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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 />

Figure 4-10 Flow diagram <strong>for</strong> acidification impact category.<br />

4.7.2 Criteria <strong>for</strong> Evaluation of this impact category<br />

Next to the general criteria described in Chapter 2, the main criteria ‗Environmental<br />

relevance‘ <strong>and</strong> ‗scientific robustness‘, have been specified by 9 sub criteria:<br />

Atmospheric fate <strong>and</strong> transport is considered.<br />

Only deposition of acidifying chemicals on l<strong>and</strong> is considered, while ocean is<br />

disregarded.<br />

For damages on biodiversity/bioproductivity, a fate sensitivity factor discriminating<br />

between sensitive <strong>and</strong> insensitive areas is considered.<br />

Sensitive areas include areas with limited buffer capacity, in addition to the areas at<br />

critical load (insensitive ones do not contribute).<br />

Sensitive areas consider areas above critical load, i.e. the magnitude of the deposition<br />

above critical load is considered.<br />

Acidification potential is considered at midpoint.<br />

Dose response model <strong>for</strong> biodiversity/bioproductivity is considered at endpoint.<br />

The model uses the latest data on (changes in) current emission levels.<br />

The model addresses temporal changes <strong>for</strong> future emissions.<br />

The table below presents the general <strong>and</strong> specific criteria <strong>for</strong> acidification identifying the<br />

minimum score to be met (threshold value) <strong>and</strong> the most relevant criteria <strong>for</strong> the impact<br />

category (importance).<br />

Table 4-5 General <strong>and</strong> specific criteria <strong>for</strong> acidification with threshold value <strong>and</strong> importance.<br />

ACIDIFICATION Check the following:<br />

Introduction<br />

Completeness<br />

of scope<br />

• Timeframe, discounting, etc.<br />

• Marginal (M) or Average (A) defined, if not described<br />

(ND)<br />

• Total number of individual substances covered by<br />

specific provided characterisation factors<br />

• The impact indicator covers the majority of impact<br />

mechanisms <strong>and</strong> relevant elementary flows <strong>for</strong> the AoP<br />

Human Health<br />

• The impact indicator covers the majority of impact<br />

mechanisms <strong>and</strong> relevant elementary flows <strong>for</strong> the AoP<br />

Natural Environment<br />

• The impact indicator covers the majority of impact<br />

mechanisms <strong>and</strong> relevant elementary flows <strong>for</strong> the AoP<br />

Natural Resources<br />

• The midpoint indicator is chosen in a way that all LCI are<br />

appropriately aggregated as early as possible in the cause<br />

effect chain<br />

• The characterization model is adaptable to spatial <strong>and</strong><br />

temporal explicit evaluation<br />

Threshold<br />

(Minimum<br />

score)<br />

B H<br />

Importance<br />

(H-N)<br />

4 Requirements <strong>for</strong> specific impact categories 58

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