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

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Dedicated bus lanes have been shown toincrease travel speeds.In Bogota, CDM validation reports showed annual CO 2savings rising from 56,000 tons <strong>of</strong> CO 2e in 2006 to 79,000in 2009. Ridership increased from 346 to 449 million. <strong>The</strong>proportion <strong>of</strong> passengers attracted from private cars andtaxis fell from 9.8 to 6.9 percent.BRTSs <strong>of</strong>fer attractive economic returns infuel and time savings, reduced congestion,and reduced air pollution.In Mexico, the $47 million project is estimated to yieldannual noncarbon savings <strong>of</strong> $15.42 million (Schipper andothers 2009). About a third is from fuel and time savings <strong>of</strong>bus riders, and the remainder is external benefits from reducedair pollution, congestion, and fuel expenditure by others.Annual CO 2reductions were measured at 39,870 tons<strong>of</strong> CO 2for 2007–08. At current CO 2prices, these benefitsare small relative to the local economic benefits.ConclusionsBased on limited evidence, BRTSs <strong>of</strong>fer attractive economicreturns to cities as a whole in time savings, fuel savings, reducedpollution, and reduced congestion; the savings donot go directly to the implementing agency. <strong>The</strong> short-runreductions in GHG generate carbon credits that are modestin value compared to the direct local benefits. Single-lineBRTSs have little impact on overall urban CO 2emissions—for instance, the reductions in Mexico city are less than 0.25percent <strong>of</strong> urban emissions from transport (Schipper andothers 2009). In other words, these investments make a lot<strong>of</strong> sense as development interventions with CO 2cobenefits;they would never be chosen solely as means to reduce CO 2.In the medium run, there are likely to be declining returnsas the number <strong>of</strong> corridors increases within a city; but cumulativeemissions reductions for the system as a wholecould increase, to 250,000–400,000 tons <strong>of</strong> CO 2e per year.Long-term impacts could differ substantially; BRTSs couldbe a contributing component in the construction <strong>of</strong> efficientcities with low carbon footprints, if they are able to retaintheir share <strong>of</strong> passenger trips. Demand-side managementwill be an important part <strong>of</strong> such a scenario.Efficient transport planning will require a systems view forplanning and monitoring. Installation <strong>of</strong> a BRT corridorcauses ripples throughout the entire transport network aspeople change trip patterns and vehicles enter the system.Indirect impacts could magnify or counteract the corridorlevelbenefits; these need to be anticipated and tracked.Although CDM projects have the tremendous benefit<strong>of</strong> tracking ridership and fuel use, they typically do notmonitor systemwide travel patterns. This requires systemwidetravel surveys, which are expensive but informative.As the <strong>World</strong> <strong>Bank</strong> embarks on sponsoring BRTSs aroundthe world, it should take the opportunity to promote harmonizedmonitoring <strong>of</strong> impacts. <strong>The</strong> Clean TechnologyFund or other concessional funds could be used to mountregular, consistent travel surveys. This would allow correctmeasurement <strong>of</strong> impacts and could stimulate south-southsharing <strong>of</strong> experience and drawing <strong>of</strong> lessons.ForestsDeforestation accounts for roughly one-fifth to one-sixth <strong>of</strong>human-caused GHG emissions. Emissions result as forestsare cleared and burned to make way for farms and ranchesand to a lesser extent from damage caused by careless loggers.Most emissions are from tropical moist forests, wheredeforestation rates are high and biomass is dense.At CO 2values <strong>of</strong> $10–$20 per ton, forests are worth muchmore as living carbon storage than as sites for farms or forcattle ranches. Forests have additional value as havens forbiodiversity, and they play a role in regulating water flows.Nevertheless, forests are cut. Where land and forest tenureis well defined, landowners face strong incentives to liquidatestanding forests (rather than patiently harvest themover rotations <strong>of</strong> 30–100 years) and replace them with cashcrops, cattle, or fast-growing trees. In many forests, tenureis poorly defined, and people may use deforestation as amechanism to claim land as the approach <strong>of</strong> roads or marketscauses it to appreciate in value (Chomitz 2007).Forests can be worth more as living carbonstorage than as sites for farms or cattle ranches.In principle, landholders or nations would reduce deforestationif they were compensated for the local and globalbenefits their forests provide. This has motivated the REDDagenda, an element <strong>of</strong> ongoing negotiations on the internationalclimate regime. REDD seeks to mobilize global fundsto reward developing countries for reducing emissions.Countries would use these funds to implement programsand policies to promote sustainable land use.How, exactly, would that work? Although the forest carbonagenda is new, the forest conservation and managementagenda is not, and <strong>World</strong> <strong>Bank</strong> experience provides someparallels for potential future REDD actions.After briefly reviewing the <strong>World</strong> <strong>Bank</strong> forest strategy andportfolio, this section reviews three kinds <strong>of</strong> projects thatmay <strong>of</strong>fer lessons for REDD. By far the largest set <strong>of</strong> projectswith an explicit goal <strong>of</strong> forest conservation is protected areaprojects. A novel approach that closely resembles REDD ispayment for environmental services, a category <strong>of</strong> projects that52 | Climate Change and the <strong>World</strong> <strong>Bank</strong> Group

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