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The Economics of Desertification, Land Degradation, and Drought

The Economics of Desertification, Land Degradation, and Drought

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Box 3.1—Recent major economic assessments <strong>of</strong> the environment<br />

Stern Review<br />

<strong>The</strong> Stern Review deals with the economics <strong>of</strong> climate change as a result <strong>of</strong> externalities from greenhouse gas<br />

emissions. Climate change leads to global consequences (<strong>of</strong>f-site effects) taking place over a long period <strong>and</strong> its<br />

analysis involves ethical dimensions, because the impacts <strong>of</strong> climate change are not equally distributed among<br />

countries, people, <strong>and</strong> generations. <strong>The</strong> economic analysis needs to take into account that impacts <strong>of</strong> climate<br />

change are long term <strong>and</strong> persistent, even irreversible, <strong>and</strong> are associated with uncertainties <strong>and</strong> risks. Results<br />

are therefore dependent on assumptions about plausible future emission scenarios, as well as on assumptions<br />

about technical progress <strong>and</strong> discount rates.<br />

<strong>The</strong> review has focused on the costs <strong>of</strong> mitigation to reach the stabilization <strong>of</strong> greenhouse gas concentrations in<br />

the atmosphere in the range <strong>of</strong> 450–550 parts per million <strong>of</strong> carbon dioxide, whereas the inaction path<br />

(“business as usual”) is associated with a temperature increase <strong>of</strong> 2–3 degrees Celsius. Costs <strong>of</strong> inaction are then<br />

estimated at an average reduction <strong>of</strong> at least 5 percent in global per capita consumption.<br />

Costs <strong>of</strong> mitigation are estimated at around 1 percent <strong>of</strong> the global GDP by 2050 on average, with a range <strong>of</strong> –2<br />

to +5 percent <strong>of</strong> GDP. Comparison <strong>of</strong> the costs <strong>of</strong> mitigation with the costs <strong>of</strong> inaction suggest that there is a net<br />

gain in taking action to mitigate climate change now rather than bearing its consequences. <strong>The</strong> social costs <strong>of</strong><br />

carbon are taken as $85 per ton <strong>of</strong> carbon dioxide, which is well above the marginal abatement costs in many<br />

sectors. <strong>The</strong> net present value suggests net benefits in the order <strong>of</strong> $2.5 trillion when implementing a strong<br />

mitigation policy in 2011. <strong>The</strong>re is a high price to delay taking action on climate change. As these findings show<br />

that strong action on climate change is beneficial, the second half <strong>of</strong> the report examines the appropriate form <strong>of</strong><br />

such policy <strong>and</strong> how to fit it in a collective action framework.<br />

TEEB<br />

TEEB provides ways to create a valuation framework for ecosystems <strong>and</strong> biodiversity in order to address the<br />

true economic value <strong>of</strong> ecosystem services by <strong>of</strong>fering economic tools. <strong>The</strong> analytical framework <strong>of</strong> a cost–<br />

benefit analysis must deal with the economics <strong>of</strong> risks <strong>and</strong> uncertainty. Crucial for any cost–benefit analysis is<br />

the setting <strong>of</strong> discount rates to make future losses <strong>and</strong> benefits comparable. Decisions on discount rates involve<br />

ethical dimensions; therefore, TEEB intends to present a range <strong>of</strong> discounting choices connected to different<br />

ethical st<strong>and</strong>points. TEEB reviews a number <strong>of</strong> studies concerning the costs <strong>of</strong> both biodiversity loss <strong>and</strong><br />

biodiversity conservation. Monetary values attached to biodiversity <strong>and</strong> ecosystems have <strong>of</strong>ten focused on case<br />

studies (area-specific) <strong>and</strong> on particular aspects <strong>of</strong> ecosystems or sectors. Assessing the consequences <strong>of</strong><br />

biodiversity loss <strong>and</strong> ecosystem services globally thus dem<strong>and</strong>s a globally comprehensive <strong>and</strong> spatially explicit<br />

framework <strong>and</strong> estimation grid for the economic valuation <strong>of</strong> ecosystems <strong>and</strong> biodiversity, combined with a<br />

meta-analysis <strong>of</strong> valuation studies. <strong>The</strong> key elements <strong>of</strong> Phase 2 <strong>of</strong> TEEB include the causes <strong>of</strong> biodiversity loss;<br />

the design <strong>of</strong> appropriate scenarios for the consequences <strong>of</strong> biodiversity loss; the evaluation <strong>of</strong> alternative<br />

strategies (“actions to conserve”) in a cost–benefit framework, including risk <strong>and</strong> uncertainties; a spatially<br />

explicit analysis; <strong>and</strong> the consideration <strong>of</strong> the distribution <strong>of</strong> the impacts <strong>of</strong> losses <strong>and</strong> benefits. <strong>The</strong> evaluation<br />

also largely relies on benefit transfer, because data cannot be collected for all kinds <strong>of</strong> ecosystem services <strong>and</strong><br />

biomes.<br />

From a society’s point <strong>of</strong> view, all costs <strong>and</strong> benefits (including externalities) that occur due<br />

to ongoing l<strong>and</strong> degradation need to be considered to result in the optimal “social” rate <strong>of</strong> l<strong>and</strong><br />

degradation. This includes not only on-site <strong>and</strong> direct costs that farmers experience in terms <strong>of</strong> lower<br />

yields, but also changes in the value <strong>of</strong> the benefits derived from all ecosystem services that may be<br />

affected; <strong>of</strong>f-site costs arising at other sites within the watershed, such as sedimentation; as well as<br />

indirect effects, such as economywide impacts, threats to food security, poverty, <strong>and</strong> other outcomes<br />

affecting the society. (See Figure 1.2 for a description <strong>of</strong> the various costs <strong>and</strong> how they are linked to<br />

externalities <strong>and</strong> social costs.)<br />

Government policies <strong>and</strong> other institutional factors can also lead to socially <strong>and</strong> privately<br />

nonoptimal rates <strong>of</strong> l<strong>and</strong> degradation. Imperfect or unenforced l<strong>and</strong> rights, distorted <strong>and</strong> volatile<br />

market prices, lack <strong>of</strong> information about future damages related to degradation, <strong>and</strong> imperfect or<br />

missing credit markets are among the factors that prevent farmers from investing in potentially<br />

pr<strong>of</strong>itable soil conservation measures. Anything that creates uncertainty about the future benefits <strong>of</strong><br />

conservation measures reduces farmers’ incentives to adopt them.<br />

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