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The challenge of HIV/AIDS: Where does agroforestry fit in? - World ...

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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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