Page 212 - Membranes for Industrial Wastewater Recovery and Re-Use
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System design aids  18 1






                               Chemical
                              r G Nme
                              ,
                              i  r Sulfutic Acid
                              '  1  r Hydrochloric Acid
                                f Sdim carbate
                                r Lme
                                r Sodm Hydroxide













                    Figure 4.5  Pretreatment dialogue box (ROPRO, Koch-Fluid Systems)


           0  reduction of the number of pressure vessels per bank whilst increasing the
              number of membranes per pressure vessel
           0  recycling of part of the concentrate
           0  decreasing the element size.

           (ii) Permeate  quality  changes  with  recovery.  In  principle,  solute  diffusion
         increases  with  higher  recoveries  but  permeate  flux  also  increases.  These
         synergistic phenomena  mean  that  permeate  quality  can  increase  until  some
         specific recovery value, beyond which it may decrease again. It is rarely the case
         that  the highest permeate water quality, as may be  demanded by,  for example,
         microprocessor applications, coincides with the highest recovery.
           (iii) The specific energy demand increases with increasing recovery.
           (iv) Calcium  carbonate  scaling  can  be  very  substantially  reduced  through
         pretreatment  by  acid  dosing  or  hardness  removal,  allowing  much  greater
         recoveries and thus demanding smaller membrane areas. Hardness reduction can
         be achieved by classical chemical softening, by ion exchange or lime dosing, or by
         blending the feedwater with some of the permeate product.
           (v)  Scaling  by non-hydrolysable scalants (Table 2.14) can be suppressed through
         the  use  of  appropriate  scale  inhibitors.  Dedicated  software from  anti-scalant
         chemical suppliers is available (Fig. 4.7) and can be used in parallel with the RO
         software to calculate scaling propensity of  the chemically treated water. Scaling
         from  these  contaminants  is  otherwise  reduced  only  by  their  removal  or  by
         reducing CP.
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