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Life cycle sustainability assessment in the energy sector  135


                 If system expansion cannot be performed—for instance, if the coproduct
              has no equivalent—then physical or economic allocation can be used. In such
              cases the impacts of the system are allocated to each coproduct based on
              mass, energy content, or economic value.
                 System expansion and economic allocation have disadvantages, primarily
              in their lack of consequentiality: in other words, the presence of a new pro-
              cess or industry with large volumes of a particular coproduct will have
              knock-on effects on the market, and these effects in turn may render the
              chosen substitution or economic allocation obsolete. In contrast, the phys-
              ical allocation approaches, such as mass or energy content allocation, do not
              face this problem. They may, however, fail to value the utility of the differ-
              ent coproducts.
                 The selection of an allocation approach has been shown to dramatically
              influence theoverall results of LCAs in thebioenergysector (e.g.,Stephenson
              et al., 2010). As a result, it is advisable to explore the importance of allocation
              choices by applying different types of allocation in a sensitivity analysis.



              2.5 Benefits, limitations, and weaknesses of LCSA
              LCSA yields a large quantity of data due to the need to perform a holistic
              assessmentacrossthethreepillarsofsustainability.Itisnotuncommonforsus-
              tainability frameworks to include 40 or more indicators (see, e.g., Roth et al.,
              2009; Stamford and Azapagic, 2011). Consequently, in cases where an LCSA
              isbeingusedtochoosebetweenalternatives,interpretingtheresultsisfarfrom
              trivial. Often the best option is not clear: perhaps trade-offs need to be made
              between indicators, or value judgment is required, or uncertainty is high.
                 UncertaintywithinLCSAcanbeexploredusingscenariosorsensitivityanal-
              ysis. In the former, the analysis is rerun using different underlying assump-
              tions: an approach explored further in Section 3. The challenge in that case
              is ensuring that the selected scenarios are truly reflective of the uncertainty
              space. In other words, scenario analysis should contain a sufficient breadth
              of scenarios to cover the entire likely range of possibilities. In the case of sen-
              sitivity analysis, one key parameter is varied at a time to explore the effect on
              the overall results of the LCSA. The chosen parameters should either:
              1.  Parameters that play a leading role in determining the impacts of the
                  system (e.g., the yield, capacity factor, choice of allocation approach,
                  use case of the product, etc.); or
              2.  Parameters that are highly uncertain due to poor input data or reliance
                  on assumption (e.g., lifespan of the system, costs or environmental bur-
                  dens of a major input material, etc.).
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