Page 41 - Materials Chemistry, Second Edition
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Key Issues in Conducting Life Cycle Assessment                  27

            feedstocks in this category may include perennial plants grown on degraded lands,
            crop residues, sustainably harvested wood and forest residues, double crops and
            mixed cropping systems, municipal and industrial wastes. These various feed-
            stocks and bioenergy products in LCA should be treated with proper allocation and
            recycling procedures to attribute environmental burden of multi-functional pro-
            cesses to their input or output flows.
              A multi-functional process is a unit process, yielding more than one functional
            flow including co-production, combined waste processing, and recycling. Co-
            production is a multi-functional process having more than one functional outflow and
            no functional inflow. Recycling is a multi-functional process having one or more
            functional outflows and one or more functional inflows. Combined waste processing
            is a multi-functional process having no functional outflow and more than one
            functional inflow. The most relevant multi-functional processes in bioenergy
            systems with reference to the types of input and output inventory are the first two
            cases as illustrated in Fig. 4. Guinée (2002) distinguishes two steps in solving the
            multi-functionality problem. The first concerns avoiding burden allocation in
            accordance with the ISO preference. This is done by specifying the system boundary
            to a unit operation level (e.g., individual machines) to reduce the number of multi-
            functional processes or by system expansion. It is accomplished by extending the
            analyzed product system to include additional functions related to the co-products or
            recycled wastes. The system then includes more than one functional unit. The term
            system expansion is sometimes used to refer to the substitution method. The second
            step concerns solving the remaining multi-functionality problems by allocation on
            the basis of mass, energy, or economic values. Further discussion on the procedure to
            deal with allocation procedures and system expansion can be found in Tillman et al.
            (1994) and Heijungs and Guinée (2007).
              If some waste streams from agriculture are used to make bioenergy products,
            how the waste was produced is not included in the inventory. It is assumed that its
            production is free of environmental burden. This, however, requires a clear dis-
            tinction between products and wastes. To distinguish products from wastes, the
            economic value of flows can be used as the determining factor. A product is a flow
            between two processes with a positive economic value, whereas a waste is a flow
            between two processes with a negative economic value (Guinée et al. 2009).
            However, there are quite a few cases where we do not know for certain if the price
            of an agricultural residue is positive or negative, especially when it remains within


                                                           Bioenergy product1*
                 Biomass product    Multi-output process   Bioenergy product2*
                 Other product         (co-product)
                                                           Waste


                 Biomass waste*     Input-output process   Bioenergy product*
                 Other product          (recycling)        Other waste

            Fig. 4 Relevant multi-functional processes in bioenergy systems (*= functional flows)
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