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144  Membranes for Industrial Wastewater Recovery and Re-use


          Table 3.27  Characteristics of dyeing effluents (Horning, 1978)
          Dye                Fibre          Colour  BOD   TOC   TSS   TDS   PH
                                            (ADW  (mg/l)  (mg/l)  (mg/U  (mg/l)
          Acid               Polyamide       4000   240   315   14   2028    5.1
          Mordant            Wool            3200   135   210   9    1086    4.0
          1:2 Metal complex   Polyamide       3 70   5 70   400   5   3945   6.8
          Basic              Acrylic         5600   210   255   13   1469    4.5
          Basic              Polyester       1300  1470  1120   4    1360    5.0
          Direct             Viscose        12 500   15   140   26   2669    6.6
          Direct (cooper treated)   Cotton    525    87   135   41   2763    5.0
          Reactive (batch)   Cotton          3890     0   150   32   12500   11.2
          Reactive (continuous)   Cotton     1390   102   230   9     691    9.1
          Azoic              Cotton          2415   200   170  387   10900   9.3
          Sulphur (continuous)   Cotton       450   990   400   34   2000    3.7
          Vat                Cotton          1910   294   265   41   3945   11.8
          Disperse (high temp.)   Polyester   1245   198   360   76   1700   10.2
          Disperse (Atmosf. dyeing)  Polyester   315   234   300   39   914   7.8
          Disperse           Polyester (carpet)   215   159   240  101   771   7.1
          Disperse           Polyamide (carpet)   100   78   130   14   396   8.3
          Disperse/acid/basic   Polyamide (carpet)   130   160   49  258   6.5
          (continuous)
          Disperse/acid/basic   Polyamide(carpet)   210   42   130   8   450   6.7
          (batch)
          Disperse/vat       Cotton/polyester   365   360   350   9   691    9.1
           (continuous)


          the  spiralling  costs  of  mains  water.  Guide  values  for  key  water  quality
          determinants are included in Table 3.28 (Mattioli et al., 2002), which includes
          process water quality data for three operational textile finishing plants in the
          Como and Prato textile production areas of  Italy. It is evident from these guide
          values that the water quality requirement  is less rigorous than that demanded
          for drinking water by European Union legislation, which additionally has to be
          bacteriologically  safe,  such  that  tertiary-treated  wastewater  is  apparently
           suitable for reuse (Section 3.1.7).


          3.3.4 Legislation

           USA
           The most important environmental regulation affecting the textile industry in
           the USA  is  the Clean  Water  Act.  In  1982 the US  Environmental  Protection
           Agency  (EPA) promulgated  effluent  guidelines  for  the  textile  manufacturing
           point  source  category.  The  Textile  Mills  Point  Source  Category  effluent
           guidelines are listed under 40 CFR (Code of Federal Regulations) Part 410. Part
           410  is  divided  into  nine  subparts,  each  applying  to  a  different  textile
          manufacturing  subcategory  as outlined below. Each subpart contains effluent
           limitations,  new  source  performance  standards  (NSPS), and  pre-treatment
          standards. The definition of  Subpart D for the woven fabric includes desizing,
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