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The Role of Sustainable Land Management for Climate ... - CAADP

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!<br />

Transaction costs can prohibit the viability <strong>of</strong> many projects, especially small ones. Most<br />

project developers responding to a recent study <strong>of</strong> the cost <strong>of</strong> AFOLU mitigation projects<br />

indicated that the cost <strong>of</strong> registering carbon units with the CDM were greater than $200,000,<br />

roughly twice the cost <strong>of</strong> certification in voluntary markets (Baalman and Schlamadinger 2008).<br />

According to the project developers interviewed, the high costs <strong>of</strong> CDM registration are due<br />

largely to the need to use expensive specialists to develop methodologies and project design<br />

documents, because <strong>of</strong> the complexity <strong>of</strong> the issues and procedures involved (Ibid.). Among the<br />

complex issues that must be addressed are the needs to show “additionality” <strong>of</strong> the investment<br />

(i.e., that it increases carbon sequestration relative to what would have occurred in absence <strong>of</strong> the<br />

project) and that “leakages” (shifting <strong>of</strong> carbon emissions to other locations as a result <strong>of</strong> the<br />

project) are avoided. Simplified procedures are allowed <strong>for</strong> addressing these issues <strong>for</strong> small<br />

scale projects (i.e., use <strong>of</strong> default values or assumptions to address them), but even so, the main<br />

methodology used <strong>for</strong> small scale A/R CDM projects typically requires completion <strong>of</strong> a 30 page<br />

document, comparable to large scale methodologies in other sectors (Ibid.). Besides the costs <strong>of</strong><br />

complying with such requirements, lack <strong>of</strong> availability <strong>of</strong> qualified experts to assist with<br />

developing project methodologies and plans, or to validate and verify project plans and<br />

implementation, can also be a major constraint, especially in SSA.<br />

Because many <strong>of</strong> these transaction costs are relatively independent <strong>of</strong> project size, they<br />

result in higher average costs per unit <strong>of</strong> emission reduction in smaller projects. According to<br />

one study, transaction costs <strong>of</strong> CDM projects range from $1.48 per tCO 2 e <strong>for</strong> large projects to as<br />

high as $14.78 per tCO 2 <strong>for</strong> small projects (Michaelowa and Jotzo 2005). With prices <strong>for</strong> CERs<br />

falling below 10 Euros ($12.70) in late February, 2009<br />

(http://www.carbonpositive.net/viewarticle.aspxarticleID=1472), it is clear that such high<br />

transaction costs make many potential CDM projects non-viable. As a result, few new CDM<br />

projects are being considered in the present depressed price environment (Ibid.).<br />

<strong>The</strong> problem <strong>of</strong> high transaction costs relative to CER prices is worse <strong>for</strong> A/R projects<br />

because A/R projects do not qualify <strong>for</strong> regular CERs, due to the impermanence <strong>of</strong> the emission<br />

reductions achieved (since planted trees may be cut or destroyed by fires). Two separate types <strong>of</strong><br />

CERs are applied to A/R projects, either a temporary CER (tCER) or a long-term CER (lCER).<br />

Current tCERs expire at the end <strong>of</strong> the current commitment period in 2012, while lCERs expire<br />

at the end <strong>of</strong> the project crediting period (e.g., 30 years) (Jindal, et al. 2008). Neither type <strong>of</strong><br />

!<br />

(&!

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