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3.3 Allocation  107


                                 400 kg iron ore



                                 Iron production
                  E : 1000 MJ                      300 kg slag
                   1
                                       100 kg pig iron

                                   Converter

                                       100 kg crude steel

                    : 300 MJ
                  E 2               Rolling
                                       100 kg sheet metal

                  E 3 : 200 MJ   Punching and       20 kg clipping/scrap
                                   moulding



                                  80 kg product

               3.3.4
               Allocation and Recycling for Open-Loop Recycling (COLR)


               3.3.4.1  Definition of the Problem
               OLR, contrary to CLR, represents a difficult case for allocations comparable to
               coupled production. 102)  We first have a look at two systems A and B. Note that
               the originally separated systems A and B are now contained in a common system
               boundary and connected by a box ‘collection, transport, upgrade’ (Figure 3.18). The
               reason is that for the production in system B, the product in system A after its use
               phase can be (fully or partially) used as secondary raw material. A and B now form
               one system and the problem is on how environmental burdens and resource uses
               to the subsystems are to be allocated – one of which is being investigated.
                By the small boxes (waste disposal of A) in subsystem A and (raw material
               extraction for B) in subsystem B it is suggested that a certain fraction of A despite the
               recycling has to be disposed as waste and a fraction from B has to be produced from
               primary raw material. Since product B is not recycled here – according to the model
               assumption – the process chain of B ends with the disposal. Generally of course,
               product B can also be employed for other products after use, collection, and so on.


               102) SETAC, 1991; Hunt et al., 1992; Society of Environmental Toxicology and Chemistry – Europe,
                  1992; Society of Environmental Toxicology and Chemistry (SETAC), 1993; Curran, 1996, 2007,
                  2008; Kl¨ opffer, 1996a; Ekvall and Tillman, 1997; International Standard Organization (ISO),
                  1998a; UBA, 2000; UBA, 2002; ISO, 2006b.
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