Understanding CDM Methodologies - SuSanA
Understanding CDM Methodologies - SuSanA
Understanding CDM Methodologies - SuSanA
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No Additionality<br />
Problem<br />
Another common feature of projects using the three methodologies is that<br />
additionality is undisputed and no request for review has ever been launched<br />
on any of the registered projects on additionality grounds. The projects do<br />
(almost) not create any revenue in the absence of the <strong>CDM</strong> 220 .<br />
5.3.1 AM0001<br />
Project description<br />
HCFC-22 produces<br />
HFC-23 as<br />
Byproduct<br />
Host Country<br />
Regulation on<br />
HFC Destruction<br />
determines<br />
Baseline<br />
Only pre-2005<br />
Plants with<br />
3 Years of<br />
Operation before<br />
2005 are eligible<br />
No Destruction<br />
in an Another<br />
Country<br />
HFC-23 originates from the production of Chlorodifluoromethane (HCFC-22)<br />
which is used as a refrigerant and as a feedstock for the production of PTFE<br />
(Polytetrafluoroethylene also known as Teflon).<br />
In <strong>CDM</strong> projects using AM0001, the HFC-23 is prevented from entering the<br />
atmosphere by oxidization of the HFC-23 gas at very high temperatures in an<br />
incineration furnace before the stack.<br />
In the absence of any regulations HFC-23 is typically released to the<br />
atmosphere as it does not make economic sense to capture it. The amount<br />
of HFC-23 produced during the manufacture of HCFC-22 depends on two<br />
factors: the way the process is operated and the level of process optimization.<br />
Generally, the bandwith of HFC-23 emissions is on the order of 1.5 to 3 % of<br />
the HCFC-22 production. According to IPCC estimates, a reasonable average<br />
estimate is 2% (IPCC 2000). According to the methodology, the emission<br />
reductions are therefore the quantity of gas destroyed in the <strong>CDM</strong> project<br />
minus the emissions from the decomposition facility minus leakage.<br />
The project will usually require the installation of a HFC-23 waste gas<br />
collection facility, a storage facility (to buffer HFC-23 from the HCFC-<br />
22 production process), an incinerator (in most of the cases this will be<br />
natural gas-fired device), a cooling tower and a neutralization pond. The<br />
decomposition facility will produce a sludge that will need to be landfilled.<br />
Applicability conditions<br />
In the <strong>CDM</strong> projects using AM0001, an incinerator needs to be used to<br />
convert the carbon in the HFC-23 to CO2 which is then released through the<br />
stack of the plant. Production plants that started operation after 31.12.2004<br />
are not eligible to use AM0001 (see Box 17). The plant additionally needs<br />
to have an operating history of at least three years between beginning of<br />
the year 2000 and the end of the year 2004 and has been operated from<br />
the start of 2005 until the start of the <strong>CDM</strong> project. In case the host country<br />
requires the destruction of all the HFC-23 waste gas generated AM0001<br />
cannot be used. Offsite transport from the HCFC-22 production plant to<br />
another site is not allowed under the methodology (see Box 22)<br />
Box 22: Destruction of HFC in another country<br />
The Mexican “Quimobásicos HFC Recovery and Decomposition Project” (UNFCCC<br />
no. 0151) initially planned to destroy HFC-23 in an existing decomposition plant<br />
in the U.S. However, the EB decided that this is not covered under AM 0001 255 .<br />
The project developers therefore built the decomposition plant on their site.<br />
220<br />
Thermal decomposition projects can technically generate heat that might be used to generate steam for on-site<br />
use.<br />
221<br />
EB 22, para 27<br />
65