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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 />

Toxicity<br />

Bioaccumulation/magnification<br />

Effects on biodiversity<br />

Table 4-7 presents the general <strong>and</strong> specific criteria <strong>for</strong> eco-toxicity, 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 4-7 General <strong>and</strong> specific criteria <strong>for</strong> eco-toxicity with threshold value <strong>and</strong> importance.<br />

ECOTOXICITY Check the following:<br />

Introduction<br />

Completeness of<br />

scope<br />

Environmental<br />

relevance<br />

Overall evaluation<br />

• Timeframe, discounting, etc.<br />

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

(ND)<br />

Total number of substances covered by the provided<br />

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<br />

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

cause effect chain<br />

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

temporal explicit evaluation<br />

• Global geographical validity preferable, separate<br />

validity <strong>for</strong> Europe beneficial<br />

• The method is compatible with, or developed<br />

specifically <strong>for</strong>, the comparative assessment scope of<br />

LCA (e.g. factors do not include security factors /<br />

precautionary principle)<br />

• When empirical data is used, double counting is<br />

avoided<br />

The following critical parts of the environmental<br />

mechanism describing the cause-effect chain are<br />

included with acceptable quality:<br />

• Advection out of a region or of a continent is not<br />

considered a final loss.<br />

• Marine environment <strong>and</strong> coastal zone are differentiated<br />

• Influential fate processes are considered (classic -<br />

volatilization, deposition/sedimentation, intermittent rain)<br />

• The effect factors are derived from the average toxicity<br />

over all species instead of the most sensitive species<br />

• Direct effects on species diversity of toxicants are<br />

considered<br />

Threshold<br />

(Minimum<br />

score)<br />

B H<br />

B H<br />

C H<br />

C H<br />

C H<br />

Importance<br />

(H-N)<br />

4 Requirements <strong>for</strong> specific impact categories 70

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