Page 174 - Materials Chemistry, Second Edition
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158  3 Life Cycle Inventory Analysis

                      However, an LCA software cannot provide secure and adequate linkage of the
                    processes of the product system. The conductors of an LCA in general have to
                    correctly realize the logic of the product system before the actual calculation can
                    start. The user must not trust a software blindly. This is why the system check is
                    such an important step of the critical review procedure (see Section 5.5).


                    3.7.6
                    Calculation of the Life Cycle Inventory

                    If the system is modelled adequately and all process data records are available
                    in sufficient quality, the LCI of the examined product system can be calculated.
                    Tables 3.12–3.19 show as an example the LCI of the system variant 1-l-beverage
                    carton with closure related to the fU. 196)
                      In this list both inputs and outputs are indicated as elementary flows. Remember,
                    elementary flows are defined according to ISO 14040 and 14044 Section 3.12 as
                        material or energy entering the system being studied that has been drawn from
                        the environment without previous human transformation or material or energy
                        leaving the system being studied that is released into the environment without
                        subsequent human transformation

                      As supplement to these defined elementary flows, the LCI results CED
                    (Section 3.2.2) and use of natural land are included.
                      Nearly all LCA studies make use of newly procured as well as generic data of
                    diverse origin. Since the designation of inputs and outputs may vary even for the
                    same substance, the same substance may occur with different designations in an
                    LCA, for example: hexafluoroethane or perfluoroethane or C F . If the calculation
                                                                   2 6
                    of an impact assessment is accomplished by means of a software, it must be
                    assured that all variants of the same substance are clearly assigned.
                      An LCI supplies much more data than used in the next phase, namely LCIA.
                    The reason is that the development of a scientifically justified transfer of LCI data
                    into impact indicators still does not allow a complete use of all LCI data (see
                    Chapter 4). It is thus even more important that the data of the LCI may not be
                    lost, for a retrieval of their information content within the interpretation phase
                    (see Chapter 5).
                      In Tables 3.12–3.19 the first step from LCI to LCIA is already represented, the
                    classification: The LCI parameters are assigned to the impact categories considered
                    in this specific LCA study serving as a praxis example (see also Section 4.6).









                    196) IFEU (2006) These detailed data have been provided for this book by courtesy of the IFEU.
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