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Adapting to Climate Change: Assessing the World Bank Group ...

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APPENDIX HADDITIONAL EVIDENCEDrylands are defined (FAO/IIASA 2010) as having a growing period lengthof 60 <strong>to</strong> 180 days.Accessibility map, created by Siobhan Murray. Areas were classified asremote if <strong>the</strong>y were more than 5 hours travel time from <strong>the</strong> nearest city of100,000 or moreH2: Economic Value of Mangrove Coastal Protection BenefitsIEG examined 16 completed <strong>World</strong> <strong>Bank</strong> projects approved since 1990 of which 8identified coastal protection as a project impact (even if coastal protection was notnecessarily an objective or goal of <strong>the</strong> project). But <strong>the</strong>se projects provided littleevidence on <strong>the</strong> economic value of coastal protection benefits.In <strong>the</strong> cases where disaster risk reduction benefits were estimated, <strong>the</strong>y were forproject-wide benefits (which came primarily from dikes or o<strong>the</strong>r forest benefits)without a breakout for <strong>the</strong> mangrove component. In one case, <strong>the</strong> percentage ofdisaster damage that would need <strong>to</strong> be averted in order for project benefits <strong>to</strong> exceedcosts was estimated at 4.62 percent, but <strong>the</strong> likelihood that this target would besurpassed was merely asserted as “likely” without any fur<strong>the</strong>r analysis. In ano<strong>the</strong>rcase, <strong>the</strong> main economic analysis did not include “unquantifiable” protectivebenefits from mangroves, but a secondary calculation assumed mangrove values of$3,100-$3,800 per hectare (based on extrapolation from estimations used for o<strong>the</strong>r,unnamed regions). Where economic returns from afforestation benefits aremeasured, <strong>the</strong>se are usually due <strong>to</strong> economic benefits from aquaculture ra<strong>the</strong>r thanestimating <strong>the</strong> value of protective benefits. In some cases, attribution of projectimpacts on forest cover is also unclear, because <strong>the</strong> project overlapped with o<strong>the</strong>r(sometimes much larger) programs outside of <strong>the</strong> project aimed at supportingmangrove afforestation in <strong>the</strong> same region.A number of papers attempt <strong>to</strong> estimate <strong>the</strong> “<strong>to</strong>tal economic value” of mangroveand o<strong>the</strong>r wetland ecosystems, which includes direct benefits, option values, andexistence values. But most of <strong>the</strong>se focus primarily on forest goods and services(such as timber and fisheries), and many that estimate protective benefits usequestionable methodologies. For example, Gunawardena and Rowan (2005) use areplacement cost approach (“what would be <strong>the</strong> cost of building a physical coastalprotection system in this area, if mangroves were removed”) but fail <strong>to</strong> considerwhe<strong>the</strong>r it would be optimal <strong>to</strong> build such a system and without consideringwhe<strong>the</strong>r mangroves provide equivalent protective benefits <strong>to</strong> <strong>the</strong> proposed physicalbarriers. This method can thus dramatically overstate <strong>the</strong> protective benefitsprovided by mangroves. O<strong>the</strong>r papers (Ramsar Convention on Wetlands 2005) riskmisstating <strong>the</strong> benefits of coastal protection by calculating an average benefit per126

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