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The Challenge of Low-Carbon Development - World Bank Internet ...

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for Costa Rica for the period 2000–05 found that only0.4 percent <strong>of</strong> targeted landholdings would have experienceddeforestation in the absence <strong>of</strong> the program; similarfindings were found for earlier periods (Sánchez-Az<strong>of</strong>eifaand others 2007; Pfaff and others 2009). Sills and others(2008) find that PES recipients did not reduce deforestation,but increased reforestation. 4 It is possible that the PESscheme worked at a political level rather than at the plotlevel, by reinforcing decisions to stiffen penalties for deforestationand to market Costa Rica as an ecological touristdestination. Costa Rica’s deforestation rate declined to verylow levels by the late 1990s.Early programs targeted lands with littlerisk <strong>of</strong> deforestation, but program designshave since improved.In both countries, ongoing <strong>World</strong> <strong>Bank</strong>–supported programsare contributing to better targeting. One lessonlearned has been the need to incorporate better up-frontdesign for monitoring and evaluation in PES programs toallow more timely and reliable impact analysis. <strong>The</strong> RegionalSilvopastoral Project (see box 4.2) is an exemplary use <strong>of</strong>experimental determination <strong>of</strong> the impact <strong>of</strong> alternativepayment schemes and agr<strong>of</strong>orestry approaches on carbon,biodiversity, and farm pr<strong>of</strong>its. 5Bio<strong>Carbon</strong> FundLaunched in 2004, the Bio<strong>Carbon</strong> Fund provides carbon financefor projects that sequester or conserve GHGs in forestsand agro- and other ecosystems. <strong>The</strong> Bio<strong>Carbon</strong> Fundis mostly oriented to forest projects creditable under theKyoto Protocol: afforestation and reforestation. But it alsopays for credits generated from reduced deforestation andfrom soil carbon, which are not recognized under Kyoto.It is thus a prototype <strong>of</strong> REDD and other post-Kyoto proposedsystems.<strong>The</strong> Bio<strong>Carbon</strong> Fund has helped catalyzethe forest carbon market.<strong>The</strong> Bio<strong>Carbon</strong> Fund has helped catalyze the forest carbonmarket by contributing to the development <strong>of</strong> 3 <strong>of</strong> the 12approved afforestation/reforestation methodologies. <strong>The</strong>Bio<strong>Carbon</strong> Fund accounts for 5 <strong>of</strong> the 13 forestry projectsregistered with the CDM to date.Box 4.2<strong>The</strong> Silvopastoral Project: A Successful Demonstration<strong>The</strong> GEF/IBRD Regional Integrated Silvopastoral Approaches to Ecosystem Management Project (2002–08)—implemented in Colombia, Costa Rica, and Nicaragua—was designed to test the effects <strong>of</strong> payment schemes onthe adoption <strong>of</strong> conservation practices on cattle farms. <strong>The</strong> project, the outcome <strong>of</strong> which IEG rated as highlysatisfactory, identified a range <strong>of</strong> technical approaches in each country and tested four main categories <strong>of</strong>silvopastoral systems: forest plantations with livestock grazing; live fencing, wind protection shields, biologicalcorridors, and shade for animals; managed succession within silvopastoral systems; and intensive systems for cattleand other animal species.<strong>The</strong> implementation <strong>of</strong> these systems resulted in a large body <strong>of</strong> learning, including 70 reports, refereed journalarticles, and books about how to induce farmers to adopt biodiversity-friendly, carbon-fixing land uses. In somecases, technical assistance and credit are sufficient. In other cases, short-term payments are needed to coverfarmers’ initial investment costs, but not thereafter. However, land use changes that represent an ongoingopportunity cost for farmers require mid- to long-term payments for the environmental services being produced;those services could include watershed protection or secondary forest recovery in degraded pastures.Different combinations <strong>of</strong> silvopastoral practices have proven to yield varying internal rates <strong>of</strong> return; economicanalysis conducted in Esparaza, Costa Rica, revealed rates from 14 percent for a system with natural pasture anda fodder bank to 37 percent for a system with improved pasture and low tree density. Based on the attractiveness<strong>of</strong> a system to an individual farmer, some farmers may be willing to adopt certain systems even in the absence <strong>of</strong>short-term PES incentives.Lines <strong>of</strong> credit for scaled-up silvopastoral system implementation are now being made available through CostaRica’s Cattle Ranchers Association, Nicaragua’s Local <strong>Development</strong> Fund, and the Ministry <strong>of</strong> Agriculture in Colombia.However, it is unlikely that most farmers will be able to afford the high initial costs <strong>of</strong> introducing a new land usesystem or that credit will be able to be tapped across all farm households across varying silvopastoral applications.Additional and recurrent finance will be especially needed to promote investments in silvopastoral systems thatgenerate a high level <strong>of</strong> public environmental services compared to a more attractive private rate <strong>of</strong> return.Source: IEG.Beyond Energy: <strong>Low</strong>-<strong>Carbon</strong> Paths in Cities and Forests | 55

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