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Science, Research and Development Working Group

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Title: Science, Research and Development Working Group


1
NON-FERROUS METALS CONSULTATIVE
FORUM ON SUSTAINABLE DEVELOPMENT
Science, Research and Development Working
Group Policy Aspects of Life Cycle
Assessment Sub Group Leader Dr Christian
Bauer The Hague, 25 November 2002
2
Conclusions from Oporto 2001
  • compile lessons learned
  • derive dos and donts
  • build bridges to ongoing initiatives
  • identify linkages within the science group and
    also amongst the working groups
  • How important is LCA to Sustainable Development ?
  • How is LCA used and misused in decision making ?

3
What was done ?
  • community Montreal (April 2002)
  • Life Cycle Initiative
  • SETAC (May 2002)
  • Ecobalance (Nov. 2002)
  • feedback on existing LCA-work
  • contacts to industry
  • summary paper on policy making, LCA and metals

4
Application of LCA as a tool
5
Strengths of LCA
  • LCA can manage a very detailed process level as
    well as considerations on services in general
  • LCA is useful for a multitude of decision-makers
    starting at the level of the designing engineer
    up to policy makers
  • LCA can aid decisions on any spatial and temporal
    scale (company level, community level, national
    level, short term, mid term, long term)

6
Chosing LCA as a tool
  • It is not always self evident in which cases to
    use LCA.
  • More appropriate tools may exist within a given
    decision context.
  • Not all stakeholders have a common understanding
    about when to use which tool.

7
Life Cycle Inventories
  • There is no universal life cycle inventory (LCI)
    which enables a multitude of decisions.
  • Each LCI is individually aligned to a specific
    decision context.

8
Life Cycle Impact Assessment
  • There is no universal Life Cycle Impact
    Assessment (LCIA).
  • Each case will vary e.g. in relation to the
    number of categories in the analysis and their
    definition.

9
Interpretation
  • There is no universal interpretation of LCA
    outcomes.
  • Each interpretation has to include additional
    information that cannot be expressed in LCIA.
  • One LCIA may have two or more valid
    interpretations when different spatial and
    temporal aspects are considered.

10
Relevance of life cycle stages E-Class
11
Recommendations
In order to strengthen the tool and its
application range further discussion across
stakeholders is necessary. Actions are
  • Establish linkages to other tools (Risk
    Assessment, Mass Flow Analysis, etc.)
  • Reach consensus on background systems (primary
    production but also recycling)
  • suggest appropriate impact indicators
  • translate and embed LCA into broader frameworks
    such as Product Stewardship
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