Page 206 - Materials Chemistry, Second Edition
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192                                               R.K. Rosenbaum et al.

              product system. As a general principle, the larger the reference system, the lesser
              the risk of such bias when normalising against the background activities of
              society.
            • While supporting comparison of results across impact categories, normalised
              LCA results cannot be interpreted as reflecting a weight or importance of one
              impact category relative to others. Normalisation helps to identify the impacts
              from the product system that are large compared to the chosen reference system,
              but large is not necessary the same as important. It is therefore not suitable as the
              only basis for identification of key issues/impacts in a product system, unless
              explicitly required by the goal and scope definition (e.g. evaluating the envi-
              ronmental impact contribution of a product system to a reference system which
              it is part of).
            • Unless (a) the reference system is global or (b) all environmental interventions
              of the product system assessed take place in the same region as those of the
              reference system, the direct interpretation of normalised impacts as contributions
              to or fractions of the reference system is misleading because parts of the life
              cycle of the product or service take place in different regions of the world,
              including outside the reference system.
              By expressing the different impact scores on a common scale, normalisation can
            also help checking for potential errors in the modelling of the product system. If the
            results are expressed in person equivalents, it is possible to spot modelling errors
            leading to extremely high or low impacts in some of the impact categories—like
            frequent unit errors when emissions are expressed in kg instead of g. Looking
            across the impact category results in a normalised impact profile, it is also possible
            for the more experienced LCA practitioner to check whether they follow the pattern
            that would be expected for this type of product or service.
              Although characterisation and aggregation at endpoint level leads to fewer im-
            pact scores (typically three), normalisation may still be useful with the same pur-
            poses as normalisation at midpoint level. The calculation and application of the
            endpoint normalisation references follows the same procedure as for midpoint
            normalisation, just applying combined midpoint and endpoint characterisation
            factors in Eq. 10.2.




            10.3.2 Weighting (and Aggregation)


            Weighting can be used to determine which impacts are most important and how
            important they are. This step can only be applied after the normalisation step and
            allows the prioritisation of impact categories by applying different or equal weights
            to each category indicator. It is important to note that there is no scientificor
            objective basis for this step. This means that, no matter which weighting method or
            scheme is applied, it will always be based on the subjective choices of one person
            or a group of individuals. Weighting can be useful for:
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