98<strong>World</strong> Agr<strong>of</strong>orestry <strong>in</strong>to the Futuremanagement. For example, Ramadhani etal. (2002) found that 5-year-old woodlots<strong>of</strong> Acacia crassicarpa <strong>in</strong> the Tabora district<strong>of</strong> Tanzania produced five times as muchwood as mature ‘miombo’ woodlands.Simple calculations show that if all thewood needed for tobacco dry<strong>in</strong>g camefrom woodlots <strong>in</strong>stead <strong>of</strong> the ‘miombo’,then 8 675 hectares <strong>of</strong> woodland would beconserved each year <strong>in</strong> the Tabora district.Govere (2002) attempted to test this substitutionhypothesis for the example <strong>of</strong> improvedfallows <strong>in</strong> eastern Zambia. His resultsare mixed: <strong>in</strong> one village the adopters<strong>of</strong> improved fallows gathered less woodthan non-adopters; <strong>in</strong> another village adoptersand non-adopters gathered roughly thesame amount <strong>of</strong> wood.A study by Garrity et al. (2002) around theMount Kitanglad Range National Park <strong>in</strong>M<strong>in</strong>dañao, the Philipp<strong>in</strong>es, provides supportfor a l<strong>in</strong>k between agr<strong>of</strong>orestry and reducedpressure on protected areas. Farmersaround this area <strong>of</strong> high biodiversity wereeducated about the use <strong>of</strong> natural vegetativestrips to stabilize hillside farm<strong>in</strong>g areas,and improved germplasm and nurserytechniques to enhance on-farm production<strong>of</strong> fruit and timber. <strong>The</strong> key <strong>in</strong>stitutional<strong>in</strong>novation was Landcare – farmer-ledknowledge-shar<strong>in</strong>g organizations <strong>in</strong>spiredby the Landcare movement <strong>in</strong> Australia.After a number <strong>of</strong> years, this comb<strong>in</strong>ation<strong>of</strong> technical and <strong>in</strong>stitutional <strong>in</strong>terventionsproduced positive impacts <strong>in</strong> terms <strong>of</strong> <strong>in</strong>creasedmaize yields, greater density <strong>of</strong>fruit and timber trees, reduced run<strong>of</strong>f anderosion, enhanced environmental awareness,reduced encroachments <strong>in</strong>to the park,and restored stream corridor vegetation.By 2002 there were more than 800 households<strong>in</strong> M<strong>in</strong>dañao that belonged to villageLandcare chapters around the parkboundary.Another study <strong>of</strong> the buffer zone <strong>of</strong> theKer<strong>in</strong>ci Seblat National Park, Indonesiahighlights the relationship between farmdiversification and reliance on adjacent nationalpark resources (Murniati et al. 2001).Compar<strong>in</strong>g a sample <strong>of</strong> rice-only farms,mixed garden farms and a comb<strong>in</strong>ation <strong>of</strong>both, the authors found that farms practis<strong>in</strong>gboth rice grow<strong>in</strong>g and mixed garden<strong>in</strong>ghad 80 percent lower dependency on parkresources. Factors associated with a higherpropensity to extract from protected forestresources were low farm <strong>in</strong>come and lowsupply <strong>of</strong> on-farm tree-based products,suggest<strong>in</strong>g that agr<strong>of</strong>orestry systems wereparticularly relevant <strong>in</strong> the buffer zones.ICRAF research around the Mabira ForestReserve <strong>in</strong> Uganda suggests that largerscale economic forces and forest policycan have greater impact on protected areasthan agr<strong>of</strong>orestry and other development<strong>in</strong>terventions undertaken around them.While resource extraction by adjacentcommunities <strong>in</strong>creased with proximity tothe forest, agr<strong>of</strong>oresry <strong>in</strong> the buffer zonecould not have any significant impact onthe quantitatively far more significant pressuresorig<strong>in</strong>at<strong>in</strong>g from outside the bufferzone, particularly from fuelwood marketsfor sugar and tea process<strong>in</strong>g, and for brickand charcoal mak<strong>in</strong>g (Mrema et al. 2001a;2001b; 2001c; 2001d).Angelsen and Kaimowitz (2004) argue thatthe conservation bene<strong>fit</strong>s <strong>of</strong> agr<strong>of</strong>orestryhave <strong>of</strong>ten been overstated, particularly <strong>in</strong>places where the forest frontier is still opento settlement and harvest<strong>in</strong>g. Angelsen andKaimowitz (2004) and Tomich et al. (2001)po<strong>in</strong>t out there are likely to be trade-<strong>of</strong>fsassociated with pr<strong>of</strong>itable agr<strong>of</strong>orestry: onone hand, there will be pressure to convertprimary forest to pr<strong>of</strong>itable alternative landuses; on the other hand, degradation <strong>of</strong>agr<strong>of</strong>orestry systems may lead to conversionto less desirable land uses. A classiccase <strong>of</strong> these trade-<strong>of</strong>fs is cocoa. Conversion<strong>of</strong> primary forest to cocoa productionhas been a major source <strong>of</strong> biodiversityloss <strong>in</strong> many parts <strong>of</strong> the humid tropics.However, compared to sun-grown cocoaor compet<strong>in</strong>g annual crops, shade-growncocoa agr<strong>of</strong>orests reta<strong>in</strong> much higher levels<strong>of</strong> biodiversity (Donald 2004).3. Agr<strong>of</strong>orestry and habitat for wildspeciesProposition: Agr<strong>of</strong>orestry can createhabitat for wild species <strong>in</strong> landscapematrices surround<strong>in</strong>g forest conservationareas.<strong>The</strong> <strong>in</strong>tegration <strong>of</strong> trees <strong>in</strong>to multiple-uselandscape matrices can contribute to wildbiodiversity through the ma<strong>in</strong>tenance <strong>of</strong>landscape connectivity, heterogeneity andcomplexity <strong>of</strong> vegetation structure, <strong>in</strong>tegrity<strong>of</strong> aquatic systems, and cleaner water. Treescan contribute nest<strong>in</strong>g sites, protectivecover aga<strong>in</strong>st predators, access to breed<strong>in</strong>gterritory, access to food sources <strong>in</strong> allseasons, and encourage beneficial speciessuch as poll<strong>in</strong>ators. Evidence <strong>of</strong> the nature<strong>of</strong> these relationships has been generatedthrough a fairly large number <strong>of</strong> field studies,most <strong>of</strong> which have focused on birds.One caveat is that there have been limitedstudies to date on how the spatial configuration<strong>of</strong> trees on farms and <strong>in</strong> landscapesaffects the conservation <strong>of</strong> different types <strong>of</strong>biodiversity.Buck et al. (2004) reviewed 12 studies thatfound agr<strong>of</strong>orestry systems to provide habitatfor diverse populations <strong>of</strong> birds, withthe greatest amount <strong>of</strong> evidence po<strong>in</strong>t<strong>in</strong>gtowards the habitat value <strong>of</strong> shade-grown
Chapter 11: <strong>The</strong> potential for agr<strong>of</strong>orestry99c<strong>of</strong>fee and cocoa systems <strong>in</strong> Southeast Asiaand Central America. However, there arealso contrast<strong>in</strong>g results: So<strong>in</strong>i (2004) foundlow levels <strong>of</strong> bird diversity <strong>in</strong> the multistrataChagga homegardens <strong>of</strong> Kilimanjaro,Tanzania. So<strong>in</strong>i postulates that the veryhigh levels <strong>of</strong> human population <strong>in</strong> thoseareas have created an <strong>in</strong>hospitable habitatfor most bird species.Naidoo (2004) presents a novel analysis <strong>of</strong>the relationship between forest types andbird types <strong>in</strong> and around the Mabira forest<strong>in</strong> Uganda. He analysed the diversity <strong>of</strong>songbirds along transects across differenttypes <strong>of</strong> landscapes, from <strong>in</strong>tact primaryforest, to regenerat<strong>in</strong>g secondary forests andagricultural fields. Songbirds were classifiedas forest specialists, forest generalists, forestvisitors and open habitat species. He foundroughly similar numbers <strong>of</strong> total songbirdspecies <strong>in</strong> each <strong>of</strong> the three land-use types,but marked differences <strong>in</strong> the percentages<strong>of</strong> different species groups. Forest specialistswere not found <strong>in</strong> the agricultural area;open habitat species were not found <strong>in</strong> the<strong>in</strong>tact forest. Statistical models <strong>of</strong> the habitat–speciesrelationship showed that treedensity and distance to <strong>in</strong>tact forest had thegreatest impacts on number <strong>of</strong> forest species.Model results <strong>in</strong>dicate that greater treedensity <strong>in</strong> agricultural fields could result <strong>in</strong>a sizeable expansion <strong>in</strong> the habitat <strong>of</strong> forestspecialists with<strong>in</strong> the forest and forest generalists<strong>in</strong> the forest marg<strong>in</strong>.Agr<strong>of</strong>orestry can enhance connectivity andlandscape heterogeneity <strong>in</strong> multi-functionalconservation landscapes. Zomer etal. (2001) found that an agr<strong>of</strong>orestry system<strong>in</strong>volv<strong>in</strong>g Alnus nepalensis and cardamomcontributed to the <strong>in</strong>tegrity <strong>of</strong> riparian corridorsfor wildlife conservation around theMakalu Barun National Park and ConservationArea <strong>of</strong> eastern Nepal.Grif<strong>fit</strong>h (2000) suggests a different ecologicalmechanism by which agr<strong>of</strong>orestry cancontribute to biodiversity – by provid<strong>in</strong>ga low risk refuge <strong>in</strong> the case <strong>of</strong> fire. Heassessed bird biodiversity <strong>in</strong> two agr<strong>of</strong>orestryfarms <strong>in</strong> the buffer zone <strong>of</strong> the MayaBiosphere Reserve <strong>in</strong> Guatemala <strong>in</strong> orderto determ<strong>in</strong>e whether those farms hadserved as biodiversity refuges dur<strong>in</strong>g thefires <strong>of</strong> 1998 that burned eight percent <strong>of</strong>the reserve. He found high numbers <strong>of</strong> birdspecies, <strong>in</strong>clud<strong>in</strong>g forest specialists and forestgeneralists – birds that are not usuallyfound <strong>in</strong> agr<strong>of</strong>orestry areas.4. Agr<strong>of</strong>orestry and the threats <strong>of</strong><strong>in</strong>vasive alien speciesProposition: Agr<strong>of</strong>orestry developmentcan be implemented <strong>in</strong> a way thatreduces the risk <strong>of</strong> alien <strong>in</strong>vasive speciesto acceptable levels, if adequateprecautions are taken.In the <strong>in</strong>troduction to this chapter wenoted that there are major concerns <strong>in</strong> theconservation community about the potentialthreat that farmer plant<strong>in</strong>g <strong>of</strong> treesmay pose to biodiversity. For example, theUNCBD <strong>The</strong>matic Programme <strong>of</strong> Workstates: “Tree plantations and agr<strong>of</strong>orestry areimportant sources <strong>of</strong> biological <strong>in</strong>vasions…Of species used for agr<strong>of</strong>orestry aroundseven percent are said to be weeds undersome conditions, but around one percentare weedy <strong>in</strong> more than 50 percent <strong>of</strong> theirrecorded occurrences.”Evidence from across the world <strong>in</strong>dicatesthat agr<strong>of</strong>orestry projects have contributedto the ecological problems associated withalien <strong>in</strong>vasive species. News <strong>of</strong> impend<strong>in</strong>g‘fuelwood crises’ a generation ago ledto the creation <strong>of</strong> a large number <strong>of</strong> newagr<strong>of</strong>orestry projects across the develop<strong>in</strong>gworld <strong>in</strong> the late 1970s and early 1980s.While many <strong>of</strong> these projects undoubtedlycontributed to <strong>in</strong>creased energy supplies,they have also had negative consequencesfor welfare, biodiversity and water availability.Better design <strong>of</strong> the current generation<strong>of</strong> agr<strong>of</strong>orestry projects should help tom<strong>in</strong>imize negative impacts <strong>in</strong> the future. Forexample, ICRAF has adopted a policy thatfocuses on reduc<strong>in</strong>g the risk <strong>of</strong> <strong>in</strong>troduc<strong>in</strong>g<strong>in</strong>vasive alien species as part <strong>of</strong> newagr<strong>of</strong>orestry research and developmentprogrammes. We are also conduct<strong>in</strong>g researchon effective management <strong>of</strong> selected<strong>in</strong>vasive alien species. For example, ongo<strong>in</strong>gresearch on Prosopis juliflora <strong>in</strong>the Bar<strong>in</strong>go area <strong>of</strong> Kenya <strong>in</strong>dicates thepotential bene<strong>fit</strong>s and limitations <strong>of</strong> effectivemanagement through susta<strong>in</strong>ed use.Challenges for the future<strong>The</strong> overall conclusion that emerges fromthis review is that agr<strong>of</strong>orestry generallyproduces biodiversity bene<strong>fit</strong>s that are <strong>in</strong>termediatebetween monocrop agricultureand primary forests. <strong>The</strong> overall contribution<strong>of</strong> agr<strong>of</strong>orestry to biodiversity conservationdepends, therefore, on the type <strong>of</strong> land usethat it replaces and on the attributes <strong>of</strong> thespecific agr<strong>of</strong>orestry system. <strong>The</strong> effectiveness<strong>of</strong> agr<strong>of</strong>orestry <strong>in</strong> biodiversity conservationdepends on the design <strong>of</strong> the system and thenature <strong>of</strong> the biodiversity to be conserved.Agr<strong>of</strong>orestry is not a stand-alone approachto conservation. Rather, it needs to be seenas an element <strong>of</strong> conservation strategies,which also <strong>in</strong>clude policy and <strong>in</strong>stitutionalchanges, and spatial configurations that emphasizema<strong>in</strong>tenance <strong>of</strong> natural habitats.Additional research, <strong>in</strong>clud<strong>in</strong>g appropriatemeasurement, modell<strong>in</strong>g and
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CitationGarrity, D., A. Okono, M. G
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Enhancing Environmental ServicesCha
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viWorld Agroforestry into the Futur
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viiiWorld Agroforestry into the Fut
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Agroforestry and the Future
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Keywords:Millennium Development Goa
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Chapter 1: Science-based agroforest
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Chapter 1: Science-based agroforest
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Trees and Markets
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Keywords:Dacryodes edulis, Irvingia
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Chapter 2: Trees and markets for ag
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Chapter 2: Trees and markets for ag
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Chapter 2: Trees and markets for ag
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Chapter 2: Trees and markets for ag
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Chapter 2: Trees and markets for ag
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Keywords:Perennial tree crops, plan
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Chapter 3: The future of perennial
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Chapter 3: The future of perennial
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Chapter 3: The future of perennial
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Chapter 3: The future of perennial
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Chapter 3: The future of perennial
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Chapter 3: The future of perennial
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“Trees influence landscape scaled
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Chapter 18: Building capacity for r
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Chapter 18: Building capacity for r
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Keywords:E-learning, agricultural e
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Chapter 19: Can e-learning support
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Chapter 19: Can e-learning support
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Chapter 19: Can e-learning support
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Chapter 20Strengthening Institution
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Chapter 20: Strengthening instituti
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Author ContactsFahmudin Agusisri@in
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Acronyms and AbbreviationsACIARAFTP
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CreditsFront cover photo: Karen Rob
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World Agroforestry into the Future