Page 327 - Materials Chemistry, Second Edition
P. 327

References  311


                 In Figure 4.5 REQ normalised results of considered impact categories are
                 represented.
                   The highest normalised indicator results for Germany occur for impact
                 categories fossil resource demand, greenhouse effect and land use. There is
                 a particularly large margin with regard to the remaining impact categories.
                   Taken by themselves the normalised results suggest that the results of
                 scenarios with respect to the impact categories fossil resources demand,
                 greenhouse effect and natural utilisation of space should be adequately
                 considered within an interpretation of the results. A special relevance of
                 these categories for a comparison of scenarios is also owing to large
                 absolute differences in REQs.

               4.6.6
               Weighting


                 ‘Weighting’ for LCAs including comparative assertions to be disclosed to the
                 public is not permissible in accordance with ISO 14040/44 and therefore not
                 included in this study.



               References
               Alcamo, J., Doll, P., Henrichs, T., Kaspar,  Spatial Planning and the Environment,
                F., Lehner, B., Rosch, T., and Siebert, S.  The Hague.
                (2003) Development and testing of the  Amiro, B.D. (1993) Protection of the
                Water GAP 2 global model of water use  environment from nuclear fuel waste
                and availability. Hydrol. Sci. J., 48 (3),  radionuclides: a framework using envi-
                317–337.                         ronmental increments. Sci. Total Environ.,
               Althaus, H.J., de Haan, P., and Scholz,  128, 157–189.
                R.W. (2009a) Traffic noise in LCA. Part 1:  Amiro, B.D. and Zach, R. (1993) A method
                state–of-science and requirement profile  to assess environmental acceptability of
                for consistent context-sensitive integration  releases of radionuclides from nuclear
                of traffic noise in LCA. Int. J. Life Cycle  facilities. Environ. Int., 19, 341–358.
                Assess., 14 (6), 560–570.      Atkinson, R. (1989) Kinetics and mech-
               Althaus, H.J., de Haan, P., and Scholz, R.W.  anisms of the gas-phase reactions of
                (2009b) Traffic noise in LCA. Part 2: analy-  the hydroxyl radical with organic com-
                sis of existing methods and proposition of  pounds. J. Phys. Chem. Ref. Data Monogr.,
                a new framework for consistent, context-  1, 1–246.
                sensitive LCI modeling of road transport  de Baan, L., Alkemade, R., and Koellner, T.
                noise emission. Int. J. Life Cycle Assess., 14  (2013) Land use impact on biodiversity in
                (7), 676–686.                    LCA: a global approach. Int. J. Life Cycle
               Amann, M., Bertok, I., Cofala, J., Gyrfas, F.,  Assess., 18 (13) Special issue, 1216–1230.
                Heyes, C., Klimont, Z., and Sch¨ opp, W.  Bachmann, T.M. (2006) Hazardous sub-
                (1999) Integrated Assessment Modelling for  stances and human health: exposure,
                the Protocol to Abate Acidification, Eutroph-  impact and external cost assessment at the
                ication and Ground-level Ozone in Europe,  European scale, in Trace Metals and other
                Publications Series Air and Energy, vol.  Contaminants in the Environment,vol.8,
                132, Netherlands Ministry for Housing,  Elsevier, Amsterdam.
   322   323   324   325   326   327   328   329   330   331   332