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ACTIVATED CARBON PROCESSES               14.5


         •  The AWWA  standard  for PAC  specifies a  minimum iodine number of 500.  Higher io-
           dine numbers  indicate greater  adsorbancy.
         •  Higher molasses  numbers  indicate greater  adsorbancy.
         •  Moisture  content  should  be  minimized and  should  not exceed 8%.
         •  AWWA  standard  specifies a  minimum  apparent  density of 0.25  g/cm 3.
         •  Ash  content,  which  is  an  impurity  that  reduces  adsorptive  capacity,  should  be  mini-
          mized.
         •  Smaller PAC particles adsorb organic compounds  more rapidly than larger particles,  so
          PAC  is manufactured  as  a  very fine powder.  Typically,  65%  to  95%  of commercially
          available PAC  passes  through  a  325-mesh  (44-/zm)  sieve.


         Selecting  a  PAC  Application  Point
        PAC  is primarily  used  to  control tastes  and  odors.  Important  factors  that  should  be  con-
         sidered  in selecting a  PAC  application  point include  the  following:

         •  The  contact  time between  PAC  and  organics  in the  source  water  is  important  and  de-
          pends  on the ability of the carbon to remain in suspension.  Providing a minimum of 15
          min  of contact  time  is  generally  sufficient for  most  taste  and  odor  compounds.  Con-
          siderably  longer contact times  may  be needed  for  2-methylisoborneol  (MIB)  geosmin
          removal.
        •  The  surface  of  PAC  particles  should  not  be  coated  with  coagulants  or  other  water
          treatment  chemicals  before  the  PAC  has  had  adequate  contact  time  with  the  source
          water.
        •  PAC  should  not  be  added  concurrently  with  chlorine  or potassium  permanganate  be-
          cause  PAC  will adsorb  these chemicals.  The best location for PAC  addition  is usually
          at  the head  of the  plant,  either  in  the  source  water  pipeline  or in  a  basin  dedicated  to
          rapid  or flash  mixing  chemicals.  Applying  PAC  at  the  earliest  point  in  the  treatment
          process  allows the  longest contact time possible  before the  application  of other chem-
          icals.  If PAC  must  be  added  later in  the  treatment  process,  dosages  may  be higher  to
          account for  shorter  contact times  and  interference  by  other  chemicals,  such  as  coagu-
          lants  and  chlorine.
           If  PAC  is  added  to  the  sedimentation  basin  effluent  or  filter  influent,  particular
        care  must  be  taken  in  filter  operation.  Because  of  its  small  carbon  particle  size,
        PAC  can  pass  through  a  filter and  cause  black  water  complaints  from  consumers.  An
        approach  used  by  some  systems  is  to  add  carbon  at  two  or  more  application  points,
        with part  of the  carbon  added  to the  source  water  and  smaller doses  added  before fil-
        tration  to  remove  remaining  taste-  and  odor-causing  compounds.  Table  14.2  summa-
        rizes  some  of the  important  advantages  and  disadvantages  of PAC  addition  at each  of
        these  points.
           PAC  is  increasingly  being  used  in  conjunction  with  microfiltration  or  ultrafiltration
        membrane  systems.  Not all membrane  filtration products  are compatible with PAC so the
        types  of PAC that  can be used may be limited.  Therefore, it is vital that  the use  of PAC
        be discussed  with the membrane  filtration  supplier when  considering  this  application.
           PAC  dosage  depends  on  the  type  and  concentration  of  organic  compounds  present.
        Common  dosages  range  from  2  to  20  mg/L  for  nominal  taste  and  odor  control,  but
        doses  can exceed  100 mg/L to handle  severe taste  and  odor episodes  or spills of organic
        chemicals.
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