Page 272 - Materials Chemistry, Second Edition
P. 272

260   LIFE CYCLE ASSESSMENT   HANDBOOK

              materials from waste are shipped to foreign markets. In many cases, these sec-
              ondary markets are located in the East Asia region. While it is relatively straight
              forward to characterize transportation-related energy consumption and associ-
              ated emissions, data characterizing the energy and emissions for  manufactur-
              ing operations  in East Asia  is not readily available. This has been  recognized
              as perhaps being the biggest gap in knowledge  for completing LCAs for recy-
              cling (Kviseth and Tobiasson, 2011). Therefore, there is an implicit  assumption
              those manufacturing  facilities  have similar energy use and  emissions  profiles
              as North American   or European  manufacturing  facilities  where data  is more
              readily available.


              11.4.5   Time Scale  Boundaries

              Typically, waste  management  studies  focus  on  annual  waste  generation  and
              management    (tied  to  municipal  and  regional  waste  management  and  plan-
              ning) and therefore most LCAs for waste management    often  reflect a one-year
              time  boundary.  However,  for  landfills  emissions  occur  over  a  long  period
              of  time  after  waste  placement.  For  landfills,  the  time  boundary  is  typically
              extended  to  100 years  (or  more, or  less)  to  capture  emissions  over  time  and
              then apply those emissions to the current year being studied  so results among
              waste management alternatives are comparable.
                 LCA can be used  to  project  future  end-of-life  burdens  and  impacts. Waste
              tonnages,  composition,  and  other  aspects  (e.g.,  energy  prices,  recyclables
              prices, and compost product prices) can be altered to reflect changes over time.


              11.4.6   Key LCA Modeling Decision       Points

              As with any LCA, many decisions must be made in building an LCI/LCA      for
              waste management. Even in quantitative LCIs/LCAs, a combination    of factual
              data,  engineering  estimates,  proxies,  and  assumptions  are  used.  Estimates,
              proxies and  assumptions  allow  LCA practitioners  to  evaluate  systems  when
              factual  data  either  cannot  be  obtained  within  the  context  of  the  study  or  do
              not exist. Figure 11.5 provides a qualitative (and general) representation  of the
              level of significance  to LCA results and uncertainty for different  data elements
              by waste process.
                 Because  decisions  about  the  use  of  engineering  estimates,  proxy  data,
              and  assumptions   can  substantially  affect  study  results,  a  series  of  "what
              if"  calculations  or sensitivity analyses are often  performed  on the results  to
              examine  the  effect  of  making  changes  in  the  system.  A sensitivity  analysis
              will  temporarily  modify  one  or  more  parameters  and  affect  the  calcula-
              tion  of the results. Observing  the change in the results will help  determine
              how   important  the  assumptions  are  with  respect  to  the  results.  The  com-
              putational  spreadsheet  is  also  used  to  perform  these  sensitivity  analysis
              calculations.
                 In addition  to what  type  of  data  is both  available and  needed  to meet  the
              goals  of the LCA, additional, and  key, decision points might include:
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