. Non-timber forest POLICIES FOR BUILDING a framework to improve support for pro- products in the food security and nutrition RESILIENT LANDSCAPES AND ducer organizations and user groups. Trade of smallholders afflicted by HIV/AIDS in RESILIENT HOUSEHOLDS associations have shown that they can play sub-Saharan Africa. Forests, Trees and Various policy responses have been shown a role in promoting market diversification, Livelihoods, 14: 3–18. to increase the incorporation of trees and improving the prospects for niche market Bellefontaine, R., Petit, S., Pain-Orcet, M., forests in managed landscapes to improve entry and establishing product standards. Deleporte, P. & Bertault, J.G. 2002. Trees social–ecological resilience. Some of these Payments for ecosystem services can outside forests: towards better awareness. are described below. help. Markets for ecosystem services FAO Conservation Guides No. 35. Rome, Policies and institutions can be reori- from trees and better-managed farming FAO. ented to ensure that trees, forests and landscapes could be developed more fully. Bucher, E.H. & Huszar, P.C. 1999. Sustainable landscape restoration are addressed. Experience suggests that these types of management of the Gran Chaco of South The devolution of full control over land and initiative are most successful when they America: ecological promise and economic other natural resources to local institutions are integrated with other rural development constraints. Journal of Environmental and organizations is increasingly seen as activities; they can lead to productivity Management, 57: 99–108. a requirement for bringing about better increases and improve climate resilience. Carpenter, S., Walker, B., Anderies, J.M. natural resource management. The chal- Policies that improve land, water & Abel, N. 2001. From metaphor to lenges are to increase the legitimacy of and tree governance can minimize the measurement: resilience of what to what? local management organizations, ensure risks associated with large-scale land Ecosystems, 4: 765–781. that these organizations can put in place acquisitions. Large-scale land acquisitions Chidumayo, E.N. & Gumbo, D.J. 2013. effective management mechanisms, and are increasingly a reality in Africa and The environmental impacts of charcoal see that local organizations have the capac- elsewhere, and present both risks and oppor- production in tropical ecosystems of the ity to limit elite capture. At the same time, tunities. Policies that strengthen access world: a synthesis. Energy for Sustainable centralized government forest authorities, to information and protect existing land Development, 17: 86–94. which have tended to resist change, need to rights can help ensure that land transfers Delacote, P. 2007. Agricultural expansion, forest be reoriented from their earlier role, which are voluntary and beneficial for local people. products as safety nets, and deforestation.

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Environment and Development Economics, Ngaga, Y.M., Munyanziza, E. & Masalu, Zulu, L.C. 2010. The forbidden fuel: charcoal, 12: 235–249. H.E. 2006. The role of wild mushrooms in urban woodfuel demand and supply Dewees, P., Place, F., Scherr, S. & Buss, C. the livelihoods of rural people in Kiwele dynamics, community forest management 2011. Investing in trees and landscape village, Iringa, Tanzania: implications and woodfuel policy in Malawi. Energy restoration in Africa: what, where, and for policy. Discovery and Innovation, 18: Policy, 38(2010): 3717–3730. u how. Washington, DC, Program on Forests. 246–251. FAO. 2005. Miombo woodlands and HIV/AIDS Paumgarten, F. 2007. The significance interactions – Mozambique country report. of the safety net role of NTFPs in rural Forestry Policy and Institutions Working livelihoods, South Africa. Rhodes University, Paper No. 2. Rome (available at: www.fao.org/ Grahamstown, South Africa (MSc thesis). docrep/008/j5251e/j5251e00.htm). Ribot, J.C. 1999. A history of fear: imagining Fisher, M. & Shively, G.E. 2005. Can income deforestation in the West African dryland programs reduce tropical forest pressure? forests. Global Ecology and Biogeography, Income shocks and forest use in Malawi. 8: 291–300. World Development, 37(7): 1115–1128. Rietbergen-McCracken, J., Maginnis, S. Haglund, E., Ndjeunga, J., Snook, L. & Sarre, A. 2007. The forest landscape & Pasternak, D. 2011. Dry land tree restoration handbook. London, Earthscan. management for improved household Shackleton, S.E. 2006. Forests as safety livelihoods: farmer managed natural regen- nets for mitigating the impacts of HIV/ eration in Niger. Journal of Environmental AIDS in southern Africa. Forest Livelihood Management, 92: 1696–1705. Brief No. 4. Bogor, Indonesia, Center for Hegde, R. & Bull, G. 2008. Economic shocks International Forestry Research. and Miombo woodland resource use: a Tairo, V.E. 2007. The composition and household level study in Mozambique. regeneration status of wild food plants In: P. Dewees, ed. Managing the miombo in Chenene miombo woodland, Dodoma woodlands of southern Africa (Technical Rural District, Tanzania. Discovery and Annex 4). Washington, DC, The World Bank. Innovation, 19: 107–111. Hollings, C.S. 1973. Resilience and stability The World Bank. 2012. Albania Natural of ecological systems. Annual Review of Resources Development Project. Ecology and Systematics, 4: 1–23. Implementation Completion and Results Hollings, C.S. & Goldberg, M.A. 1971. Report (ICR1859). Washington, DC, Europe Ecology and planning. Journal of the and Central Asia Department, Sustainable American Institute of Planners, 37(4): Development Department, The World Bank. 221–230. Volker, M. & Waibe, H. 2010. Do rural Kayambazinthu, D., Barany, M., Mumba, R. household extract more forest products & Holding Anyonge, C. 2005. Miombo in times of crisis? Evidence from the woodlands and HIV/AIDS interactions: mountainous uplands of Vietnam. Forest Malawi country report. Forestry Policy and Policy and Economics. DOI:10.1016/ Institutions Working Paper No. 6. Rome, j.forpol.2010.03.001. FAO (available at: www.fao.org/docrep/008/ Walker, B., Hollings, C.S., Carpenter, S.R. & j6038e/j6038e00.htm). Kinzing, A. 2004. Resilience, adaptability Michon, G., Mary, F. & Bompard, J. 1986. and transformability in social–ecological Multistoried agroforestry garden system systems. Ecology and Society, 9(2): 5. in West Sumatra, Indonesia. Agroforestry Wilson, K.B. 1989. Trees in fields in southern Systems, 4(4): 315–338. Zimbabwe. Journal of Southern African Mwampanda, T.H., Ghilardi, A., Sander, K. Studies, 15(2): 1–15. & Chaix, K.J. 2013. Dispelling common Wurster, K.W. 2010. Management matter? misperceptions to improve attitudes and Effects of charcoal production management policy outlook on charcoal in developing on woodland regeneration in Senegal. countries. Energy for Sustainable PhD thesis, University of Maryland, Development, 17: 75–85. College Park.

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B. Vinceti, A. Ickowitz, B. Powell, K. Kehlenbeck, C. Termote, B. Cogill and D. Hunter

More research, and greater use raditionally, policy-makers have those diets with low environmental of traditional knowledge, will focused on energy-rich staple crops impacts which contribute to food and help fulfil the potential of forest such as wheat, rice and maize in nutrition security and to healthy life foods as a valuable component Tthe quest for national and global food for present and future generations. of nutritious diets. security. However, many staple foods Sustainable diets are protective contain only low amounts of limiting and respectful of biodiversity and micronutrients essential for human health ecosystems, culturally acceptable, and by themselves are insufficient to accessible, economically fair and address the problem of “hidden hunger”, affordable; nutritionally adequate, or micronutrient deficiency (Pinstrup- safe and healthy; while optimizing Barbara Vinceti, Céline Termote Andersen, 2013; Miller and Welch, 2013). natural and human resources. and Bruce Cogill are with Bioversity The challenge for policy-makers and other International, Rome, Italy, Amy Ickowitz stakeholders is to promote food systems Figure 1 shows some of the dimensions and Bronwen Powell are with the Center for International Forestry Research, Bogor, that are productive, nutritious, sustainable of sustainable diets. This article examines Indonesia, Katja Kehlenbeck is with the and culturally acceptable. The ultimate the contribution that forests and trees can World Agroforestry Centre, Nairobi, Kenya, goal is to have a food system that ensures make to some of these dimensions and and Danny Hunter is with Bioversity International and Charles Sturt University, “sustainable diets”, defined (in Burlingame proposes recommendations for optimizing Orange, Australia. and Dernini, 2012) as: that contribution.

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Previous page: A woman prepares to transport Landolphia spp. fruits (mabongo) to be sold at the market in Yangambi, the Democratic Republic of the Congo. A number of wild indigenous fruit trees in sub-Saharan Africa have high vitamin and mineral contents, and increasing their production and consumption could increase the sustainability of diets in the region

Right: Leaves of Vitex doniana and powder from baobab leaves (Adansonia digitata) at the market in Parakou, Benin

FORESTS AND SUSTAINABLE DIETS Use and nutrition of forest foods INTERNATIONAL/B. ©BIOVERSITY Forest foods such as wild fruits, nuts, veg- etables, mushrooms and animal products contribute in many ways to food security. While few communities worldwide rely on forest foods to provide their complete diet (Colfer, 2008), forest foods help maintain household nutrition in many communities, VINCETI especially during lean seasons (comple- menting, for example, the seasonality of staple agricultural crops), in times of low The dietary quality of many forest foods year and is also associated with high rates agricultural production, during periods of is high. Many of the micronutrients pro- of infection (e.g. diarrhoea, measles and climate-induced vulnerability, and when vided by forest foods have important health respiratory-tract infections) because of gaps in the availability of food occur due to and developmental functions, and their its importance in the functioning of the other cyclical events (Kehlenbeck, Asaah absence in diets therefore has important immune system (Black, Morris and Bryce, and Jamnadass, 2013). health implications (UNSCN, 2004). For 2003). Good dietary sources of vitamin example, vitamin A deficiency causes A are green leafy vegetables and orange- 1 blindness in up to 500 000 children per coloured fruits and vegetables. Deficiencies The many dimensions of a sustainable diet in iron, zinc and vitamin B12 can impair growth, cognitive development and school performance in children, with lifelong implications for health and socio-economic success (UNSCN, 2004). The best dietary Well-being, sources of these micronutrients are animal- Food and health Biodiversity, sourced foods (meat). nutrient needs, Most animal foods, including those environment, food security, sourced from forests, are rich in highly climate 1 accessibility bioavailable iron, zinc and vitamin B12 (as well as protein and fat) (Nasi, Taber and Van Vliet, 2011; Murphy and Allen, Sustainable 2003). Forests also provide diverse options diets for leafy vegetables, fruits and other plant foods important for the intake of vitamin A, iron, folate, niacin and calcium (Vinceti, Cultural Equity, Eyzaguirre and Johns, 2008). In one heritage, fair trade skills study in the United Republic of Tanzania, Ecofriendly, local, seasonal 1 The commonly accepted definition of bioavail- foods ability is the proportion of a nutrient that is digested, absorbed and metabolized through normal pathways. It is not enough to know how much of a nutrient is present in a dietary Source: Burlingame and Dernini, 2012 supplement; the more important issue is how much of that present is bioavailable.

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A woman prepares gbedegbede (Amaranthus dubius), a leafy vegetable harvested in the wild in Kisangani, the Democratic Republic of the Congo. Green leafy vegetables are good dietary sources of vitamin A, an essential micronutrient for human health

children who consumed forest foods had more diverse and nutrient-dense diets than those who did not, and there was also greater tree cover in close proximity to their homes (Powell, Hall and Johns, 2011). Another study in the Democratic Republic of the Congo found the consumption of wild plant foods to be associated with a higher intake of vitamin A and calcium (Termote et al., 2012). Even though the nature of much of the available evidence is circumstantial, a grow- ing body of data indicates that increased agricultural and forest biodiversity leads to a more varied diet, which in turn improves human health (Johns and Eyzaguirre, 2006; ©

Johnson, Jacob and Brown, 2013). BIOVERSITY INTERNATIONAL/C. T ermote

Wildlife resources. Wild meat, here defined as non-domesticated terrestrial mammals, birds, reptiles and amphibians harvested in the wild for food, is the main source of animal protein in many tropical forest regions, especially the Congo and Amazon basins (Arnold et al., 2011; Nasi, Taber and Van Vliet, 2011). A significant proportion of the wildlife biomass hunted TABLE 1. Nutrient contents of selected African indigenous and exotic fruits by humans for food across the tropics, per 100 g edible portion especially large-bodied primates, ungulates Species Energy Protein Vitamin C Vitamin A Iron Calcium and rodents (average weight greater than (Kcal) (g) (mg) (RE*) (µg) (mg) (mg) 1 kg), is found in tropical forest ecosystems, Indigenous fruits with ungulates and sometimes rodents Adansonia digitata L. 327 2.5 126–509 0.03–0.06 6.2 275 dominating the biomass in more open Dacryodes edulis 263 4.6 19 n.a. 0.8 43 habitats (Robinson and Bennett, 2004). Edible insects are also important elements Grewia tenax (Forrsk.) Fiori n.a. 3.6 n.a. n.a. 7.4–20.8 610 in the diet (Ndoye and Tieguhong, 2004; Irvingia gabonensis (kernels) 697 8.5 n.a. n.a. 3.4 120 Termote et al., 2012; Kuyper, Vitta and Sclerocarya birrea Hochst. 225 0.7 85–319 0.035 3.4 35 Dewey, 2013; van Huis et al., 2013). Tamarindus indica L. 275 3.6 11–20 0.01–0.06 3.1 192 Animal-based foods supply many Ziziphus mauritiana Lam. 184 0.4 3–14 0.07 0.8 23 important micronutrients in much higher Exotic fruits amounts or with higher bioavailability Guava (Psidium guajava L.) 68 2.6 228.3 0.031 0.3 18 than most plant-based foods (Murphy Mango (Mangifera indica L.) 65 0.5 27.7 0.038 0.1 10 and Allen, 2003). A recent study in a Orange (Citrus sinensis (L.) Osbeck) 47 0.9 53.0 0.008 0.1 40 remote part of the eastern rainforest in Pawpaw (Carica papaya L.) 39 0.6 62.0 0.135 0.1 24 Madagascar (where local communities Notes: high values are shown in bold. *RE = retinol equivalents. rely heavily on local wildlife resources) Sources: Kehlenbeck, Asaah and Jamnadass, 2013; Stadlmayr et al., 2013

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estimated that the loss of wild meat from nutrient composition of selected indig- non-cultivated indigenous vegetables in the the diet of children, without substitution by enous fruits in sub-Saharan Africa noted United Republic of Tanzania with regard to other sources, would result in a 29 percent very high variability in nutrient content iron, zinc and β-carotene (Msuya, Mamiro increase in children suffering from iron- among naturally occurring populations of and Weinberger, 2009), and also in cereals deficiency anaemia (Golden et al., 2011). the same species. This offers the oppor- (millet, sorghum, rice, wheat and fonio) The overexploitation of certain wild ani- tunity to select individual trees with the in Mali analysed for iron, zinc, thiamine, mal populations is leading to the depletion highest nutrient contents in their fruits for riboflavin and niacin, with ecological and of populations of some species (Nasi, Taber future domestication programmes. Similar climatic conditions strongly affecting values and Van Vliet, 2011). The resultant decline genetic variability has been documented in (Barikmo, Ouattara and Oshaug, 2007). in the availability of wild meat threatens the food security and livelihoods of forest communities (Heywood, 2013), especially those in which home consumption is more common than wild-meat trading.

Forest fruits in sub-Saharan Africa. Fruit consumption in sub-Saharan Africa has been estimated to fall considerably short of the recommended daily amount (Ruel, Minot and Smith, 2005). Kehlenbeck, Asaah and Jamnadass (2013) showed that a number of wild indigenous fruit trees have high vitamin and mineral contents (Table 1), with the potential to contribute year-round to the micronutrient supply of local communities, even during seasons of food shortages. For example, consuming 40–100 g of berries produced by Grewia tenax (a widespread, fruit- producing deciduous shrub) could supply almost 100 percent of the daily iron requirement of a child under the age of eight years. In addition to micronutrients, the high sugar content of fruits such as tamarind (Tamarindus indica) and baobab (Adansonia digitata) make them important sources of energy. The fruits of Dacryodes edulis and the seeds of Irvingia gabonensis, Sclerocarya caffra and Ricinodendron rautanenii all have higher fat contents than peanuts (Barany et al., 2004). Until a decade ago, little research had been conducted on the range of intraspe- cific genetic variation behind the variable nutritive values and other properties of edible products from key tree species. Although data are still sparse, a recent

review by Stadlmayr et al. (2013) of the FAO/A. PROTO

Fruit of the baobab tree (Adansonia digitata) hang ready to harvest near Basse, the Gambia. Baobab fruit are high in vitamin C

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Berries from a jujube fruit tree (Ziziphus zizyphus) in Bangladesh. Jujube is a drought- resistant tree that produces a nutritious fruit that can be eaten fresh or dried. Over many generations, indigenous peoples have developed knowledge systems, practices and decision-making for the identification, preparation and sustainable management of wild foods in forests and on farms

Homegardens. Seminal work on the domestication of wild tree species was carried out in West Africa in order to boost food supply and cope with food insecurity during conflicts (Okafor, 1976). Domestication programmes are now being developed to bring wild tree species into cultivation and to integrate them into NAPOLITANO FAO/G. agroforestry systems (Leakey, 2012), including homegardens. Homegardens are common in the tropics and subtropics and can provide readily available, diverse food products and many ecosystem services (Kehlenbeck, Arifin and Maass, 2007). It local markets maintain a prime position in 1999), yet they can attract premium prices has been estimated that around 1 billion local cultures; in several cases, commercial in urban markets (Chelang’a, Obare and people in the tropics obtain produce substitutes for forest foods do not exist, Kimenju, 2013). Others, such as wild meat from homegardens supported by semi- and wild-harvested products are generally in parts of Africa, bestow cultural prestige subsistence agriculture (Heywood, 2013). preferred even when alternative products (Lindsey et al., 2013). Improving homegarden systems can be can be found (Shackleton, Shanley and The availability of and access to forest highly effective in improving micronutrient Ndoye, 2008). foods may decline due to physical short- intake (Masset et al., 2012). Some studies ages of the product as a consequence have found that a child’s nutritional CHALLENGES AND OPPORTUNITIES of deforestation, forest degradation and status is associated with the presence The concept of sustainable diets is relatively overexploitation, among other reasons. of a homegarden and that the garden’s new, and it has not yet been incorporated In many countries, changes in livelihood biodiversity, rather than its size, is the in forest management approaches. The strategies, the processes of urbanization most important factor (Jones et al., 2005). following challenges must be met to and globalization, and changes in diets strengthen the contribution of forest foods have resulted in considerable changes in Cultural importance of forest foods to sustainable diets. the consumption of indigenous wild foods A recent extensive review of indigenous (Pingali, 2007). food systems around the world, including Cultural challenges Research has shown that as former in many forest regions, highlighted the cul- One of the factors most likely to determine hunter–gatherer groups, such as the Baka tural importance of traditional foods, many differences in the use and value of forest and Kola Pygmies of Cameroon and the of which are wild or semi-domesticated foods is ethnicity (Termote, Van Damme Tubu Punan of Borneo, became sedentary, (Kuhnlein, Erasmus and Spigelski, 2009; and Dhed’a Djailo, 2011). Traditional they suffered many negative dietary, nutri- Kuhnlein et al., 2013). Over many genera- knowledge should therefore be taken into tional and epidemiological consequences tions, indigenous peoples have developed consideration when promoting nutritious (Dounias and Froment, 2011). Around knowledge systems, practices and decision- forest foods as part of diets and in the the world, forest-based communities are making for the identification, preparation selection of priority species for marketing abandoning traditional lifestyles and food and sustainable management of wild foods and domestication (Shanley et al., 2011). regimes in exchange for diets higher in in forests and on farms (Kuhnlein, Erasmus Some indigenous wild foods, especially processed foods, salt, refined sugar and and Spigelski, 2009; Turner et al., 2011). In vegetables, may be perceived as old-fash- fat – a shift referred to as the nutrition South Africa, most forest foods traded in ioned or inferior (Chweya and Eyzaguirre, transition (Popkin, 2004).

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“Soumbala” produced from seeds of Parkia biglobosa, sold in a local market in Parakou, Benin. The availability of and access to forest foods may decline as a consequence of deforestation, forest degradation and overexploitation

(for example, Sunderland, Besong and Ayeni, 2002, on Gnetum spp.). Detailed inventories of these wild species exist for only a few countries and species, and the literature is scattered.

The rise of food-based approaches The overall health outcomes of a diet rich in multiple micronutrients and phytochemical and other components of food that regulate physiological functions are being increasingly recognized (Miller BIOVERSITY INTERNATIONAL/B. VINCETI © and Welch, 2013). This has led to a shift in focus in nutrition interventions towards Sustainability of use of forest foods frontiers in the Amazon Basin indicated improving overall dietary patterns and Several threats could affect the capacity that contributes to declining quality by increasing dietary diversity – of forests and other tree-based systems access (Shanley, 2012). Other reports defined as the number of unique foods to provide food and nutrients. The have shown that 5 of the 12 most valu- or food categories consumed in a given unsustainable harvesting of wild species able fruit and medicinal species traded in period – and promoting the consumption has been documented in various contexts eastern Amazonia are also valued timber of foods naturally rich in micronutrients (Sundriyal and Sundriyal, 2004; Delvaux, species (Serra et al., 2010). In Cameroon, or enriched through fortification2 (Torheim Sinsin and Van Damme, 2010). It is timber harvesting targets species that et al., 2010; Fanzo et al., 2013). increasingly accepted that the commer- have edible fruits and oils; others host Forest foods can play an important role cialization of non-wood forest products caterpillars that, at a certain time of the in such interventions. The increasing focus frequently leads to overharvesting and year, comprise 75 percent of the protein on dietary diversity as an indicator of food declining availability in the absence of consumed by Baka Pygmies (Ndoye and security and a proxy for diet quality allows sustainable forest management (Belcher, Tieguhong, 2004). Conflicts between a quick, user-friendly, low-cost assessment Ruiz-Perez and Achdiawan, 2005). A multiple uses have also been documented of the whole diet (Kennedy, Ballard and review of important fruit species in the in Asia (Limberg et al., 2007). In West Dop, 2011). Translating the findings into local economy and diet near Iquitos, Peru, Africa, selected multipurpose trees that programmes is challenging, however, and revealed that the availability of several supply food, wood and medicines are researchers are investigating the best tools of the most popular wild-harvested fruit maintained when woodland is cleared for evaluating diversity in diets and the species had decreased markedly (Vasquez for traditional agriculture (Faye et al., nutritional outcomes (Ruel, 2003; Arimond and Gentry, 1989). 2010). However, useful trees and shrubs et al., 2010; Masset et al., 2012). Many Subsets of species, usually referred to are now disappearing due to shortening as “conflict-of-use” species, are valued for fallow periods, conflicts over tenure, a 2 According to the definition used by the World both wood and non-wood forest products drying climate, overbrowsing by livestock, Health Organization and FAO, fortification refers (Guariguata et al., 2010). Research on and the absence of management practices to the practice of deliberately increasing the content of essential micronutrients (i.e. vitamins the rates of extraction (for timber) to protect regeneration (Maranz, 2009). and minerals, including trace elements) in a of species that are valued locally for For most wild-collected animal and food, irrespective of whether the nutrients medicinal and food use (e.g. Dipteryx plant species, little is known about the were originally in the food before processing, to improve the nutritional quality of the food odorata, Parahancornia fasciculata and effects of harvesting on genetic diversity supply and provide a public health benefit with Endopleura uchi) carried out in logging and the long-term survival of populations minimal risk to health.

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interacting factors affect the content and Increasing knowledge behaviours they think researchers will bioavailability of micronutrients in human Bringing about a change in attitude consider inappropriate. The generation and diets and there is a need to adopt a food- towards the consumption of traditional use of better data on the nutrient composi- system approach that includes all the steps foods is a challenge because they are tion of forest foods should be combined from forest/farm to plate, examining all often considered inferior (see van Huis with research on ecology, management aspects affecting the nutritional outcomes et al., 2013, for edible insects). Improved and (participatory) domestication so that of a particular diet, from agricultural scientific knowledge of nutritional values, appropriate, nutritionally rich species can production systems to food-processing and greater documentation of indigenous be integrated into fields and homegardens methods and consumer education strate- knowledge, could lead to more conducive (Pudasaini et al., 2013). gies (Miller and Welch, 2013). policies and a change in attitude towards There is growing interest in the use of forest foods (Kuhnlein, Erasmus and Adapting management of forests and micronutrient-rich foods, including wild Spigelski, 2009; Kuhnlein et al., 2013). trees to account for forest foods plant and animal foods, to supplement In some cases, the consumption of Many traditional communities actively the diets of children who predominantly micronutrient-rich foods has increased manage the wild resources they use. Where consume staple foods (Kuyper, Vitta and as a result of information dissemination there is conflict over the use of multi- Dewey, 2013). Based on local availability and promotion, but nutrition interventions purpose species that supply both timber and ease of access, underused comple- remain complicated by a lack of data on the and food products, forest management mentary foods may be affordable and nutrient content of lesser-known species plans should be negotiated with timber potentially more acceptable than some and limited understanding of the dietary companies and adapted to consider the other options. An example is the fermented requirements for many micronutrients. interests of both local communities and condiment known as soumbala obtained There are also challenges in measuring timber companies (Ndoye and Tieguhong, from the seeds of Parkia biglobosa, a west habitual food intake due to the difficulty 2004). Such an approach should be based African tree species. A rich source of iron, that study participants have in recalling on sound cost–benefit analyses that take soumbala is often used by families as a exactly what they have eaten over a certain into account the nutritional and cultural low-cost substitute for meat (Savadogo period of time, and also self-report bias, importance of forest foods in the diets of et al., 2011). where participants tend to under-report the most vulnerable: women and children.

Women in Parakou, Benin, gather for a focus group discussion about the food tree species commonly used in the diet during food

©BIOVERSITY INTERNATIONAL/B. VINCETI shortage periods

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In Gulmi in western Nepal, a socially marginalized family poses in their homegarden, which is an essential source of nutritious foods, including several derived from trees. Homegardens are key elements in rural landscapes; they are important reservoirs of agricultural biodiversity and of the knowledge to make use of it, and they can also help empower women. Better approaches are needed to manage heterogeneous landscapes for nutrition-sensitive food- production systems BIOVERSITY INTERNATIONAL/B. STHAPIT ©

Women have a central role in ensur- planting key tree-food species. In many higher. In the mixed landscapes of western ing food security and adequate nutrition countries, local control and management Panama, Smith (2005) found that each (de Schutter, 2011), and interventions of forests is still constrained by weak land use made a unique contribution to directed towards women are likely to political and institutional arrangements providing access to different species of have a particularly beneficial impact and a lack of access by the poor to wild meat, highlighting the importance of (Hoddinott, 1999). Supporting the role resources that can yield forest foods and diversified landscape approaches in both of women as producers and consum- income. Policies and programmes that research and conservation. ers of food would help remove barriers enable local people to have a genuine role to improved nutrition, including the in decision-making are rare (Larson and RECOMMENDATIONS increased consumption of forest foods. Ribot, 2007). To help optimize the role of forests and A process led by FAO that reviewed guid- trees in sustainable diets, we recommend ance documents developed by several Integrating forest biodiversity into that policy-makers, land-use planners and international organizations found that complex landscapes land managers: empowering women is a key principle Landscape approaches can help reconcile • seek innovative approaches to the in better linking agriculture and nutrition conservation and development objectives management of heterogeneous land- (Herforth, 2013). (Sayer et al., 2013). In many places, fallow scapes to ensure that food-production Maintaining forest cover near villages land and farm bushland areas are managed systems are nutrition-sensitive, while and homes may be necessary if forest actively to protect and regenerate species minimizing their ecological footprint; foods are to retain their place in diets. that are valued by local communities. In • prioritize research into and the Nutritionally important indigenous trees the Brazilian Amazon, primary forests development of nutritious forest foods, can also be introduced to farming systems were found to sustainably provide more including the documentation and to produce traditional forest foods through wild meat per unit area than secondary integration of indigenous knowledge, processes of domestication that improve forests (Parry, Barlow and Peres, 2009), the analysis and documentation of the product quality and yield. whereas the density of useful plant spe- nutritional composition, digestibility cies was lower in mature forests than in and bioavailability of forest foods, Access to forest foods secondary forests in the Bolivian Amazon the effect of storage and processing A lack of secure access rights and land (Toledo and Salick, 2006). In the Peruvian on the nutritional value of specific tenure discourages many poor and mar- Amazon, Gavin (2004) found that fallow forest foods, and the potential for the ginalized communities from investing provided fewer useful species than second- domestication of important forest spe- in more productive and sustainable land ary forest, but the total monetary value cies and their integration into farming management and from protecting and of the items obtained from fallow was systems and product value chains;

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• encourage research that examines the Colfer, C.J.P. 2008. Human health and forests: relative contribution of forest foods to global overview of issues, practice and local diets and nutrition; policy. London, Earthscan. • support research on governance and References Delvaux, C., Sinsin, B. & Van Damme, P. access to forests and forest products; 2010. Impact of season, stem diameter and • support the development of nutrition- Arimond, M., Wiesmann, D., Becquey, E., intensity of debarking on survival and sensitive product value chains Carriquiry, A., Daniels, M.C., Deitchler, bark re-growth pattern of medicinal tree involving forest foods; M., Fanou-Fogny, N., Joseph, M.L., species, Benin, West Africa. Biological • study the ecological impacts and sus- Kennedy, G., Martin-Prevel, Y. & Conservation, 143: 2664–2671. tainability of harvesting the various Torheim, L.E. 2010. Simple food group de Schutter, O. 2011. Report submitted by forest species for food; diversity indicators predict micronutrient the UN Special Rapporteur on the Right • ensure that extension services, schools, adequacy of women’s diets in 5 diverse, to Food: UN General Assembly Human hospitals and health centres are aware resource-poor settings. Journal of Nutrition, Rights Council (available at: www.srfood. of the benefits of, and promote, the 140(11): 2059S–2069S. org/index.php/en/component/content/article/ consumption of nutritious forest foods Arnold, M., Powell, B., Shanley, P. & 1-latest-news/1174-report-agroecology-and- in their programmes and interventions; Sundernald, T.C.H. 2011. Forests, the-right-to- food). • promote the better integration of infor- biodiversity and food security. International Dounias, E. & Froment, A. 2011. From foraging mation and knowledge on nutritious Forestry Review, 13(3): 259–264. to farming among present-day forest hunter- forest foods and their conservation Barany, M., Hammett, A.L., Stadler, K.M. gatherers: consequences on diet and health. into national nutrition strategies and & Kengni, E. 2004. Non-timber forest International Forestry Review, 13(3): 338–354. programmes by establishing policy products in the food security and nutrition Fanzo, J., Hunter, D., Borelli, T. & Mattei, F. platforms that bring together the of smallholders afflicted by HIV/AIDS in eds. 2013. Diversifying food and diets: using environment, health, development, sub-Saharan Africa. Forests, Trees and agricultural biodiversity to improve agriculture, forestry and other sec- Livelihoods, 14: 3–18. nutrition and health. London, Earthscan. tors with the aim of mainstreaming Barikmo, I., Ouattara, F. & Oshaug, A. Faye, M.D., Weber, J.C., Abasse, T.A., the use of forest foods in strategies 2007. Differences in micronutrients content Boureima, M., Larwanou, M., Bationo, addressing food security, nutrition, found in cereals from various parts of Mali. A.B., Diallo, B.O, Sigué, H., Dakouo, J.M., conservation and land-use planning Journal of Food Composition and Analysis, Samaké, O. & Sonogo Diaité, D. 2010. and related policies. 20(8): 681–687. Farmers’ preferences for tree functions and Belcher, B., Ruiz-Perez, M. & Achdiawan, species in the West African Sahel. Forests, Acknowledgements R. 2005. Global patterns and trends in Trees and Livelihoods, 20(2–3): 113–136. This article is adapted from: The con- the use and management of commercial Gavin, M.C. 2004. Changes in forest use value tribution of forests to sustainable diets, NTFPs: implications for livelihoods and through ecological succession and their a background paper prepared for the conservation. World Development, 33(9): implications for land management in the International Conference on Forests for 1435–1452. Peruvian Amazon. Conservation Biology, Food Security and Nutrition by Barbara Black, R.E., Morris, S.S. & Bryce, J. 2003. 18(6): 1562–1570. Vinceti, Amy Ickowitz, Bronwen Powell, Where and why are 10 million children dying Golden, C.D., Fernald, L.C.H., Brashares, J.S., Katja Kehlenbeck, Céline Termote, Bruce every year? (Child survival). The Lancet, Rasolofoniaina, B.J.R. & Kremen, C. 2011. Cogill and Danny Hunter. The prepara- 361.9376: 2226. Benefits of wildlife consumption to child tion of this article, and the background Burlingame, B. & Dernini, S. eds. 2012. nutrition in a biodiversity hotspot. Proceedings paper on which it is based, was supported Sustainable diets and biodiversity. Rome, of the National Academy of Sciences of the by the CGIAR research programmes FAO and Bioversity International. United States of America, 108(49): 19653– “Forests, Trees and Agroforestry” and Chelang’a, P.K., Obare, G. & Kimenju, 19656. DOI:10.1073/pnas.1112586108. “Agriculture for Nutrition and Health” S.C. 2013. Analysis of urban consumers’ Guariguata, M.R., Garcia-Fernandez, C., and by the Global Environment Facility/ willingness to pay a premium for African Sheil, D., Nasi, R., Herrero-Jáuregui, United Nations Environment Programme/ leafy vegetables (ALVs) in Kenya: a case of C., Cronkleton, P. & Ingram, V. 2010. FAO project “Biodiversity for Food and Eldoret Town. Food Security, 5(4): 591–595. Compatibility of timber and non-timber Nutrition”, led by Bioversity International. Chweya, J.A. & Eyzaguirre, P.B. 1999. The forest product management in natural The authors thank Ian Dawson and several biodiversity of traditional leafy vegetables. tropical forests: perspectives, challenges, anonymous reviewers who commented on Rome, International Plant Genetic Resources and opportunities. and earlier versions. u Institute. Management, 259: 237–245.

Unasylva 241, Vol. 64, 2013/2 63

Herforth, A. 2013. Synthesis of guiding T. Borelli & F. Mattei, eds. Diversifying food environment: lessons learnt from the principles on agriculture for nutrition. and diets: using agricultural biodiversity Malinau Research Forest, East Kalimantan, Rome, FAO (available at: www.fao.org/ to improve nutrition and health issues Indonesia. Bogor, Indonesia, Center for fileadmin/user_upload/wa_workshop/docs/ in agricultural biodiversity, pp. 257–269. International Forestry Research. Synthesis_of_Ag-Nutr_Guidance_FAO_ London, Earthscan. Lindsey, P.A., Balme, G., Becker, M., Begg, IssuePaper_Draft.pdf). Kennedy, G., Ballard, T. & Dop, M.C. 2011. C., Bento, C., Bocchino, C. & Zisadza- Heywood, V. 2013. Overview of agricultural Guidelines for measuring household and Gandiwa, P. 2013. The bushmeat trade in biodiversity and its contribution to nutrition individual dietary diversity. Rome, FAO. African savannas: impacts, drivers, and and health. In J. Fanzo, D. Hunter, T. Borelli Kuhnlein, H., Erasmus, B., Spigelski, D. possible solutions. Biological Conservation, & F. Mattei, eds. Diversifying food and diets: & Burlingame, B. eds. 2013. Indigenous 160: 80–96. using agricultural biodiversity to improve Peoples’ food systems and well-being: Maranz, S. 2009. Tree mortality in the African nutrition and health issues in agricultural interventions and policies for healthy Sahel indicates an anthropogenic ecosystem biodiversity, pp. 35–67. London, Earthscan. communities. Rome, FAO and Montreal, displaced by climate change. Journal of Hoddinott, J. 1999. Operationalizing Canada, Centre for Indigenous Peoples’ Biogeography, 36: 1181–1193. household food security in development Nutrition and Environment. Masset, E., Haddad, L., Cornelius, A. & projects: an introduction. Washington DC, Kuhnlein, H.V. 2009. Introduction: why are Isaza-Castro, J. 2012. Effectiveness International Food Policy Research Institute. Indigenous Peoples’ food systems important of agricultural interventions that aim to Johns, T. & Eyzaguirre, P.B. 2006. Linking and why do they need documentation? In improve nutritional status of children: biodiversity, diet and health in policy and H.V. Kuhnlein, B. Erasmus & D. Spigelski, systematic review. British Medical Journal, practice. Symposium on “wild-gathered eds. Indigenous peoples’ food systems: 344: d8222. DOI:10.1136/bmj.d8222. plants: basic nutrition, health and survival”. the many dimensions of culture, diversity Miller, B.D.D. & Welch, R.M. 2013. Linking biodiversity, diet and health in and environment for nutrition and health, Food system strategies for preventing policy and practice. Proceedings of the pp. 1–7. Rome, FAO and Montreal, Canada, micronutrient malnutrition. Food Policy. Nutrition Society, 65: 182–189. Centre for Indigenous Peoples’ Nutrition http://dx.doi.org/10.1016/j.foodpol. Johnson, K.B., Jacob, A. & Brown, M.E. 2013. and Environment. 2013.06.008. Forest cover associated with improved child Kuhnlein, H.V., Erasmus, B. & Spigelski, D. Msuya, J.M., Mamiro, P. & Weinberger, K. health and nutrition: evidence from the 2009. Indigenous peoples’ food systems: 2009. Iron, zinc and β-carotene nutrient Malawi Demographic and Health Survey the many dimensions of culture, diversity potential of non-cultivated indigenous and satellite data. Global Health: Science and environment for nutrition and health. vegetables in Tanzania. Acta Horticulturae and Practice, 1(2): 237–248. Rome, FAO and Montreal, Canada, Centre (ISHS), 806: 217–222. Jones, K.M., Specio, S.E., Shrestha, P., for Indigenous Peoples’ Nutrition and Murphy, S.P. & Allen, L.A. 2003. Nutritional Brown, K.H. & Allen, L.H. 2005. Nutrition Environment (available at www.fao.org/ importance of animal source foods. Journal knowledge and practices, and consumption docrep/012/i0370e/i0370e00.htm). of Nutrition, 133: 3932S–35S. of vitamin a rich plants by rural Nepali Kuyper, E., Vitta, B. & Dewey, K. 2013. Nasi, R., Taber, A. & Van Vliet, N. 2011. participants and nonparticipants in a Novel and underused food sources of Empty forests, empty stomachs? Bushmeat kitchen-garden program. Food and Nutrition key nutrients for complementary feeding. and livelihoods in the Congo and Amazon Bulletin, 26(2): 198–208. Alive&Thrive Technical Brief, Issue 6 Basins. International Forestry Review, 13(3): Kehlenbeck, K., Arifin, H.S. & Maass, B.L. (available at www.aliveandthrive.org). 355–368. 2007. Plant diversity in homegardens in a Larson, A.M. & Ribot, J.C. 2007. The poverty Ndoye, O. & Tieguhong, J.C. 2004. Forest socio-economic and agro-ecological context. of forestry policy: double standards on an resources and rural livelihoods: the conflict In T. Tscharntke, C. Leuschner, M. Zeller, uneven playing field.Sustainability Science, between timber and non-timber forest E. Guhardja & A. Bidin, eds. The stability 2(2). products in the Congo Basin. Scandinavian of tropical rainforest margins: linking Leakey, R.R.B. 2012. Living with the trees of Journal of Forest Research, 19(sup004): ecological, economic and social constraints life: towards the transformation of tropical 36–44. DOI:10.1080/14004080410034047. of land use and conservation, pp. 297–319. agriculture. Wallingford, UK, CABI. Okafor, J.C. 1976. Development of forest Berlin, Springer. Limberg, G.R., Iwan, M., Moeliono, M., treecrops for food supplies in Nigeria. Forest Kehlenbeck, K., Asaah, E. & Jamnadass, R. Sudana, I.M. & Wollenberg, E. 2007. Ecology and Management, 1: 235–247. 2013. Diversity of indigenous fruit trees and Community-based forestry and management Parry, L., Barlow, J. & Peres, C.A. 2009. their contribution to nutrition and livelihoods planning. In P. Gunarso, T. Setyawati, Hunting for sustainability in tropical in sub-Saharan Africa: examples from T. Sunderland & C. Shackleton, eds. secondary forests. Conservation Biology, Kenya and Cameroon. In J. Fanzo, D. Hunter, Managing forest resources in a decentralized 23(5): 1270–1280.

Unasylva 241, Vol. 64, 2013/2 64

Pingali, P. 2007. Westernization of Asian diets to reconciling agriculture, conservation, and marketing, value addition and implications and the transformation of food systems: other competing land uses. Proceedings for management. Economic Botany, 58(2): implications for research and policy. Food of the National Academy of Sciences of 300–315. Policy, 32(3): 281–298. the United States of America, 110(21): Termote, C., Bwama Meyi, M., Dhed’a Djailo, Pinstrup-Andersen, P. 2013. Can agriculture 8349–8356. B., Huybregts, L., Lachat, C., Kolsteren, P. meet future nutrition challenges? European Serra, M., Shanley, P., Melo, T., Fantini, A., & Van Damme, P. 2012. A biodiverse rich Journal of Development Research, 25: 5–12. Medina, G. & Viera, P. 2010. From the environment does not contribute to a better Popkin, B.M. 2004. The nutrition transition: forest to the consumer: the ecology, local diet: a case study from DR Congo. PloS an overview of world patterns of change. management and trade of Amapá amargoso, ONE, 7(1): e30533. DOI:10.1371/journal. Nutrition Reviews, 62(7Pt 2): S140–143. Parahancornia fasciculata (Poir) Benoist in pone.0030533 Powell, B., Hall, J. & Johns, T. 2011. the state of Pará. In U.P. Albuquerque & N. Termote, C., Van Damme, P. & Dhed’a Djailo, Forest cover, use and dietary intake in Hanazaki, eds. Recent developments and B. 2011. Eating from the wild: Turumbu, the East Usambara Mountains, Tanzania. case studies in ethnobotany, pp. 213–231. Mbole and Bali traditional knowledge on International Forestry Review, 13(3): 305–324. Recife, Brazil, Sociedade Brasileira de non-cultivated edible plants, District Tshopo, Pudasaini, R., Sthapit, S., Suwal, R. & Etnobiologia. Núcleo de Publicações em DRCongo. Genetic Resources and Crop Sthapit, B. 2013. The role of integrated Ecologia e Etnobotânica Aplicada. Evolution, 58(4): 585–618. DOI:10.1007/ home gardens and local, neglected and Shackleton S., Shanley, P. & Ndoye, O. s10722-010-9602-4. underutilized plant species in food security 2008. Invisible but viable: recognising Toledo, M. & Salick, J. 2006. Secondary in Nepal and meeting the Millennium local markets for non-timber forest products. succession and indigenous management in Development Goal 1 (MDG). In J. Fanzo, International Forestry Review, 9(3): 697–712. semideciduous forest fallows of the Amazon D. Hunter, T. Borelli & F. Mattei, eds. Shanley, P., Cymerys, M., Serra, M. & Basin. Biotropica, 38(2): 161–170. Diversifying food and diets: using Medina, G. 2011. Fruit trees and useful Torheim, L.E., Ferguson, E.L., Penrose, K. agricultural biodiversity to improve nutrition plants in Amazonian life. Rome, FAO, Bogor, & Arimond, M. 2010. Women in resource- and health issues in agricultural biodiversity, Indonesia, Center for International Forestry poor settings are at risk of inadequate intakes pp. 242–256. London, Earthscan. Research and Bristol, USA, People and of multiple micronutrients. Journal of Robinson, J.G. & Bennett, E.L. 2004. Having Plants International. Nutrition, 140: 2051S–2058S. your wildlife and eating it too: an analysis Shanley, P., Silva, S., Melo, T., Carmenta, Turner, N.J., Łuczaj, Ł.J., Migliorini, P., of hunting sustainability across tropical R. & Nasi, R. 2012. From conflict of use to Pieroni, A., Dreon, A.L., Sacchetti, L.E. ecosystems. Animal Conservation, 7: 397–408. multiple use: forest management innovations & Paoletti, M.G. 2011. Edible and tended Ruel, M.T. 2003. Is dietary diversity an by small holders in Amazonian logging wild plants, traditional ecological knowledge indicator of food security or dietary quality? frontiers. Forest Ecology and Management, and agroecology. Critical Reviews in Plant A review of measurement issues and research 268: 70–80. Sciences, 30(1–2): 198–225. needs. Food and Nutrition Bulletin, 24(2): Smith, D.A. 2005. Garden game: shifting UNSCN. 2004. Fifth report on the world 231–232. cultivation, indigenous hunting and wildlife nutrition situation. Geneva, Switzerland, Ruel, M.T., Minot, N. & Smith, L. 2005. ecology in western Panama. Human Ecology, United Nations Standing Committee on Patterns and determinants of fruit and 33(4): 505–537. Nutrition and International Food Policy vegetable consumption in sub-Saharan Stadlmayr, B., Charrondiere, R., Eisenwagen, Research Institute. Africa: a multi-country comparison. S., Jamnadass, R. & Kehlenbeck, K. 2013. van Huis, A., Van Itterbeeck, J., Klunder, Presentation made at the FAO/WHO Nutrient composition of selected indigenous H., Mertens, E., Halloran, A., Muir, G. & Workshop on Fruit and Vegetables for Health, fruits from sub-Saharan Africa. Journal of Vantomme, P. 2013. Edible insects: future Kobe, Japan. the Science of Food and Agriculture, 93: prospects for food and feed security. FAO Savadogo, A., Iboudu, J.A., Gnankine, O. 2627–2636. Forestry Paper No. 171. Rome, FAO. & Traore, A.S. 2011. Numeration and Sunderland, T.C.H., Besong, S. & Ayeni, Vasquez, R. & Gentry, A.H. 1989. Use and identification of thermotolerant endospore- J.S.O. 2002. Distribution, utilization and misuse of forest-harvested fruits in the forming Bacillus from two fermented sustainability of the non-timber forest Iquitos area. Conservation Biology, 3: 350–61. condiments Bikalga and Soumbala. products of the Takamanda Forest Reserve, Vinceti, B., Eyzaguirre, P. & Johns, T. 2008. Advances in Environmental Biology, 5: Cameroon. Consultancy Report for the The nutritional role of forest plant foods 2960–2966. Project Protection of the Forests Around for rural communities. In C.J.P. Colfer, ed. Sayer, J., Sunderland, T., Ghazoul, J., Pfund, Akwaya. Mamfe, Cameroon, GTZ. Human health and forests: a global overview J.-L., Sheil, D., Meijaard, E. & Buck, L.E. Sundriyal, M. & Sundriyal, R.C. 2004. of issues, practice and policy, pp. 63–96. 2013. Ten principles for a landscape approach Wild edible plants of the Sikkim Himalaya: London, Earthscan. u

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Participants attend the opening session of the International Conference on Forests and trees The International Conference on Forests for Forests for Food Security and Nutrition Food Security and Nutrition was organized at FAO headquarters in Rome, Italy outside forests are by FAO in partnership with Bioversity International, the Center for International Key messages essential for global Forestry Research, the World Agroforestry • The role of forests and trees outside food security and Centre and the World Bank.1 This technical forests2 in the fight against hunger meeting was attended by more than demands much greater attention and nutrition 400 participants, comprising experts from should be integrated with strategies for governments, civil-society organizations, food security and nutrition. Summary of the International indigenous and other local communities, • Food security is grounded in diversity – in donors and international organizations in terms of biota, landscapes, cultures, diets, Conference on Forests for more than 100 countries, who made a wide production units and management. Forests Food Security and Nutrition range of important points, many of which are and trees are critical for maintaining summarized below. that diversity. FAO headquarters, Rome, Italy, This summary and the recommendations • The ecosystem services provided by forests 13–15 May 2013 therein were developed by the conference and trees make essential contributions organizers and do not necessarily represent to forest-dependent communities and the position of the member states of FAO. agriculture by, among other things, protecting soil and water, maintaining soil fertility, regulating the climate, and 1 The conference was sponsored by the providing habitat for wild pollinators and Department for International Development of Great Britain and Northern Ireland, the the predators of agricultural pests. German Federal Ministry of Food, Agriculture and Consumer Protection, the Norwegian 2 As used in this summary, the term “trees outside Ministry of Agriculture and Food, the United forests” encompasses agroforestry systems, States Forest Service, the World Agroforestry other trees on farms, and trees in non-forested Centre and the World Bank. rural and urban landscapes.

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Key messages (continued) production and protecting forests, includ- • Greater collaboration at the national and • Forest foods and tree products have been ing through the restoration of degraded international levels is needed to improve important components of rural diets for forest land, the greater use of trees in data collection on, and the communication, millennia and today provide essential agriculture, and the alignment of policies reporting and monitoring of, the contribu- nutrition for millions of people. More than and institutional frameworks to that end. tions of non-wood forest products, forest one-third of the world’s people rely on • Secure land and forest tenure and more ecosystem services and other forest- woodfuel for cooking. equitable access to resources for local and tree-related aspects of food security • Forests, trees outside forests and the sus- communities and women will encour- and nutrition. tainable management of these resources age sustainable forest- and tree-based • Training in the management of sustainable are crucial for ensuring the resilience of approaches to food security and nutrition. forest enterprises can help forest-dependent food-production systems in the face of • There is a need to retrieve, document and communities, particularly women and youth, climate change and economic, social and make better use of traditional knowledge to gain access to equitable value chains, political instability. Forest- and tree-based and to combine it with scientific knowl- such as those applied in fair trade, thereby sources of income can contribute to build- edge to increase the role of forests and improving the food security and nutrition ing resilience. trees outside forests in food security of such communities and helping them to • There are opportunities to use more forest and nutrition. capitalize on their traditional knowledge. species, especially plants and insects, • Women often have specialized knowledge • Governments, civil society, indigenous peo- for the large-scale production of food of forests and trees in terms of species ples, bilateral and multilateral development products. However, deforestation and diversity, uses for various purposes, and assistance agencies, the private sector and forest degradation risks the loss of many conservation and sustainable manage- other stakeholders are invited to strengthen such species. ment practices, but the role of women the contributions of forests and trees out- • The single biggest cause of forest loss in ensuring the food security and nutri- side forests to food security and nutrition is agricultural expansion, but there is tion of forest-dependent communities is through a number of feasible actions, listed potential for both increasing agricultural underappreciated. in the recommendations below.

The benefits of forests, trees outside forests and agroforestry Globally, millions of people depend on forests and trees outside forests for their food security and nutrition – directly through the consumption and sale of foods harvested from forests and trees outside forests, and indirectly through forest-related employment, forest ecosystem services, and forest-based biodiversity. Forest foods and tree products, such as leaves, seeds, nuts, honey, fruits, mush- rooms, insects and game animals, have been important components of rural diets for millennia. The wide range of medicinal plants found in forests contributes to the health and

A woman in Guinea walks past a mature Parinari exca, an evergreen forest tree with rough-skinned, edible fruit. Globally, many millions of people depend on forests and trees outside forests for their food security and nutrition through the consumption and sale of foods harvested from forests and trees outside forests and through forest- related employment, forest ecosystem

FAO/R. FAIDUTTI services, and forest-based biodiversity

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Fishermen in Nagapattinum, Tamil Nadu, India, sit on an upturned boat after the 2005 tsunami. There is strong evidence that forests help protect coastal areas from flooding, thereby increasing the stability of food production on coastal lands, and they also act as sources of employment and provide food in the wake of such disasters

resilience and the capacity of people to meet their nutritional needs. An estimated 2.6 billion people rely on woodfuel, including charcoal, for cooking. The use of wood as a source of energy is vital for local economies and for maximizing the palatability and nutritional value of foods that require cooking. A wide range of agroforestry systems, including agrosylvipastoral systems, is

FAO/A. VITALE available to support food security and nutri- tion through the direct provision of food, by well-being of forest-dependent people and vital roles in riverine and coastal fisheries, raising farmer incomes and providing fuel forms the basis of many pharmaceutical which are often particularly important in for cooking, by improving soils and thereby products now produced globally. Forests and poor communities. Mountain forests per- increasing agricultural productivity, and trees outside forests are important sources form essential ecosystem services, such as through the provision of other ecosystem of fodder for livestock, especially in drylands. the provision of high-quality water for down- services. The genetic diversity in natural forests offers stream communities and their agricultural Indigenous peoples and other local commu- huge potential for the discovery, development activities. nities hold an immense wealth of traditional and improvement of new sources of food and Forests and trees outside forests are knowledge on the cultivation, harvesting and medicine, among others. important sources of food and income, preparation of forest foods and tree products There is enormous potential to use more especially for the poor and women, and and on sustainable land management. forest species, including plants and insects, may be key in times of economic, political or Traditional forest–agriculture landscapes for the large-scale production of foods. Many ecological crisis. The presence of forests and tend to have high resilience in the face of forest foods and tree products have extremely trees outside forests increases ecosystem environmental and social perturbations. high nutritional value. The ecosystem services provided by forests and trees outside forests make important contributions to agricultural production and forest-dependent communities, such as by protecting water and soil resources, contribut- ing to soil development processes, increasing soil fertility, regulating climate and providing habitat for wild pollinators and agricultural pest predators. Forested wetlands and mangrove forests help protect coastal areas from flooding, thereby increasing the stability of food pro- duction on coastal lands. Forests also play

Beekeepers near Kigoma, the United MAINA FAO/S. Republic of Tanzania, harvest honeycomb from a hive. Forest foods and tree products, such as honey, have been important components of rural diets for millennia

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Key challenges and bottlenecks areas, the harvesting of wood for energy is food security and nutrition; and the socio- The many contributions of forests and trees a major driver of forest degradation. economic circumstances of forest-dependent outside forests to food security and nutri- Agricultural practices should take into people. Moreover, there is no internationally tion are usually poorly reflected in national account the economic, social and environ- agreed framework (or formats) to guide the development, agricultural, and food security mental pillars of sustainable development. The collection, reporting and dissemination of and nutrition strategies, and there is often environmental costs of agricultural practices data on the use and trade of NWFPs, wildlife a lack of long-term funding to ensure the are often ignored. Along with unbalanced and forest ecosystem services important for success of projects to promote sustainable subsidies, this can make agriculture more food security and nutrition. forest management and agroforestry. Many profitable than the sustainable management Women often have specialized knowledge land-use planning strategies, often developed of forests and agroforestry systems but can of forests and trees in terms of their species without the participation of affected people, lead to unsustainable agricultural practices. diversity, uses for various purposes, and man- and large-scale agriculture investments, have Research is lacking on forest biodiversity agement and conservation. Compared with undermined smallholder farmers by excluding with potential importance for food security men, women’s knowledge tends to be linked them from emerging value chains, inadver- and nutrition. Moreover, there is a risk that more directly to household food consumption tently creating competition for resources, and traditional knowledge of forest foods will be and health and is particularly important during limiting the capacity of smallholders to cope lost, or will be exploited by outsiders who food crises. However, the role of women in with climatic risk, pests, and the uncertainty obtain most of the commercial benefits of forestry value chains is often poorly supported of market demand. Globally, agriculture is this knowledge. Local traditional knowledge by policy-makers and service providers. the main cause of forest loss. is often ignored in conventional approaches In many places, forest foods and tree to land-use planning, development and man- Policy options, practical products are being overharvested. For agement, which tend to reduce biodiversity innovations and emerging example, the overexploitation of wild meat is a and lead to a corresponding loss of resilience. opportunities serious issue in some forests in Africa. Poorly There is a lack of knowledge and data to The potential economic, social and environ- implemented land-use actions associated support effective policy‐making on (among mental gains from secure land tenure are with, for example, unsustainable logging, others): the role of non-wood forest products substantial and can lead to fundamental mining and agriculture can have cumulative (NWFPs), wildlife and forest ecosystem improvements in land management. The effects that cause the impoverishment of services in food security and nutrition and recent endorsement of the Voluntary land and local communities. Land and forest the realization of the right to food; labour Guidelines for the Responsible Governance degradation contributes to food insecurity and decent employment in the forest sector, of Tenure of Land, Fisheries and Forests in and is associated with increased rates of especially the NWFP subsector; the role of the Context of National Food Security by the child mortality. As people become more forests and trees in urban food security and Committee on World Food Security, coupled food insecure, their capacity to innovate is nutrition; mountain forests and their role in with the Voluntary Guidelines to Support hindered, further exacerbating their food insecurity. Those who are food insecure are more likely to deplete and mine natural resources unsustainably. If the technology is inefficient, the use of wood for cooking can cause severe health problems related to indoor air pollution and may also generate significant greenhouse gas emissions. In the absence of proper manage- ment and distribution systems, the collection of fuelwood can be a disproportionately high burden for women and children, but it can also be an important source of income. In some FAO/FO-0264/T. HOFER Steep agricultural fields in a highly degraded landscape in southwest China. Deforestation and unsustainable land management can have cumulative effects that cause the impoverishment of land and local communities

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Workers in Indonesia harvest rice. A landscape approach to management with a strong ecological basis can increase the capacity of people to produce, harvest and buy food in the face of social, economic and environmental shocks and stresses FAO/R. FAIDUTTI

the Progressive Realization of the Right to farmers to adopt agroforestry systems and and the introduction of trees and shrubs Adequate Food in the Context of National ensure the recognition of agroforestry as and by supporting farmer-managed natural Food Security, provide a basis for progress an investment option. Investments that regeneration are also promising. In a number in this area. support smallholder agroforestry ventures of countries, schemes to share forest-related Sustainable forest management is a broad in marketing their products and ecosystem revenues more equitably are improving the and evolving concept for ensuring the sustain- services, including through fair-trade food security and nutrition of the poor. able use and conservation of forests while initiatives, are yielding encouraging results for Decent employment in forestry is an generating benefits for local people, including both investors and producers. Microfinance important means of improving food security increased food security and nutrition. loans to small and medium-sized forest and nutrition for people who rely on forests A landscape approach to natural resource enterprises have been shown to lead to for their livelihoods. A sustainable approach management that addresses the economic, rises in family incomes in rural areas and would look at creating more high-skill jobs in social and environmental pillars of sustain- to increases in health, nutrition and quality the forest sector and upgrading existing ones able development can help ensure the of life, especially when such microloans are to increase income and productivity and make sustainable management of forests and trees made to women. In many cases, producer working conditions safer and more stable. outside forests in a broader context. Such a associations designed to meet the needs of This, in turn, will help improve the availability systematic approach with a strong ecological smallholders and marginalized and excluded of, access to and consumption of food in basis can increase the capacity of people to people have had a significant impact on terms of calories, and increase the quality produce, harvest and buy food in the face of improving livelihoods. The Committee on of food in terms of variety, diversity, nutrient social, economic and environmental shocks World Food Security is developing principles content and safety. Small and medium-sized and stresses. This focus on resilience can for responsible agricultural investments in the forest enterprises and community-based contribute to the long-term achievement of context of food security and nutrition. forest management have huge potential to food security. The active participation of all REDD+ initiatives can help in the provide employment in forest communities stakeholders, including the economically recognition of the forest rights of indigenous and can be especially important for women. marginalized and socially excluded, in sus- peoples and other local communities, Strong rural institutions can help ensure tainable land management, benefit-sharing although income from such initiatives has the contribution of forests and trees outside and decision-making is crucial. not yet proved sufficient to sustain forests forests to the food security and nutrition of Policies that improve rights of use and financially. Initiatives to promote sustainable rural communities. The commitment and access to land, forests and trees could development and food security and nutrition capacity of governments to engage openly create significant incentives for small-scale through sustainable forest management with rural communities is required.

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This wooded area in the communally owned and managed Ejido Canalejas de Otates in Mexico contains useful timber and provides shelter and fodder for livestock. Broad, intersectoral partnerships are needed to promote the sustainable use of forests and trees outside forests by rural communities to contribute to the achievement of food security and nutrition

8. Taking an integrated approach to food security and nutrition so that relevant sectoral policies, including those on agri- culture, forests, trees, wildlife and food security and nutrition, have well-defined objectives, targets and time frames for their implementation and are coordinated intersectorally, and that all stakeholders, from forest‐dependent communities to all relevant ministries, are involved actively

FAO/A. CONTI in their development, implementation and monitoring. Recommendations stewards and beneficiaries of forests 9. Encouraging spatial land-use planning Governments, civil society, indigenous peo- and wildlife. that takes into account the many impor- ples, bilateral and multilateral development 5. Eliminating all forms of discrimination in tant roles of forests and trees outside assistance agencies, the private sector and forests and promoting equal opportuni- forests in food security and nutrition. other stakeholders are invited to strengthen ties for youth, women and men and the 10. Encouraging intersectoral cooperation the contributions of forests and trees outside protection of the rights of indigenous to promote the sustainable management forests to food security and nutrition by: peoples and other local communities, of forests and trees outside forests at 1. Participating in broad partnerships to including the right to free, prior and the landscape scale, include forests promote the sustainable use of forests informed consent and the right to territory. and trees outside forests in resilience and trees outside forests by rural com- 6. Reviewing all relevant laws, policies strategies, and investigate the lessons munities to contribute to the achievement and actions so that they uphold the from sustainable forest management that of food security and nutrition. food-related rights set out in the could be applied to achieve sustainability 2. Ameliorating conditions that currently Universal Declaration of Human Rights, at the landscape scale. keep forest-dependent people in low‐ the Covenant on Economic, Social and 11. Supporting sustainable wildlife manage- status and low-productivity jobs. Cultural Rights and other relevant treaties ment as a source of food with scientific, 3. Providing access to resources by indige- and documents, and so that, among other technical and traditional knowledge, nous peoples and other local communities things, they: do not violate the right to balancing the economic, social and and marginalized people by, for example, food; protect citizens from such violations; environmental values of wildlife for applying the Voluntary Guidelines for provide mechanisms to ensure that mar- present and future generations. the Responsible Governance of Tenure ginalized and excluded forest-dependent 12. Increasing opportunities for green jobs of Land, Fisheries and Forests in the communities have access to justice if and improving conditions for forest work- Context of National Food Security. such violations occur; and provide for ers, especially the most vulnerable, and 4. Creating, as appropriate, and strengthen- concrete possibilities to enable people integrating decent employment concerns ing rural community-based institutions to feed themselves, including through in forest and other natural resource poli- and increasing social dialogue and the use of forests and trees. cies and programmes. representation with the aim, among other 7. Protecting forests and seeking ways in 13. Encouraging the development of markets things, of improving access to knowl- which agricultural production can be for forest ecosystem services, such as edge, finance, markets, better prices expanded without the loss or degradation the provision of clean drinking water and and technologies for local people and of forests, such as through the restoration other innovative financing mechanisms their equitable involvement in decision- of degraded forest lands and the greater to support the role of forests and trees making and recognizing the rights, roles use of trees outside forests as a means outside forests in food security and and responsibilities of communities as of intensifying agricultural productivity. nutrition.

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14. Promoting long-term investments in the socio-economic circumstances of these resources and their contributions forests and trees outside forests to forest-dependent people, and the role to food security and nutrition. build resilience so that food aid is less of forests and trees outside forests in 26. Developing indicators, tools and methods necessary. food security and nutrition, with a strong of data collection for food security and 15. Training institutional staff on gender emphasis on robust data. nutrition that incorporate forests and issues, involving women in monitoring, 23. Creating incentives for greater collabo- trees outside forests and the concerns reporting and verification activities, and ration between scientific disciplines, of women and youth, and develop the developing a gender-sensitive intersec- government sectors and rural institutions necessary capacity. toral global roadmap for forests and trees to synthesize scientific data and tradi- 27. Developing safeguard mechanisms to outside forests. tional knowledge on the role of forests ensure that the full impacts of forest 16. Making better use of traditional and trees outside forests in food security conversion and other activities such as knowledge about natural resource and nutrition. mining on food security and nutrition are management and working with local 24. Supporting efforts and investments to taken into account. stakeholders to improve the manage- communicate knowledge on the role Conference participants encouraged all ment of wild forest foods to ensure their of forests and trees outside forests in stakeholders to use this summary to attract sustainability. food security and nutrition in accessible, greater attention to the role of forests and 17. Increasing the efficiency of biomass- compelling formats to key stakeholders, trees outside forests in food security and based cooking systems through including civil society, rural institutions, nutrition. They further encouraged the FAO integrated approaches that take into scientists and policy-makers. Forestry Department to present this summary account both the woodfuel production 25. Recognizing and celebrating the cultural to the Committee on World Food Security chain and the woodfuel conversion chain. value, emotional connection and public and the Committee on Forestry, and to 18. Supporting the development of entre- appeal of forest foods and tree products other important fora, including the Second preneurial, financial and planning skills to rural and urban communities with a International Conference on Nutrition (ICN2) among small-scale forest producers view to leveraging political will and public to be held at FAO headquarters in Rome on to encourage their participation in, support for practices and policies that 19–21 November 2014. u and maximize the remuneration they support the sustainable management of receive from, market-oriented activities in agroforestry, tree-growing, NWFPs, small-scale and the What policy-makers need to do provision of ecosystem services. 19. Supporting the development of producer FAO has developed a brief for policy-makers • Promote policies that increase access associations to assist them to gain based on this conference summary and other by smallholders to credit, technology, access to markets and receive equitable outcomes of the International Conference extension services and insurance, as well benefits from forests, including through on Forests for Food Security and Nutrition. as to markets for their forest and tree local added value. The brief makes the following five strategic products and ecosystem services. 20. Collaborating nationally and internation- recommendations: • Achieve gender equality in the formula- ally to improve data collection, reporting • Provide secure land and forest tenure tion, implementation and evaluation of and monitoring of NWFPs, forest ecosys- and equitable access to resources by food-security, nutrition and poverty- tem services, forest wildlife and other applying the principles outlined in the alleviation policies and investment forest-related aspects of food security Voluntary Guidelines for the Responsible strategies. and nutrition. Governance of Tenure of Land, Fisheries • Strengthen mechanisms for the collec- 21. Encouraging research that supports the and Forests in the Context of National tion and timely dissemination of data sustainable use of wild forest species Food Security. on the contribution of forests and trees of plants, as well as insects and other • Develop mechanisms for coordina- to food security and nutrition for use in animals, to improve yields and increase tion across the agricultural, forestry, policy-making. the sustainability of food production. livestock, fisheries, energy, mining Towards food security and improved 22. Establishing transparent and inclusive and other relevant sectors to ensure nutrition: increasing the contribution of platforms for the dissemination and stronger coherence of food security and forests and trees, a brief for policy-makers, exchange of knowledge and experiences nutrition interventions and better policy can be downloaded at www.fao.org/forestry/ and to build awareness of the importance alignment. food-security/en/. of NWFPs and forest ecosystem services,

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fao forestry ©FAO/G. BIZZARRI Researchers tend seedlings in a greenhouse at the Indian FAO members adopt first global action plan for Council for Forestry Research Institute, Dehradun, India. A new global action plan aims to conserve the genetic diversity forest genetic resources of the estimated 80 000–100 000 tree species worldwide There are an estimated 80 000–100 000 tree species worldwide. Forests and trees outside forests provide essential ecosystem in June 2013. The Global Plan was prepared based on needs services, such as the protection of water catchments and soil and priorities identified in regional consultations and reports and carbon sequestration, and they also produce important foods submitted by member countries for the first edition of State of and other products. The capacity of humanity to meet the present the world’s forest genetic resources, which will be released and future challenges of food security, poverty alleviation and by FAO in 2014. FAO’s Commission on Genetic Resources sustainable development depends in large part, therefore, on the for Food and Agriculture has asked the Organization to continued availability of the rich diversity between and within tree develop an implementation strategy for the Global Plan and to species. Genetic diversity is needed to ensure that forest trees ensure the mobilization of adequate financial resources for its can survive, adapt and evolve under changing environmental implementation, particularly in support of developing countries. conditions, such as those brought about by climate change. The main aims of the Global Plan of Action for the Genetic diversity is also needed for selection, breeding and Conservation, Sustainable Use and Development of Forest domestication programmes for the development of adapted Genetic Resources are to: varieties or to strengthen useful traits. In many countries, the • strengthen understanding and knowledge of forest genetic prospects for sustainable development in rural areas will be resources; greatly influenced by the state of diversity in forest ecosystems • promote the sustainable use and management of forest and species. genetic resources; The Global Plan of Action for the Conservation, Sustainable • develop and strengthen in situ and ex situ forest genetic Use and Development of Forest Genetic Resources, the first of resource conservation programmes through collaboration at its kind in the forest sector, was adopted by the FAO Conference the national, regional and global levels;

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• promote access to, and the sharing of, information on forest • strengthen national programmes and enhance institutional genetic resources at the regional and national levels; capacity – particularly in developing countries and countries • create and strengthen national programmes to increase with economies in transition – and develop relevant regional regional and international cooperation, including in and international programmes. Such programmes should research, education and training on the use and sustainable include education, research and training to address the management of forest genetic resources, and enhance characterization, inventory, monitoring, conservation, institutional capacity; development and sustainable use of forest genetic resources. • assist countries, as appropriate, to integrate forest genetic A total of 27 strategic priorities at the international, regional and resource conservation and management needs into wider national levels are identified in the Global Plan, grouped into the national policies and programmes and frameworks of action following four areas: at the national, regional and global levels; • improving the availability of, and access to, information on • promote the assessment of traditional knowledge, forest genetic resources; innovations and practices related to forest genetic resources, • the conservation of forest genetic resources (in situ and the equitable sharing of benefits arising from their use, the ex situ); recognition of their roles, and, where appropriate, the putting • the sustainable use, development and management of forest in place of effective policies and legislation addressing genetic resources; these matters; • policies, institutions and capacity-building. • promote adequate access to, and use of, quality forest For more information go to: www.fao.org/forestry/fgr/64582/en/. reproductive material to support research and development programmes at the national and regional levels and in Latin American and Caribbean Forestry Commission line with international laws and regulations regarding The 28th Session of the Latin American and Caribbean Forestry intellectual property; Commission was convened in Georgetown, Guyana, on 9–13 • promote ecosystem and ecoregional approaches as efficient September 2013. It was attended by delegates from 21 member means of promoting the sustainable use and management of countries and the representatives of seven international, forest genetic resources; intergovernmental and non-governmental organizations. The • assist countries and institutions responsible for the session was opened by His Excellency, Mr Donald Ramotar, management of forest genetic resources to establish, President of Guyana. implement and regularly review national priorities for the The Commission considered, and made recommendations on, sustainable use and management of forest genetic resources; a range of topics, including FAO’s sustainable forest management

Delegates pose during the 28th session of the Latin American and

Caribbean Forestry FAO Commission

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toolbox, which is under development, the FAO Fire Management of the region on forest issues in the context of the Organization’s Umbrella Programme, the state and conservation of the world’s new Strategic Objectives. forest genetic resources, voluntary guidelines on national forest Meeting during the session, the Commission’s four Subregional monitoring, incentive mechanisms for the protection of natural Groups (Caribbean, Mesoamerica, Amazon and Southern forests, such as payments for ecosystem services, and follow-up Cone) discussed and prepared their work plans for the period to the conclusions of the International Conference on Forests for 2014–2015. Food Security and Nutrition. For more information go to: www.rlc.fao.org/en/events/28- The Commission formulated regional priorities for consideration session-of-the-lacfc/. by FAO’s Committee on Forestry (COFO) and recommendations for the attention of the 33rd FAO Regional Conference for Latin America and the Caribbean. It expressed support for FAO’s African Forestry and Wildlife Commission wants new Strategic Framework, which promotes an intersectoral sustainable development goal on forests working approach, highlighting the role of forests in the five One of the main outcomes of the Rio+20 Conference, held in Strategic Objectives. 2012, was the agreement by countries to launch a process to The Commission recommended that COFO promote the develop a set of Sustainable Development Goals, which will build revision and strengthening of public forest policies so that forest on the Millennium Development Goals and converge with the management can be better integrated with national development post-2015 development agenda. processes seeking to achieve food security and social well- At its 19th session, held at Windhoek, Namibia, on 30 September being. The Commission also recommended that COFO promote to 4 October 2013, the African Forestry and Wildlife Commission the appropriate governance of forest resources, including land “strongly recommended a standalone forest Sustainable and forest tenure, and support the development of mechanisms Development Goal that takes into account the achievements and for the valorization and recognition of ecosystem services for inadequacies of the Millennium Development Goals and related the benefit of those owning or managing forests. All this should processes”. The Commission requested its Chair to submit this be done while promoting the appropriate incorporation and recommendation to the Open Working Group process on the recognition of the economic importance of the forest resource in development of the Sustainable Development Goals, including national accounts. through the G-77 and China; encouraged its members to convey The Commission recommended that the Regional Conference the recommendation through their representatives in the Open for Latin America and the Caribbean stress among its member Working Group; and invited other forestry and related bodies on countries the contribution of forests to reducing poverty the African continent and other regions of the world to support the and food security, improving and protecting livelihoods, implementation of the recommendation. and guaranteeing sustainable, productive agrosilvipastoral A report on other outcomes of the African Forest and Wildlife systems. The Commission reinforced the importance of forest Commission meeting will appear in the next edition of Unasylva. ecosystem services for the development of the agricultural and livestock sectors. The Commission recommended that the Regional Conference consider that food security depends on a strengthened forest sector, given that forests, trees and forest genetic resources play important roles in achieving strong and resilient agricultural and livestock sectors. It further recommended that the Regional Conference promote national-level institutional efforts to develop intersectoral development policies and agendas, which should encompass forest, environmental, agricultural and livestock issues in a holistic approach to promoting food security and economic development and reducing rural poverty. The Commission recommended that the Regional Conference, working at the international level, foster action to strengthen intergovernmental organizations carrying out technical cooperation in the forest sector, with a view to promoting sustainable forest management for the benefit of food security and poverty reduction. It specifically requested that FAO be strengthened so that it can continue to work with the countries

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world of forestry CATIE Participants listen to an address at the Third IUFRO Latin American Congress Third IUFRO Latin American Congress This event, held on 12–15 June 2013 in San José, Costa Rica, had 600 participants, comprising scientists, decision-makers, need to be adapted. Year after year, figures are being used professionals, students, community leaders and forest managers for which the origin is often unknown, as is the case with the and owners, and featured 300 scientific papers presented in number of forest-dependent people and the rate of species’ 53 technical sessions. The Congress produced the following extinctions. key messages: • There are clear examples of countries that have managed • Latin America needs a stronger and more permanent to achieve substantive objectives by creating a strong discussion about forests, especially with a view to base of renewable natural resources, especially forests, sustainable development and the importance of forests on a which has facilitated development (e.g. Republic of Korea, global scale. Finland, Costa Rica and Chile). This is the result of long-term • In Latin America, forests face major challenges related to government policies. deforestation (with record highs in the region), degradation, • The landscape approach is gaining in importance and climate change, poverty and food security. Further coincides with the Millennium Ecosystem Assessment challenges are the loss of genetic resources and the loss of concept of the adaptive mosaic and also with another topic irreplaceable social and cultural attributes. of worldwide priority – human security as a basis for building • These problems call for technical, economic, social and socio-ecological systems. political solutions. Therefore, it is necessary to improve the • Although bidirectional, the landscape approach should be science base for decision-making. This does not mean that bottom-up rather than top-down, with local governance at the there is insufficient science but that its messages are not centre of landscape organization. being transmitted well. • The landscape vision has become stronger at both the global • Statistics (the major reference figures at the global, regional and regional levels, as demonstrated by concepts such and national levels) that are used in the discourse urgently as adaptive watershed management, biological corridors,

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model forests and other actions that add to less-integrated tends to stick to the philosophy of “command and control”, land management methods. They can be summed up in the which implies high transaction costs. concept of climate-smart landscapes. This is a way of giving • The Congress demonstrated that the challenges facing an analytical framework to progress towards the integration forests and landscapes have transboundary effects. It of landscapes in an adaptive-mosaic strategy. has also become evident that a large quantity of scientific • In view of evident climate-change, there are challenges in knowledge is available in the region. More than ever, providing wood and non-wood forest products and meeting however, scientists need to become involved in networking growing demands for these products, which are considered across disciplines and borders. The Congress therefore carbon-positive, and their consumption will therefore continue highlighted the role of networking organizations such as to rise, as will the profitability of management actions related the International Union of Forest Research Organizations to forests and trees. (IUFRO) and Centro Agronómico Tropical de Investigación y • Forest management and wood production in natural forests Enseñanza (CATIE). took a prominent position in Congress presentations. Congress organizers produced “guidance for action” based This shows that sustainable forest management is being on keynote speeches and the 300 presented papers. For the recognized as an excellent way of conservation. In the conference summary, including the guidance for action, go to region, however, there are considerable discrepancies www.iufro.org/download/file/9793/3684/iufrolat3-resolutions_pdf/. between “rules on paper” and “rules in use”; governance

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books

Managing forests for climate change More than timber in tropical forests

Climate change guidelines for forest managers. FAO 2013. FAO Forestry Paper Multiple-use forest management in the humid tropics: opportunities and challenges No. 172. Rome. ISBN 978-92-5-107831-0 (print), E-ISBN 978-92-5-107832-7 (PDF). for sustainable forest management. C. Sabogal, M.R. Guariguata, J. Broadhead, The effects of climate change and climate variability on forest G. Lescuyer, S. Savilaakso, N. Essoungou & P. Sist. 2013. FAO Forestry Paper ecosystems are evident around the world and further impacts are No. 173. Rome, FAO, and Bogor, Indonesia, Center for International Forestry unavoidable, at least in the short to medium term. Addressing the Research. ISBN 978-92-5-107823-5 (print), E-ISBN 978-92-5-107824-2 (PDF). challenges posed by climate change will require adjustments to The multiple-value nature of forests has long been appreciated forest policies, management plans and practices. and used by forest-dependent people in the tropics. Explicitly These guidelines have been prepared to assist forest managers managing for some or all of these values – multiple-use forest to better assess and respond to climate-change challenges and management – is stipulated in the laws of many countries, but its opportunities at the forest management unit level. The actions formal implementation in the tropics is thought to be rare. they propose are relevant to all kinds of forest manager – such This paper reports on three regional assessments carried out as individual forest owners, private forest enterprises, public- to identify and draw lessons from on-the-ground initiatives in sector agencies, indigenous groups and community forest multiple-use forest management in the Amazon Basin, the Congo organizations. They are applicable in all forest types and regions Basin and Southeast Asia. In all three regions, information was and for all management objectives. collected through interviews with country-based forestry experts, Forest managers will find guidance on the issues they should forest managers and technicians. A complementary, Web-based consider in assessing climate-change vulnerability, risk and questionnaire further examined the reasons for the successes mitigation options, and a set of actions they can undertake to help and failures of multiple-use forest management initiatives. adapt to and mitigate climate change. Forest managers will also The paper concludes that forest managers need more find advice on the additional monitoring and evaluation they may support if they are to realize the potential of multiple-use need to undertake in their forests in the face of climate change. forest management. Greater effort is needed to eliminate This document complements a set of guidelines prepared by unfair competition from operators whose sole objective is to FAO in 2010 to support policy-makers in integrating climate- extract timber with little or no concern for multiple uses. In change concerns into new or existing forest policies and national most countries, the demarcation of a permanent forest estate forest programmes. and development of national land-use plans would increase Also available online: http://www.fao.org/docrep/018/i3383e/ investment in multiple-use forest management. Improving the i3383e00.htm. value of logged-over forest through would also increase the uptake of multiple-use approaches. Also available online: http://www.fao.org/docrep/018/i3378e/ i3378e00.htm.

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books

Improving the accuracy of forest carbon stocks Native trees in Burkina Faso

Manual for building tree volume and biomass allometric equations: from field Guide d’identifcation des arbres du Burkina Faso. M. Sacande, L. Sanou & measurement to prediction. N. Picard, L. Saint-André & M. Henry 2012. Rome, H. Beentje. 2012. 280 pages. Royal Botanic Gardens Kew, London, Kew Publishing. FAO, and Centre de Coopération Internationale en Recherche Agronomique pour le ISBN 978-1-84246-470-0. Développement, Montpellier, France. This book is a product of the Millennium Seed Bank Partnership, Under the United Nations Framework Convention on Climate which has worked for a decade to collect and conserve, in Change, the benefits to accrue to non-Annex I parties will be duplicates, seeds of more than 1 100 native plant species in based on results that must be measured, reported and verified. Burkina Faso. To address a lack of knowledge of the region’s The precision of these results, therefore, has a major impact on rich flora, this field guide identifies 250 native tree species and potential financial compensation. The capacity to measure forest provides valuable information on their habitats and distribution in carbon stocks is of increasing importance for countries that plan to Africa and elsewhere, their uses and physiology, the germination contribute to mitigating climate change through their forest activities. of their seeds, and their conservation status. The brief botanical Whatever the method used to measure carbon stocks, including descriptions, keys, local names and more than 500 fascinating remote sensing, ultimately trees must be measured in the field. photographs will help specialists and non-specialists to identify Measurements of trees in the field enable the development each species. of allometric equations, which can predict tree biomass from All these species are important for ecosystem functioning easy-to-measure dendrometric characteristics such as tree and most provide food, feed, energy, timber, traditional diameter and height (which may be obtained remotely). Allometric medicines, pesticides and insecticides, or are suitable for use equations, therefore, are key factors in estimating the contribution as ornamentals. The information provided on seed germination made by forest ecosystems to the carbon cycle. and propagation techniques is aimed at helping the cultivation This manual covers all the steps in the construction of of these native trees, which grow readily in local conditions allometric equations, starting with the measurement of tree without the need for irrigation, fertilizers or pesticides. The guide biomass in the field. It should therefore prove particularly useful also paves the way for the use of these tree species in habitat in countries that are not yet in possession of measurements and restoration. Guide d’identifcation des arbres du Burkina Faso is equations that match their forests. It takes the form of a guide a useful document for a wide range of people, such as foresters, intended for students, technicians and researchers working to park managers, agronomists, horticulturists, environmentalists, assess forest parameters such as volume, biomass and carbon tourists, teachers and students. stocks for commercial, bioenergy or climate-change mitigation purposes. Also available online: http://foris.fao.org/static/allometric/ Manual_EN_WEB.pdf.

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books

Surviving global economic turmoil Evaluating certification

Riding out the storm: improving resilience of the tropical timber sector to the An overview of current knowledge about the impacts of forest management impacts of global and regional economic and fnancial crises. F. Maplesden, certifcation: a proposed framework for its evaluation. C. Romero, F.E. Putz, A. Attah, I. Tomaselli & N. Wong. ITTO Technical Series No. 41. Yokohama, Japan, M.R. Guariguata, E.O. Sills, P.O. Cerutti & G. Lescuyer. 2013. Occasional Paper International Tropical Timber Organization. No. 91. Bogor, Indonesia, Center for International Forestry Research. Consumer and producer member countries of the International The often-claimed environmental and social benefits of forest Tropical Timber Organization (ITTO) were severely affected certification remain to be empirically evaluated. Virtually all by the global financial and economic crisis that stemmed from of the numerous publications on the impacts of tropical forest the United States subprime mortgage crisis in 2007. The crisis certification are based on secondary sources of information and triggered a plunge in housing starts and consumer demand not on field-based measurements. for wood products in traditional markets, resulting in cancelled This paper proposes an empirical research framework for a orders, depressed prices and a severe rationalization of the carefully designed field-based evaluation of the ecological, social, tropical timber processing industries in producer and consumer economic and political impacts of tropical forest management countries. The short-term impacts of the crisis included: difficulty certification, taking into account location-specific contextual among producer countries in accessing capital, a key source of factors that shape certification outcomes. The paper suggests growth, as domestic stimulus packages began to compete for that solid methodological quantitative and qualitative approaches global finance; a decline in foreign direct investment; a reduction be used to build proper counterfactuals on which to base the in exports by ITTO producer countries as imports by developed comparisons for inferring impacts, all informed by a thorough countries fell; increased competition for export markets; an end theory of change and through processes that bring stakeholders to the recent commodity price boom; increased unemployment, together. The proposed research framework is a first step towards particularly in emerging country export sectors; and reduced the design and future implementation of evaluation research in spending on research and development. the context of tropical forest certification on a global basis. It is This report was produced in response to concerns expressed hoped that the proposed research framework will help in learning by ITTO producer member countries that the global financial from past mistakes, building on lessons learned and improving and economic crisis had exposed the vulnerability and lack of decision-making towards the maintenance of forest values over preparedness of the tropical timber sector to manage future the long term, for the benefit of society as a whole. global and regional economic crises. It draws on a broad Also available online: www.cifor.org/online-library/browse/view- knowledge base and experiences in producer and consumer publication/publication/4188.html. countries in addition to other wood and non-wood industries, and it recommends a number of measures to be adopted by ITTO, ITTO member countries, regional organizations and forest industry and trade associations to support the tropical timber sector’s resilience to global economic shocks. Also available online: www.itto.int/direct/topics/topics_pdf_ download/topics_id=3351&no=1&disp=inline.

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Climate change in southern Africa First textbook on forestry

Forests, rangelands and climate change in southern Africa. S. Naidoo, C. Davis, & Sylvicultura oeconomica. Transkription in das Deutsch der Gegenwart. H. Thomasius E. Archer van Garderen. 2013. Forests and Climate Change Working Paper No. 12. & B. Bendix. 2013. Remagen, Germany, Verlag Kessel. ISBN 978-3-941300-70-5. Rome, FAO. The first textbook specifically about forestry, Sylvicultura Forests and rangelands are vital for rural communities in southern oeconomica, also known as Instructions about wild Africa but they are under threat from climate change and other (Anweisung zur wilden Baumzucht), was published in 1713 by pressures. While many climate-change efforts under way in Hans Carl von Carlowitz, a Saxonian mining administrator (see the forest sector in southern Africa are focusing on mitigation, Unasylva 240 for a detailed account of the influence of this book). countries recognize the urgent need to build resilience and facilitate Three reprint editions of the book have been published since adaptation in the sector. 2000, and a scientific edition has also seen the light, although the Forests, rangelands and climate change in southern Africa latter was only a literal account of the original Baroque text in its investigates the implications of climate change for forests and Gothic script. rangelands in southern Africa, including their vulnerabilities and Now, two forest scientists, Professor Harald Thomasius adaptation needs and options. Combined with an analysis of the (Tharandt) and Dr Bernd Bendix (Bad Schmiedeberg), have economic and social roles of forests and rangelands and the transcribed the original text into contemporary German with the drivers of change, this publication lays the foundation for stronger aim of overcoming difficulties posed to contemporary readers collaboration in this area among countries in southern Africa. by the elaborate Baroque language of the 18th century and its This publication is part of an initiative by FAO, in cooperation Gothic script. with the Southern African Development Community, on forests, The publisher and authors hope that this modern edition of rangelands and climate-change adaptation in southern Africa. The Sylvicultura oeconomica, which is complemented by in-depth initiative was launched at a workshop in Johannesburg, South background information and a number of comprehensive indices, Africa, in June 2013 to take stock of countries’ current efforts in this will make access to this 300-year-old publication as enjoyable area, identify country priorities and potential areas of cooperative and enriching as when it was first published. work, and define the scope of a programme for climate-change Verlag Kessel publications in German: www.forstbuch.de (Verlag adaption in the region’s forest and rangeland sectors. Kessel publications in English: www.forestrybooks.com) This report, which was prepared for the workshop, will be a valuable resource for specialists, policy-makers, forest managers, students and members of the public who want to know more about the crucial task of adapting forests and rangelands to climate change in southern Africa.

Unasylva 241, Vol. 64, 2013/2 E-book on edible insects now available

The FAO Forestry Paper Edible insects: future prospects for food and feed security, which achieved worldwide attention at its launch during the International Conference on Forests for Food Security and Nutrition, is also proving popular as an e-book. Edible insects describes the contribution of insects to food security and shows the many traditional and potential uses of insects for human consumption. Download it – and other selected FAO titles – to your iPad, Kindle, Nook or Sony Reader and highlight interesting passages, bookmark pages, make notes and search the full-text content with one click. www.fao.org/publications/e-book-collection/en/

Unasylva reader survey

At FAO we believe that Unasylva plays an important role in articulating the ideas, practicalities and challenges of sustainable forest management. But we want to know what you think. Please help us by participating in a short Web-based survey. We will use your responses to improve Unasylva and increase its impact in the development of effective forest policy and practice. The survey will take 5–10 minutes to complete. Check it out at the Unasylva webpage today! www.fao.org/forestry/unasylva

FAO Forestry: delivering information resources for 21st century learning and communication. www.fao.org/forestry I3482E/1/10.13I2890E/1/11.12