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120  Membranesfor  Industrial Wastewater Recovery and Re-use









                                                   Dehydrator
                                    Backnsshable
                                            1
               San  mer


              ~
                                               Filtered
                                              water lank
         Figure 3.22  Schematic flow sheet of  a paper mill spiral-wound  nunofiltration process (Lien and Simonis.
         1995), Osmonics, Inc.


         (New Logic  Int.,  2002; Johnson, 2002) and  as well  as  recycle mill  effluent
         treatment (Monroe, 1997; New LogicInt., 2002).

         Bench- and pilot-scale research
         As already mentioned, implementation of membrane technology within the pulp
         and paper industrial sector accelerated in the early 1990s, with the development
         of  less  expensive  membrane  materials,  more  robust  modules  and  more
         sophisticated technologies such CR and VSEP filters. A concomitant acceleration
         in research activity took place at this time, focused on the treatment of bleaching
         effluents and the closing of  a bleaching plant water cycle (Jonsson et al.,  1988;
         Jonsson, 19  8 9; Jonsson and Petersson, 19 8 9; Afonso and de Pinho, 19 9 1 ; Luque
         et al.,  1994; de Pinho et al., 1995, 1998; Rosa and de Pinho, 1995; Geraldes and
         de  Pinho,  1995; Falth  et  al.,  1999, 2000, 2001a, 2001b). Another  area of
         interest  has  been  the  filtrates  and  circulation  waters  originating  from
         mechanical pulp production (Beaudoin et al.,  1992; Paleologou, 1994; Salovius
         et al., 1993; Konishi et al.,  1998; Edelmann, 2001). and paper mill white water
         and total effluent have also been intensively studied  (Nuortila-Jokinen, et al.,
         1995a, 1995b; Nuortila-Jokinen and Nystrom, 1996; Manttari and Takeshita,
         1997;  Nuortila-Jokinen,  1997;  Manttari  et  al.,  1997,  1998;  Kuide  and
         Yamamoto, 1999; Manttari et al., 1999; Huuhilo et al., 2001). Studies have also
         been conducted on the concentration of  coating colour effluents (Jonsson et al.,
         1996; Singh et al., 1997, 1999; Takeshita, 1997; Kuide and Yamamoto, 1999;
         Nuortila-Jokinen and Nystrom, 2000).
           Pulp and paper  mill process waters  and effluents have a very  high fouling
         propensity,  such  that  the  most  effective  membrane  material  for  these
         applications  seem  to  be  highly  hydrophilic,  almost  uncharged  regenerated
         cellulose.  For  the  coating  colour  effluents,  on  the  other  hand,  the  more
         hydrophobic  membranes  are  preferred  (Singh et  aZ.,  1997, 1999; Nuortila-
         Jokinen and Nystrom, 2000).
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