Page 72 - Materials Chemistry, Second Edition
P. 72

56  2 Goal and Scope Definition

                         An evaluation of the accuracy of data records is difficult, as process
                       data are usually not available with variants, error margins or standard
                       deviations. The evaluation is thereby essentially based on qualitative expert
                       knowledge. Therefore, for a descriptive evaluation of the data material,
                       available information such as, the average of a used technology, the year
                       of reference, and so on, has to be consulted. Thus, above all, information
                       is obtained on how representative the data are. Exceptions are packaging
                       specifications of the beverage cartons. Here, a mapping of qualified band
                       widths is possible.


                    2.3.2.8  Type of Life Cycle Impact Assessment
                    At this stage impact categories to be considered are already defined. From this
                    results the data set to be procured in the inventory analysis (see Table 2.1).


                       Table 2.1 Correlation of inventory parameters procured in the project and impact
                       categories (for explanation of the impact categories, see Chapter 4).

                       Impact category    Substantial LCI parameter a  Unit of category indicator

                       Resource demand  Crude oil, raw gas, brown coal,  kg of crude oil
                                        hard coal               equivalents
                       Land use         Spatial categories II–V  m 2
                       Greenhouse effect b  CO fossil, CH ,CH   kg CO -equivalent
                                          2       4  4              2
                                        regenerative, N O, C F ,CF ,
                                                      2 6
                                                           4
                                                  2
                                        CCl
                                          4
                       Eutrophication   NO ,NH 3                kg PO 4 3− -equivalent
                                          x
                       (terrestrial)
                       Acidification     NO ,SO ,H S, HCl, HF, NH ,  kg SO -equivalent
                                          x   2  2          3       2
                                        TRS
                       Photo smog ∼ ozone  NMVOC, VOC, benzene, CH ,  kg of ethene equivalents
                                                           4
                       formation (near  acetylene, ethanol,
                       surface)         formaldehyde, hexane, toluene,
                                        xylene, aldehydes unspecified.
                                                         +           3−
                       Eutrophication   P-total, CSB, N-total, NH 4  ,  kg PO 4  -equivalent
                       (aquatic)        NO 3 − ,NO 2 − , N unspecified
                       a The complete lists of inventory parameters considered in the example can be found in Sections
                       3.7 and 4.6 for illustration of the phases Inventory Analysis and Impact Assessment.
                       b The impact category ‘climate change’ is designated as ‘greenhouse effect’ in the example.
                       TRS, total reduced sulphur; NMVOC, non-methane volatile organic substances; VOC, volatile
                       organic compounds; CSB, chemischer Sauerstoff-Bedarf.



                    63)  Since in the examined systems ozone-destroying substances are not released in relevant
                        quantities, the impact category ‘stratospheric ozone depletion’ is omitted.
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