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MODELING THE AGRI-FOOD INDUSTRY WITH LIFE CYCLE ASSESSMENT          161

              relevant impacts are relative to the stocks of the target and by-catch fish species
              and seafood habitats, but indicators are currently under development.
                 Nonetheless, the impacts related to the agri-food product system are of
              a very different nature compared to the traditional ones typically modeled in
              LC A, which raises many issues regarding the application of the LCA approach.
              For instance, agri-food systems require different considerations regarding the
              definition of the functional unit, the system boundaries, the allocation issues,
              the fertilizers and pesticides dispersion models, and the indicators for some
              impact categories. (Sleeswijk, et ah 1997). Today there are many different
              approaches, but there are no standardized methodological answers to these
              questions. Much has to be done to build a consistent, practical and life cycle
              science-based approach to product level sustainability information reporting
              for all food, beverage, and agriculture products. Moreover, the data quality
              of commercial databases for the agriculture and food systems remains, in our
              opinion, quite poor, hence the strong need to improve the quantity and quality
              of these databases.
                 In this chapter some of the typical methodological issues of agri-food LCA
              are highlighted by showing, through case studies, how they have been treated
              and managed. The starting point is the illustration of aspects regarding the
              choice of the functional unit and system boundary definition. Following,
              issues concerning the use of adequate fertilizer and pesticide dispersion models
              are addressed. Next, different land use and water use assessment approaches
              are analysed in relation to the agri-food sector. In the final part of the chapter
              the current LCA approach used by the food industry are critically analysed.




              7.2 Methodological Issues


              7.2.1 Choice of Functional Unit
              Choosing the functional unit is one of the very first critical tasks encountered
              during an LCA. The choice of the functional unit may vary according to the
              aim of the LCA study and may be determined in different terms such us func-
              tionality, nutritional value, portion size or other criteria. A functional unit is
              defined by the ISO 14044 norm as the "quantified performance of a product
              system for use as a reference unit" (ISO-14044, 2006b). In addition, the ISO
              14040 norm indicates that: "The functional unit defines the quantification of
              the identified functions (performance characteristics) of the product. The pri-
              mary purpose of a functional unit is to provide a reference to which the inputs
              and outputs are related. This reference is necessary to ensure comparability of
              LCA results. Comparability of LCA results is particularly critical when differ-
              ent systems are being assessed, to ensure that such comparisons are made on
              a common basis." (ISO-14040,2006a).
                It is important to define a suitable functional unit since the choice of differ-
              ent functional units is directly reflected on the results of the study which can
              be completely contradictory (Hischier & Reichart, 2003; Kim & Dale, 2006).
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