Page 377 - Materials Chemistry, Second Edition
P. 377

6.3 State of the Art of Methods  361

               6.3
               State of the Art of Methods
               6.3.1
               Life Cycle Assessment – LCA
                  Current practices in ecological risk assessment generally do a poor job of considering
                  biological and physical factors as most focus entirely or nearly so on chemical
                  effects. 21)

                LCA, as described in the first five chapters of this book, is the sole (‘one and
               only’) internationally standardised method of environmental-oriented analysis of
               product systems. The now relevant international standards ISO 14040:2006 and
               14044:2006 have been called The constitution of LCA by Finkbeiner. Two key issues
                                                                 22)
               determine LCA: the analytic view on the entire life cycle ‘from cradle to grave’
               and the functional unit, which allows the quantification of the benefit of goods or
               services (‘reference flow’). The original series of international standards ISO 14040
               to 14043:1997–2000 was replaced by the slightly modified standards ISO 14040 and
               14044:2006. 23)  The well-known structure – definition of goal and scope, inventory
               analysis, impact assessment and interpretation (see Chapter 1) – was developed
               by SETAC (1990–1993) and by ISO (1993–2000) in the course of harmonisation
               and standardisations. The standards provide strict requirements particularly for
               comparative assertions (see Chapter 5), which are to be publicly made available to
               prevent the abuse of LCA results. Thus LCA has reached a high level, and further
               progress will be adjusted more slowly. On the other hand, there are numerous
                                                             24)
               weak points and corresponding improvement opportunities, many of which have
               been discussed in the preceding chapters.
                Some of the weaknesses attributed to LCA can, however, only be removed with
               a loss of simplicity and robustness of the method. These are mainly related to the
               restricted resolution of location and time in life cycle inventory (LCI) and life cycle
               impact assessment (LCIA) (see Chapters 3 and 4). The way out of the world of
               potential impacts of classical LCA into a world of life-cycle based quantitative risk
               assessment is costly and implies new uncertainties. Other problem fields like, for
               example, the choice of allocation rules and system expansions could in principle be
               solved by conventions. 25)  Even the seemingly strict scientific metre convention and
               its modern successor ‘Syst` eme International des Mesures et Quantit´ es’ (Syst` eme
               International d’unit´ es, SI) 26)  is by no means scientifically superior to the obsolete
               US unit-system but ‘only’ more consistent and practicable. As there is still no
               international LCA society, 27)  SETAC would be the best suited forum to provide
               these conventions or at least activities for their preparation.

               21)  Anonymous in : SETAC Globe vol. 3(4) p. 59 (Ecological Risk Assessment section).
               22)  Finkbeiner (2013).
               23)  Finkbeiner et al. (2006).
               24)  Reap et al. (2008a,2008b) and Guin´ ee et al. (2011).
               25)  Kl¨ opffer (1998).
               26)  ISO (1981).
               27)  Kl¨ opffer (1997).
   372   373   374   375   376   377   378   379   380   381   382