Page 84 - Materials Chemistry, Second Edition
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7 Goal Definition                                                69

            results (Chap. 12). Often, several separate applications are intended in a study. For
            example, the intended applications of the results of the illustrative case on window
            frames in Chap. 39 were both to benchmark a new window design against three
            windows already on the market and to identify hot spots in the life cycle of the
            compared windows with the aim of guiding future impact reduction efforts.



            7.3  Limitations Due to Methodological Choices

            This aspect can be seen as a critical reflection of what the LCA results can and
            cannot be used for. If a study only covers climate change (often referred to as a
            “carbon footprint” study) it is, for example, important to stress that results cannot be
            used to claim a general environmental superiority of a studied product or conclude
            anything about its overall “environmental friendliness”. Also, if a comparative
            study disregards one or more life cycle stages, it is important to stress how that
            limits the interpretation of results. For example, a study comparing the production
            of 1 tonne aluminum to the production of 1 tonne steel from mining to ingot cannot
            be used to identify the environmentally soundest material for use in a car, because
            the density difference of the two metals leads to differences in the amount of metal
            used for the car body and differences in the car mileage (fuel consumption per
            kilometre), causing different environmental impacts in the use stage and finally also
            in the disposal stage. In the illustrative window frame case study (Chap. 39) a stated
            limitation of the study was that a site-generic LCIA approach was taken in spite of
            impacts being concentrated around Scandinavia, where the natural environments,
            for some impact categories, do not correspond to the global average (e.g.
            Scandinavian soils show a higher sensitivity to depositions of acidifying com-
            pounds). Note that the limitations stated here should only relate to the choices made
            in the goal and scope phases of an LCA (this chapter and Chap. 8). These choices
            all relate to the planning and use of an LCA. On the contrary, choices made during
            the inventory and impact assessment phases of an LCA (Chaps. 9 and 10) relate to
            unforeseen constraints and assumptions (for example with respect to data avail-
            ability) and must be documented at a later point in an LCA report, for example, in
            the inventory analysis part (Chap. 9) or in the interpretation part of a report (see
            Chap. 12).




            7.4  Decision Context and Reasons for Carrying Out
                 the Study


            This is an important aspect of the goal definition because it strongly influences the
            appropriate elaboration of a life cycle inventory (Chap. 9). First, the reasons for
            carrying out a study must be understood. The reasons should be clearly connected
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