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Benchmarking and additional environmental information in ... - ANEC

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• Nature occupation/l<strong>and</strong> use<br />

• Human toxicity<br />

• Ecotoxicity<br />

• Injuries<br />

4.2.1 Normalisation of life cycle <strong>environmental</strong> impacts<br />

Three ways of present<strong>in</strong>g normalised results were described <strong>in</strong> the study by 2.-0<br />

Consultants, see 2.10.9.<br />

In the current study, the <strong>environmental</strong> impacts calculated by the LCI/LCAprocedure<br />

have been normalised by relat<strong>in</strong>g them to the annual contribution<br />

form an average consumer <strong>in</strong> the EU, i.e. the option not employed by 2.-0<br />

Consultants. This way of normalisation is one of the central elements <strong>in</strong> the<br />

Danish EDIP-methodology, allow<strong>in</strong>g for a comparison of which type of<br />

<strong>environmental</strong> impacts is of largest concern. For all impact categories, the<br />

results are reported <strong>in</strong> the same basic unit, the Person Equivalent (PE). For<br />

convenience, we have chosen to present the results <strong>in</strong> milli Person Equivalents<br />

(mPE), where one PE is equal to 1000 mPE.<br />

The Person Equivalent is an expression of the annual contribution of an<br />

average citizen to a given impact category, tak<strong>in</strong>g <strong>in</strong>to consideration also the<br />

geographical scale of the impact. As an example, for Global Warm<strong>in</strong>g Potential<br />

the global emissions of greenhouse gases (measured <strong>in</strong> CO 2 -equivalents) are<br />

distributed on the total amount of citizens on the earth. Detailed <strong>in</strong>ventories, e.g.<br />

from IPCC, are available for this purpose, <strong>and</strong> the result is that the average<br />

World citizen emits greenhouse gases correspond<strong>in</strong>g to 8700 kg CO 2 -<br />

equivalents per year. For acidification, which is considered to be a regional<br />

impact, the amount of acidify<strong>in</strong>g gases be<strong>in</strong>g emitted <strong>in</strong> the region of EU is<br />

calculated us<strong>in</strong>g the databases available <strong>in</strong> EMEP/CORINAIR emission<br />

<strong>in</strong>ventories published by the European Environment Agency 1 . Be<strong>in</strong>g a regional<br />

impact, the total emission of acidify<strong>in</strong>g gases (measured <strong>in</strong> CO 2 -equivalents) <strong>in</strong><br />

the EU are divided by the number of citizens <strong>in</strong> the same area, result<strong>in</strong>g <strong>in</strong> an<br />

average contribution of 74 kg SO 2 per person <strong>and</strong> year.<br />

It is remarked that the concept of us<strong>in</strong>g Person Equivalents for comparison <strong>in</strong> all<br />

essence is similar to benchmark concept developed by Niss<strong>in</strong>en et al, 2004,<br />

us<strong>in</strong>g the average daily per capita <strong>environmental</strong> impacts of the whole F<strong>in</strong>nish<br />

economy as a basis for the benchmark<strong>in</strong>g. Obviously, the background data<br />

differ (EU versus F<strong>in</strong>nish average impacts), <strong>and</strong> the background data have also<br />

been established <strong>in</strong> different ways. However, the basic <strong><strong>in</strong>formation</strong> conveyed by<br />

the two approaches is the same if it is taken <strong>in</strong>to consideration that10 milli<br />

person equivalents (mPE) is the same as one percent. In accordance with the<br />

EDIP-methodology we have chosen to report <strong>in</strong> mPE, but this unit is readily<br />

converted to percent by divid<strong>in</strong>g with 10.<br />

The average contributions (called the “normalisation references” or the “Person<br />

Equivalent”) for the selected impact categories are summed <strong>in</strong> Table 4. For<br />

more <strong><strong>in</strong>formation</strong>, please refer to the orig<strong>in</strong>al description of the methodology<br />

1<br />

See e.g. http://reports.eea.europa.eu/EMEPCORINAIR4/en/page002.html<br />

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