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L1644_C03.fm  Page 89  Tuesday, October 21, 2003  3:11 PM










                               TABLE 3.6
                               Comparison of Concepts for Weighting across Impact Categories
                                 Type of
                                concept     Description  Costs     Advantages     Disadvantages
                                   I      Selection of one   No  Simple application.  Parameter is only a
                                 Proxy     parameter for the                     bad approximation
                                           representation of                     of total impact
                                           the total impact
                                   II     Standard or     No    The reference value is   No accepted
                                Distance to   environmental      accepted if it exists  reference value for
                                 target    objectives                            comparison of
                                           established by                        different impact
                                           the authorities as                    categories
                                           reference
                                  III     Consideration of   No  Achievement of a   Result depends on
                                 Panels    the different         value that is   composition of the
                                           opinions of           accepted by a group  panel and/or
                                           experts and/or                        selected
                                           the general                           individuals
                                           society
                                  IV      Efforts to reduce   Internal  The efforts can be   Internalized costs
                                Abatement   pollution by         expressed by costs   do not correspond
                                technology  technological        that are known  to external costs
                                           means as
                                           reference
                                   V      Expression of   External  Attempt to estimate   External costs can
                               Monetization  environmental       the actual damage   only be estimated
                                           damages in            costs
                                           monetary values




                             mental priority strategies (EPS) (Steen, 1999) and in the uniform world model
                             (UWM; Rabl et al., 1998).
                                In addition to the weighting scheme used, single index approaches can be
                             differentiated according to whether impact potentials are the basis for the weighting.
                             For instance, this is the case for eco-indicator 95 and EDIP, but not for Tellus and
                             eco-scarcity, in which directly weighting factors are applied.
                                In the ongoing methodology development of LCIA, panel methods are increas-
                             ingly important; a tendency also exists to reflect the emission–effect relation more
                             accurately. In turn, proxy indicators “energy” and “mass displacement” (as a measure
                             of energy and resource intensity) and monetization methods based on damage or
                             abatement cost are also acquiring relatively increasing importance.
                                Next, the eco-indicator 95 will be further explained as a single index method.





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