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

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96<strong>World</strong> Agr<strong>of</strong>orestry <strong>in</strong>to the Futureamong liv<strong>in</strong>g organisms from all sources,<strong>in</strong>clud<strong>in</strong>g, <strong>in</strong>ter alia, terrestrial, mar<strong>in</strong>e andother aquatic ecosystems, and the ecologicalcomplexes <strong>of</strong> which they are part; this<strong>in</strong>cludes diversity with<strong>in</strong> species, betweenspecies, and <strong>of</strong> ecosystems.” Spatial andecological scales are therefore fundamentalconcepts <strong>in</strong> biodiversity studies. <strong>The</strong>UNCBD further def<strong>in</strong>es agrobiodiversity asbiodiversity that is important for agriculturalproduction, <strong>in</strong>clud<strong>in</strong>g crop and livestockgenetic diversity, wild biodiversity closelyassociated with domesticated species, andother wild biodiversity shar<strong>in</strong>g the resources.‘Wild biodiversity’ is biodiversity that hasnot been domesticated, while ‘domestication’is the dynamic process <strong>of</strong> how humansselect, improve, manage, propagate and<strong>in</strong>tegrate trees or other plants <strong>in</strong>to land usesystems. While ICRAF and its partners haveconducted a great deal <strong>of</strong> work on belowgroundbiodiversity (e.g. van Noordwijk etal. 2004), we concentrate here on abovegroundbiodiversity at the landscape scale,explicitly focus<strong>in</strong>g on the l<strong>in</strong>ks between theplant<strong>in</strong>g and management <strong>of</strong> trees by farmersand biodiversity <strong>in</strong> the landscape.Several def<strong>in</strong>itions <strong>of</strong> the term ‘agr<strong>of</strong>orestry’are used <strong>in</strong> science and practice. Leakey’s(1996) def<strong>in</strong>ition is used most frequently:“a dynamic, ecologically based, naturalresource management system that, throughthe <strong>in</strong>tegration <strong>of</strong> trees on farms and <strong>in</strong> thelandscape, diversifies and susta<strong>in</strong>s productionfor <strong>in</strong>creased social, economic andecological bene<strong>fit</strong>s.” Three aspects <strong>of</strong> thisdef<strong>in</strong>ition are important for the biodiversityvalue <strong>of</strong> agr<strong>of</strong>orestry. Firstly, agr<strong>of</strong>orestry<strong>in</strong>volves the deliberate <strong>in</strong>tegration <strong>of</strong> treeswith farms and landscapes, which mayhave direct and <strong>in</strong>direct effects on farm andlandscape biodiversity. Secondly, there aretrade-<strong>of</strong>fs and complementarities betweenthe social, economic, ecological and biodiversitybene<strong>fit</strong>s <strong>of</strong> agr<strong>of</strong>orestry comparedto other land use systems; <strong>in</strong>deed, thequantification <strong>of</strong> trade-<strong>of</strong>fs has been at theheart <strong>of</strong> the research agenda <strong>of</strong> the Alternativesto Slash and Burn (ASB) Programmecoord<strong>in</strong>ated by ICRAF (Tomich et al. 2001).Thirdly, while some agr<strong>of</strong>orestry practices<strong>in</strong> certa<strong>in</strong> circumstances contribute greatlyto diversification and susta<strong>in</strong>ability, thereare other circumstances where it contributesvery little.Propositions aboutrelationships betweenagr<strong>of</strong>orestry and biodiversityA number <strong>of</strong> recently completed reviewpapers suggest ways <strong>in</strong> which agr<strong>of</strong>orestrycontributes to the conservation and protection<strong>of</strong> biodiversity, <strong>in</strong>clud<strong>in</strong>g that <strong>of</strong> bothwild species and species more directlyrelated to agricultural production (B<strong>of</strong>fa1999; Buck et al. 2004; Cunn<strong>in</strong>gham et al.2002; McNeely 2004; McNeely and Scherr2003; Schroth et al. 2004a; van Noordwijket al. 1997). <strong>The</strong>se and other studies suggestfour key relationships between agr<strong>of</strong>orestryand landscape biodiversity.1. Agr<strong>of</strong>orestry farmers and systemsas promoters <strong>of</strong> plant diversityProposition: While modify<strong>in</strong>g naturalvegetation for their productive use, farmersdevelop and ma<strong>in</strong>ta<strong>in</strong> agr<strong>of</strong>orestrysystems that make substantial contributionsto biodiversity <strong>in</strong> multi-functionallandscapes.<strong>The</strong> proposition that agr<strong>of</strong>orestry will result<strong>in</strong> ‘substantial contributions’ to biodiversityis supported by a good deal <strong>of</strong> evidenceregard<strong>in</strong>g the diversity <strong>of</strong> tree and vascularplant species across a variety <strong>of</strong> landscapes,<strong>in</strong>clud<strong>in</strong>g those conta<strong>in</strong><strong>in</strong>g agr<strong>of</strong>orestrysystems. <strong>The</strong>re are important caveatsto the proposition, however: i) there arelarge differences <strong>in</strong> the biodiversity value<strong>of</strong> different agr<strong>of</strong>orestry systems; ii) some <strong>of</strong>the more diverse agr<strong>of</strong>orestry systems maybecome less diverse under high levels <strong>of</strong>population pressure; and iii) the commoditiesthat underp<strong>in</strong> many <strong>of</strong> the most diverseagr<strong>of</strong>orestry systems are subject to fluctuationsand decl<strong>in</strong>es <strong>in</strong> pr<strong>of</strong>itability whenadopted on a large scale.<strong>The</strong> ASB programme has evaluated the biodiversityassociated with a range <strong>of</strong> typicalland use types, <strong>in</strong>clud<strong>in</strong>g agr<strong>of</strong>orestry, thatare found at the frontiers <strong>of</strong> tropical forests<strong>in</strong> Southeast Asia, the Congo Bas<strong>in</strong>, and theAmazon Bas<strong>in</strong>. Methods used and resultsgenerated by this comprehensive set <strong>of</strong>studies are available on the ASB web page(www.asb.cgiar.org). Summary results arealso presented <strong>in</strong> Tomich et al. (1998) andTomich et al. (2001). In general the resultsshow that multistrata agr<strong>of</strong>orestry systemsconta<strong>in</strong> an <strong>in</strong>termediate level <strong>of</strong> plant biodiversitythat lies between primary forestsand monocrop perennials or field crops.For example, Murdiyarso et al. (2002) comparedthe number <strong>of</strong> plant species found <strong>in</strong>different types <strong>of</strong> land use <strong>in</strong> the Jambi area<strong>of</strong> central Sumatra. <strong>The</strong>y found that cont<strong>in</strong>uouslycultivated cassava had 15 speciesper 1.5-hectare plot, oil palm plantationshad 25 species per plot, rubber agr<strong>of</strong>orestshad 90 species per plot, while primary forestshad 120 species per plot.Gillison et al. (2004) found that complexagr<strong>of</strong>orestry systems and shade-grownc<strong>of</strong>fee both had much higher levels <strong>of</strong>biodiversity than simple sun-grown c<strong>of</strong>fee,although all c<strong>of</strong>fee systems had lower biodiversitythan primary or secondary forests.

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