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System desigri Rids  1 9 1


           4.2.4 Computed solutions
           For  the simple  scenario  given  in  Table  4.4, implementation  of  both  LM  and
           UMIST  software  provides  the same limiting  flow  rate,  corresponding  to  the
           theoretical limit. However, the networks proposed by the two different software
           packages differ (Figs. 4.12 and 4.13). Indeed, by allowing a variable flow rate
           through the process, the UMIST software Water, which allows both approaches
           (Le. fixed and non-fixed flow rates) projects flow rates lower then the limiting
           ones. Using the LM  WaterTarget'Q  software, based  on flow rates fixed at the
           limiting value, the individual flow rates in the processes  remain  the same. To
           achieve the same target flow rate, but constraining to a fixed process flow rate,
           WaterTargetD proposes a network where part of the effluent of Process 2 and 3 is
           recycled and used as influent for those processes (Fig. 4.12). As such the overall
           flow rates through all the individual processes remains constant. The network
           proposed by Water looks the same as the WaterTargetR one, although providing
           no recycling and thus allowing a reduced flow rate through the third process.
             This example shows that whether or not the flow rate through the process is
           constrained at a fixed value, the target minimum flow rate remains the same and
           both  software  tools  provide  a  possible  water  network  achieving  the  target.
           Moreover, when the results of  the optimisation indicate recycling of the outlet
           back to the inlet of the process, this suggests the possibility of lowering the flow
           rate through the process.
             Since the two approaches result  in a different network, the inlet  and outlet
           concentrations of  the individual processes will also differ  (Table 4.5). By  not
           constraining the individual process flow rates, lower inlet concentrations from
           the Water solution  are obtained  compared  to those  from  the fixed flow rate
           approach of  WaterTarget".  However,  since the final  effluent  is produced  by
           Process  3,  the  effluent  concentration  of  this  process  is  the  same  for  both
           approaches.


                   tth
                                          Process 1

                              0.23  tlh                  I

                   0,67 t/h               Process 2

                                   0,l t/h

                                   1.77 t/h
                             I            Process 3                 2,6? tlh


                                     1,33 t/h
                   Figure4.12  Networkproposed bg WaterTargetZ toachieve the target for example I
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