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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

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