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Understanding CDM Methodologies - SuSanA

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5.6 .3 ACM0008<br />

Description of the current version of the methodology<br />

Only Methane<br />

from operating<br />

underground<br />

Mines<br />

Collection<br />

and Transport<br />

Equipment for<br />

CMM<br />

NMHC Emissions<br />

only covered if<br />

more than 1% of<br />

CMM Volume<br />

Baseline Scenario<br />

Options<br />

Ex-ante Projection<br />

of CMM must be<br />

available<br />

Emission<br />

Reduction based<br />

on Difference of<br />

GWP of unburnt<br />

and burnt<br />

Methane<br />

Engineering Study<br />

for Methane<br />

Demand in<br />

Baseline Scenario<br />

or Statistical<br />

Projection based<br />

on 5 Year Data<br />

Applicability conditions: ACM0008 (version 03) is applicable to projects<br />

that capture and destroy coal mine methane (CMM) and/or extract coal<br />

bed methane (CBM) before mining at currently operating or newly built<br />

underground coal mines. It is not applicable to closed mines or to utilization<br />

of CBM from seams that will not be mined in the foreseeable future.<br />

Project boundary: The spatial extent of the project boundary includes the<br />

equipment installed and used for the extraction, compression, and storage<br />

of CMM and CBM at the project site, and transport to an off-site user, as<br />

well as flares or engines for electricity/heat generation, and the power plants<br />

connected to the grid serving the coal mine. Only CBM wells that are within<br />

a three-dimensional “zone of influence” of the mined area are part of the<br />

project. Within the project boundary, project participants shall only account<br />

for CO 2<br />

emissions from the combustion of non methane hydrocarbons<br />

(NMHCs), if they represent more than 1% by volume of the extracted coal<br />

mine gas.<br />

Baseline scenario and additionality: The baseline scenario is the most<br />

economically viable or the lowest emissions-intensive of the following<br />

options: venting, flaring, heat and power generation or feeding into gas<br />

pipelines. The option chosen also should not face prohibitive barriers and<br />

must be technically feasible to handle CBM and CMM to comply with safety<br />

regulations. Data must be available to provide ex-ante projections of methane<br />

demand over the crediting period and must be disaggregated according to<br />

the phases of methane recovery (CBM prior to mining, underground premining<br />

CMM drainage, surface or underground post mining CMM drainage,<br />

drainage from sealed goafs before the mine is closed).<br />

Additionality of the project shall be demonstrated by application of the latest<br />

version of the “Tool for the demonstration and assessment of additionality”<br />

(additionality tool) to the selected baseline scenario.<br />

Emission reductions: Methane venting releases 21 t CO 2<br />

per t of methane<br />

whereas combustion only releases 2.75 t CO 2<br />

per t of methane. Emissions<br />

from flaring are calculated according to the “Tool to determine project<br />

emissions from flaring gases containing methane”. Methane oxidation<br />

factors are taken from the Revised 1996 IPCC Guidelines for National<br />

Greenhouse Gas Inventories as 99.5% for heat and power generation and<br />

98.5% for feeding into gas grids.<br />

Methane demand for heat generation in the baseline scenario has to be<br />

estimated on the basis of an engineering/economic study describing the<br />

current distribution system, identifying CMM/CBM users, their consumption<br />

rates, expected growth rates of users and gas grid expansion plans. If there<br />

is no information on the existing distribution system, a statistical projection<br />

based on CMM/CBM availability and thermal energy CMM/CBM usage rates<br />

over at least the past five years can be used. If less than five years of data are<br />

available, the maximum existing pipeline capacity will be used as proxy for<br />

demand.<br />

103

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