Page 97 - Materials Chemistry, Second Edition
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LIFE CYCLE IMPACT ASSESSMENT      79

              is interesting to note that the lifetime of LCIA methodologies (time elapsed
              between two releases) has varied between 5 to 10 years. On one hand, this
              reflects the high effervescence of research in LCIA over the last two decades,
              which led to rapid methodological development. On the other hand, it also
              reflects that LCIA is still in its infancy.
                From a practical point of view, any given LCIA methodology older than 10
              years is no longer likely to reflect the state of the art, thereby, showing seri-
              ous methodological weaknesses. LCA practitioners should avoid using older
              methods without at least checking the robustness of the results and conclu-
              sions by performing a sensitivity analysis with a more recent methodology.
                In the early 1990's, three methodologies were published that formed the
              basis of three main schools of thought that influenced the subsequent develop-
              ment of LCIA:


                   • Damage-Oriented (Area of Protection): The EPS (Environmental
                      Priority Strategies) methodology is based on a damage oriented
                      modeling approach and expresses results in monetary values.
                      First published in 1993 an updated version has been released in
                      2000 (Steen 1999). Category indicators are chosen to represent
                      actual environmental impacts on five safeguard subjects: human
                      health, ecosystem production capacity, biodiversity, abiotic
                      resources, and recreational and cultural values. Weighting factors
                      for the category indicators are determined according to people's
                      willingness to pay and expresses the price the society is ready to
                      pay in order to avoid these damages.
                   • Distance-to-Target: The Swiss Ecoscarcity (or Ecopoints) approach
                      is based on the distance-to-target principle. A first version was
                      published in 1991and has successively been updated to 1997
                      (Brand, Braunschweig et ah 1997). Eco-factors were originally
                      developed for Switzerland using the latest available statisti-
                      cal data and the supported goals of Swiss environmental policy
                      which set critical flows.
                   • Midpoint-Oriented: In 1992, the Centre of Environmental Science
                      (CML) at Leiden University produced a Guide and Background
                      document on the LCA methodology, known as the CML 1992
                      methodology (Heijungs, Guinee et al. 1992). This was the first mid-
                      point-oriented LCI methodology. Updated in 2002, CML claimed
                      to provide best practices for operationalizing the ISO14040 series
                      of Standards (Guinee, Gorree et al. 2002).

                The knowledge gained in developing these three methodologies formed
              the basis of LCIA methodology as it evolved. Following are brief descriptions
              of the main LCIA methodologies that are currently used (Bare and Gloria
              2006). Additional information on these approaches can be found in the ILCD
              background document that analyzes existing environmental impact assess-
              ment methodologies for use in LCA (EC-JRC 2010).
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