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Industrial waters  12 1

           In addition to the membrane material, the module structure and the operating
         parameters  have  a  significant impact  on membrane process performance.  In
         general the higher the shear rate at the membrane surface, the higher the flux
         and the lower the fouling rate. The cross-flow velocity should exceed 4 m s-l
         (Jonsson and Wimmerstedt, 1985) in a tubular membrane and 3.2 m s-l  in flat
         sheet module to avoid fouling (Manttari  et al., 1998). As already stated (Section
         2.1.4), in the high-shear modules such as the CR and the VSEP filters the rotation
         speed and the vibration amplitude have a direct impact on the flux (Figs. 3.23
         and 3.24).
           The  concept  of  critical  flux  (Section  2.2.4)  has  been  introduced  for
         nanofiltration of pulp and paper waters by Manttari and Nystrom (2000), with
         respect  to  the  spiral-wound  DS-5DK  membrane  (Osmonics). The  efficacy of
         operation below the critical flux has been clearly demonstrated in the M-Real
         Kirkniemi case described in Section 5.6. Because the CR filters are operated at 0.8
         bar, which yields fluxes well below the critical flux (depends on the membrane
         and we have not measured  it in the  CR  only in the VSEP  and C30F) for the
         membranes, hardly any fouling has arisen for this plant. The membranes are
         washed only once a week as a part of  the routine operational procedure, rather
         than  on  demand.  The  VSEP  filter  operates  with  almost  no  fouling  in
         nanofiltration applications  (Fig. 3.2 5) whereas ultrafiltration membranes are
         usually readily fouled in the VSEP filter.
           The main foulants arising from diagnosis of membranes that have been used
         for the treatment of mechanical pulp and paper mill waters are resins, fatty acids
         and other wood extractives, sugars, and metal ion coagulated organic matter
         (Carlsson et  al.,  1998; Ramamurthy  et  al.,  1995; Nuortila-Jokinen,  1997;
         Huuhilo et al.,  2001). The adsorption of  such materials is increased at higher
         membrane hydrophobicities (Fig. 3.2  6).

                   300

                   250

                 = 200
                N
                 E
                   150
                 G
                 3
                 ii 100

                    50

                     0
                       0     60    120    180   240    300   360    420
                                          Time, min
         Figure 3.23  Eflect ofrotor blade tip speed in the CRfilter on thepermeateflux for thefiltration ofacidic clear
         filtrate from upapw machine. NF200 membrane from Dow-Film Tee, pH4.9,3 5°C 10 bar TMP
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