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                                    TABLE 3.10
                                    Typical Removal Velocity Values for Different Pollutants

                                             Primary pollutants            K 2uni,eff  (m/s)
                                    NO 2  → nitrates                          0.008
                                    SO 2  → sulphates                         0.019
                                             Secondary pollutants           k uni  (m/s)

                                    PM10                                      0.01
                                                                              0.01
                                    SO 2
                                    CO                                        0.001
                                    Heavy metals                              0.01
                                    PCDD/Fs                                   0.01
                                    Source: Data taken from Rabl, A. et al., Waste Manage. Res., 16(4), 368–388. 1998.


                             3.8 SOPHISTICATION IN LIFE-CYCLE IMPACT
                                 ASSESSMENT
                             Sophistication in LCIA has been an important topic for scientific discussion (Bare
                             et al., 1999; UNEP DTIE, 2003). Sophistication is considered to be the ability to
                             provide very accurate and comprehensive reports that reflect the potential impact of
                             the stressors to help decision-making in each particular case. In language more
                             consistent with recent ISO publications, the practitioners of LCA are faced with the
                             task of trying to determine the appropriate level of sophistication in order to provide
                             a sufficiently comprehensive and detailed approach to assist in environmental deci-
                             sion-making. Sophistication has many dimensions and, depending upon the impact
                             category in LCIA, may simulate the fate and exposure, effect, and temporal and
                             spatial dimensions of the impact. It has the ability to reflect the environmental
                             mechanism with scientific validity (Udo De Haes et al., 1999; Owens, 1997, Udo
                             de Haes, 1996; Fava et al., 1993).
                                Traditionally LCIA uses linear modeling, takes the effects of the substances into
                             account (but not their fate and background concentrations), and aggregates the
                             environmental consequences over





                                                         time
                                                        locations               “potential impact”

                                                        chemicals




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