The challenge of HIV/AIDS: Where does agroforestry fit in? - World ...
The challenge of HIV/AIDS: Where does agroforestry fit in? - World ...
The challenge of HIV/AIDS: Where does agroforestry fit in? - World ...
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Chapter 10: Agr<strong>of</strong>orestry and environmental governance87Table 1.Characterization <strong>of</strong> the l<strong>in</strong>ks between five components <strong>of</strong> environmental governance and agr<strong>of</strong>orestry.Relation to farmer <strong>in</strong>centiveto deliberately manage treesLocation <strong>of</strong> policy mak<strong>in</strong>grelative to farmerTrends <strong>in</strong> policy and governancecontextProperty rights to landand treesFarmer assurance <strong>of</strong> future bene<strong>fit</strong>sfrom current <strong>in</strong>vestments; farmer<strong>in</strong>centive to obta<strong>in</strong> tree productson own farm or elsewhere <strong>in</strong> thelandscapeLocal norms; decentralized governmentagencies; national policiesGradual <strong>in</strong>dividualization; decentralizedstate agencies generally becom<strong>in</strong>gmore importantForest classificationand governanceFarmer <strong>in</strong>centive to obta<strong>in</strong> treeproducts from forest areas; farmer<strong>in</strong>centive to manage and protectnearby forestsDecentralized forest agencies;national forest agenciesDecentralization <strong>of</strong> state agencies;some movement away from commandand control approachBuffer zone and landscapeapproachesto conservationIncentives/dis<strong>in</strong>centives to managetrees near protected areas; types<strong>of</strong> trees allowed and encouraged <strong>in</strong>different parts <strong>of</strong> the landscapeDecentralized conservation/forestagencies; national forest agencies;<strong>in</strong>ternational conservation pressuresMixed success with <strong>in</strong>tegratedconservation and developmentprojects; landscape approachesstill largely experimentalEnvironmental servicemechanismsMost environmental service mechanisms<strong>in</strong>volve tree and vegetationmanagement by <strong>in</strong>dividual farmers,groups and/or local governmentsRegional dialogue for watershedservices; national policies and <strong>in</strong>ternationalmechanisms for biodiversityand carbonBecom<strong>in</strong>g part <strong>of</strong> government approaches<strong>in</strong> many countries <strong>in</strong> Lat<strong>in</strong>America; small experiments <strong>in</strong> otherregionsGlobal environmentalgovernanceUNFCCC 1 , UNCBD 2 , UNCCD 3 andGEF 4 all have significant forestrycomponents, with <strong>in</strong>adequate provisionfor smallholder agr<strong>of</strong>orestry; nospecific forestry convention s<strong>in</strong>cethe Rio conference <strong>in</strong> 1992National ratification and domestication<strong>of</strong> global agreements and fund<strong>in</strong>gopportunitiesUNFCCC has progressed furthest<strong>in</strong> explicitly consider<strong>in</strong>g potential <strong>of</strong>agr<strong>of</strong>orestry and smallholdersSource: Authors’ summary from this chapter and literature review.1United Nations Framework Convention on Climate Change2United Nations Convention on Biological Diversity3United Nations Convention on Combat<strong>in</strong>g Desertification4Global Environment Facilityand collective action, and a variety <strong>of</strong> quantitativeand qualitative research tools. Much<strong>of</strong> this research has been conducted <strong>in</strong> associationwith the Collective Action andProperty Rights Initiative <strong>of</strong> the ConsultativeGroup on International Agricultural Research(CGIAR) (Me<strong>in</strong>zen-Dick et al. 2002).In the 1980s and early 1990s, much <strong>of</strong> theevidence on the l<strong>in</strong>ks between agr<strong>of</strong>orestryand property rights <strong>in</strong> Africa emerged fromjo<strong>in</strong>t efforts by ICRAF and the Land TenureCentre at the University <strong>of</strong> Wiscons<strong>in</strong>–Madison(Bruce 1989; Fortmann 1985; Fortmannand Bruce 1988; Place 1995 and Ra<strong>in</strong>tree1987). Bruce (1989) summarizes the results<strong>of</strong> these studies by not<strong>in</strong>g that agr<strong>of</strong>orestryprojects may be associated with severalproblems <strong>of</strong> land and tree tenure. Firstly, aproject may disturb or destroy rights to otherimportant uses <strong>of</strong> the land or trees. Secondly,customary tenure systems that providemultiple uses <strong>of</strong> land and tree resourcesmay make it difficult for <strong>in</strong>dividual farmersto protect tree seedl<strong>in</strong>gs. Thirdly, some categories<strong>of</strong> <strong>in</strong>tended clients may be unable toparticipate <strong>in</strong> a project because they do nothave the right to plant or own trees. This <strong>in</strong>cludeslandless people and women <strong>in</strong> somesocieties. Fourthly, farmers may undertaketree plant<strong>in</strong>g as much to establish rights toland as for the direct products <strong>of</strong> the trees.In the mid-1990s, ICRAF, the InternationalFood Policy Research Institute (IFPRI) andTokyo Metropolitan University engaged