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Sgsteni design aids  19 5

          acquainted  with  the  software:  it  might  be  deduced  that  altering  the  inlet
          concentration of  C2 to Process 1 is more beneficial, but the negative sensitivity
          for  C1  in  the  same  process  provides  an  indication  that  this  option  is  not
          beneficial.  Indeed,  changing C2  has no influence  in this case.) The bar chart
          representation for the inlet  sensitivity  accounts for  both the inlet  and outlet
          concentrations. The negative concentration indicated in the figure implies that it
          is beneficial to lower the inlet concentration, which results from an analysis of
          the outlet  concentration. Since the inlet  and outlet are coupled  the software
          advises a change in inlet concentration since this is more practical.
            In allowing the inlet concentration of C1 of Process 2 to increase up to 37.5
          ppm and the effluent concentration to 13 7.5 ppm, and concomitantly  allowing
          C1 in Process 3 to increase up to 200 ppm, WaterTargeP indicates a target of
          2.33 t/h. This value can, in this case, easily be explained using the graphical
          presentation  of  the UMIST  software. Indeed, according to Fig. 4.1 7 a target of
          2.25 t/h can be achieved for C1. However, this is not the overall target as the
          target set for C2 indicates a flow rate of 2.33 t/h, slightly higher then the one for
          C1.  Therefore  the  overall  target  is  2.33  t/h.  The  process  of  identifying  the
         minimum flow rate proceeds through an investigation  of  C2  (Fig. 4.18), and
          continues until no further adjustments to inlet and outlet  concentrations can
          usefully be made.
            In Figs. 4.19 and 4.20 water networks are presented for the WaterTargetR and
          Water  models  respectively.  The  fixed  flow  rate  approach  of  WaterTargetm
          again produces  a  network with internal recycles,  whereas Water proposes  a
          lower flow rate through the process. As stated above, the net result for the latter
          is a lower inlet concentration to the processes (Table 4.6) with, in the case of
          Process 3, a C1 value which is below the original value of  100 ppm compared
          with  a  value  of  121 ppm  obtained  from the WaterTarget@ analysis.  One  is


                                 hlet Semitii [$hr]flconc change]





                OB
                Iw
                om                                              I c2(ppmw
                om
                om                                              li  CI  {ppmwt)
                om
                401
                -om
                          -             N
                          1
                                         P
                          p             p
                    Figure 4.16  Bar chart representation after relaxation for Cl in Process 3
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