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ILCD Handbook: Framework and requirements for LCIA models and ...

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<strong>ILCD</strong> <strong>H<strong>and</strong>book</strong>: <strong>Framework</strong> <strong>and</strong> <strong>requirements</strong> <strong>for</strong> <strong>LCIA</strong> <strong>models</strong> <strong>and</strong> indicators First edition<br />

Photochemical ozone <strong>for</strong>mation Check the following:<br />

Applicability<br />

Overall evaluation<br />

Overall evaluation<br />

Overall evaluation of science based criteria<br />

Stakeholder<br />

acceptance<br />

criteria<br />

Overall evaluation of stakeholders acceptance criteria<br />

Final recommendation<br />

4.7 Acidification<br />

4.7.1 <strong>Framework</strong> <strong>and</strong> scope<br />

• Value choices are explicitly stated<br />

• Coverage of impacting single<br />

substance/resource elementary flows of the<br />

ELCD database (version October 2007)<br />

• Ease to update to con<strong>for</strong>m e.g. with the <strong>ILCD</strong><br />

nomenclature <strong>and</strong> units<br />

• The characterisation factors are straight<strong>for</strong>ward<br />

to apply <strong>for</strong> general LCA practitioners <strong>and</strong> in most<br />

market-relevant LCA software tools<br />

• Life cycle inventory figures <strong>for</strong> the distinguished<br />

emission compartments or resource types can be<br />

made directly available by producing industry<br />

• The indicator is easily understood<br />

• There is an authoritative body behind the<br />

general model principles like the IPCC model<br />

(consensus/international endorsement)<br />

• The principles of the model are easily<br />

understood by non-<strong>LCIA</strong> experts <strong>and</strong> preferably<br />

also by the general public<br />

• The covered elementary flows <strong>and</strong> impact<br />

<strong>models</strong> do not inappropriately favour or disfavour<br />

specific industries, processes, or products<br />

• The indicator is relevant with current policy<br />

indicators of the European Commission or similar<br />

international authoritative bodies<br />

Threshold<br />

(Minimum<br />

score)<br />

A H<br />

Importance<br />

(H-N)<br />

This impact category addresses the impacts from acidification generated by the emission<br />

of airborne acidifying chemicals. Acidification refers literally to processes that increase the<br />

acidity of water <strong>and</strong> soil systems by hydrogen ion concentration. It is caused by atmospheric<br />

deposition of acidifying substances generated largely from emissions of nitrogen oxides<br />

(NOx), sulphur dioxide (SO2) <strong>and</strong> ammonia (NH3), the latter contributing to acidification after it<br />

is nitrified (in the soil).<br />

The model framework <strong>for</strong> the acidification characterization factor is expressed as a fate<br />

factor, FF multiplied by an effect factor, EF as per the equation below:<br />

CFi,ar = FF · EF = fi,ar · θi,r sensitivity · βdose-response<br />

4 Requirements <strong>for</strong> specific impact categories 56<br />

H

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