Understanding CDM Methodologies - SuSanA
Understanding CDM Methodologies - SuSanA
Understanding CDM Methodologies - SuSanA
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Interpretation<br />
of top 20% in<br />
Approach 48 (c)<br />
Top 15% instead<br />
of top 20% used<br />
in First Approved<br />
Methodology<br />
using Approach<br />
48 (c)<br />
Box 10: ACM 13 modifies the approach 48 (c) and previous EB guidance<br />
In approach 48 (c), the emissions factor shall be 169 the lower of<br />
1. output-weighted average emissions of the top 20 per cent of similar project<br />
activities undertaken in the previous five years in similar circumstances<br />
2. output-weighted average emissions of similar project activities undertaken in<br />
the previous five years under similar circumstances that are also in the top<br />
20 per cent of all current operating projects in their category.<br />
No methodology was ever approved using that approach. The EB did apply<br />
this approach in the case of ACM 13 on greenfield fossil power plants, where<br />
the benchmark group was reduced to the top 15% performing power plants<br />
(excluding cogeneration plants and including power plants registered as <strong>CDM</strong><br />
project activities) among all power plants constructed in the previous<br />
5 years that have a similar size, are operated at similar load and use the same fuel<br />
type as the project activity.<br />
4.1.2 Baseline scenario definition<br />
Choice of Baseline<br />
Scenario has to be<br />
explained<br />
Baseline has to be<br />
Output-based<br />
Suppressed<br />
Demand Question<br />
The definition of the baseline scenario is a key step in any baseline<br />
methodology. Each methodology has to include an explanation of how the<br />
baseline is chosen 170 . The additionality test should show that the project is<br />
not identical with the baseline scenario 171 . As the baseline scenario should<br />
not grant CERs for decreases in activity levels outside the project activity<br />
or due to force majeure, the baseline should be defined on an output- or<br />
product-linked basis as an emissions factor per unit of output, at least when<br />
the project produces and sells an output. This has given rise to a discussion<br />
about whether in situations of suppressed demand, only that demand should<br />
be taken into account in determining the baseline activity level. The EB<br />
registered a project (Kuyasa low-cost urban housing energy upgrade project,<br />
Khayelitsha (Cape Town; South Africa), UNFCCC no. 0079) where the<br />
baseline is calculated on the basis of an activity level (indoor temperature of<br />
houses due to heating) that has increased due to the project.<br />
169<br />
EB 8, Annex 1<br />
170<br />
EB 8, Annex 1<br />
171<br />
Ibid. According to EB 17, para 16, additionality determination shall be consistent with the determination of a<br />
baseline scenario.<br />
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