Page 196 - Materials Chemistry, Second Edition
P. 196

182                                               R.K. Rosenbaum et al.

                    Inventory results  Midpoint  Endpoint   Area of protection
                             Climate change               Human health
                             Stratospheric ozone depletion
                             Human toxicity (cancer or non-
                             cancer)
                             Particulate matter formation
                             Ionising radiation (humans and
                     Elementary flows  Photochemical ozone   Natural Environment
                             ecosystems)
                             formation
                             Acidification (terrestrial,
                             freshwater)
                             Eutrophication (terrestrial,
                             freshwater, marine)
                             Ecotoxicity (terrestrial,
                             freshwater, marine)

                             Land use
                                                          Natural resources
                             Water use
                             Resource use (mineral,
                             fossil, biotic)
            Fig. 10.2 Framework of the ILCD characterisation linking elementary flows from the inventory
            results to indicator results at midpoint level and endpoint level for 15 midpoint impact categories
            and 3 areas of protection [adapted from EC-JRC (2010b)]

            aggregation and contribution analysis of multiple impact categories are only pos-
            sible after applying normalisation and weighting.
              There are three frequent misconceptions related to that:

            1. Misconception: Applying normalisation, weighting and aggregation to midpoint
              indicator results is the same as calculating endpoint indicator results. Or in other
              words, midpoint indicator results that are normalised, weighted and aggregated
              into one impact score per AoP have the same unit as endpoint indicator results
              aggregated into one impact score per AoP. Therefore, both results are identical.
              Fact: Even though the unit of both aggregated indicators is the same, their
              numerical value and their physical meaning are completely different. They are
              not identical and cannot be interpreted in the same way.
            2. Misconception: Changing from midpoint to endpoint characterisation implies a
              loss of information due to aggregation from about 15 midpoints into only three
              endpoint indicators.
              Fact: Before aggregation is applied, endpoint indicators are constituted for the
              same amount of impact categories as on midpoint level, but not every impact
              category contributes to each AoP (e.g. mineral resource depletion does not
              contribute to human health impacts). Therefore, the same analysis of contribution
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