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HIGH-RATE GRANULAR MEDIA FILTRATION           8.3

         be  maintained  below  1.0 ntu  at any  time and  below  0.5  ntu  4  h  into  a  filter run  to  avoid
         specific reporting and performance review action levels, based on continuous  monitoring.
         Reporting  and  filter evaluation action is required if two successive  15-rain individual fil-
         ter turbidity measurements  exceed 0.5 ntu after 4 h  of filter operation and  1.0 ntu or 2 ntu
         at  any  point  during  the  filter run.  Generally,  achieving the  required  turbidity  limits  will
         provide  2.5-1og  Giardia removal  credit,  2.0-log  virus  removal  credit,  and  2.0-log  Cryp-
         tosporidium removal  credit  for  conventional  filtration  systems;  and  2.0-log  Giardia re-
         moval credit,  1.0-log virus removal credit,  and  2-log Cryptosporidium removal credit for
         direct filtration  systems.  These credits  vary from  state  to  state,  so consultation  with your
        local regulators  is encouraged.
           Pilot investigations  and filter design must consider the filter's ability to achieve these
         standards  throughout the filter run. Filter-to-waste capabilities are not specifically required
        by drinking water regulations; however, their use is recommended to achieve compliance
        with individual filter turbidity  limits. A  short filter-to-waste period can  "set" or ripen the
        filter to reduce  spikes of turbidity  at the beginning of a filter run.  For DBP  standards,  the
        use of granular  activated carbon filters may be considered to enhance removal of organic
        DBP  precursors.  While  the  regulatory  limit  for  combined  filter effluent  turbidity  is  0.3
        ntu,  general industry  practice  is to maintain  filtered water turbidity  at less  than  0.1  ntu.


        Pretreatment
        Effective operation of a high-rate granular media filtration system requires pretreating the
        source water.  The  nature,  as  well as the quantity,  of suspended  material  in the pretreated
        water is critical to  filter performance.
           Unflocculated  water can be difficult to filter regardless  of the  type  of medium  in  use
        (Cleasby,  1972;  Hsiung,  Conley,  and  Hansen,  1976).  However,  the  work  of  Robeck,
        Dostal,  and Woodward  (1964)  with dual-media  filters showed that if the applied water is
        properly  coagulated,  filtration  at rates  of 4  or  6  gprn/ft 2 (10  or  15  m/h)  produces  essen-
        tially  the  same  filtered  water  quality  as  filtration  at  a  rate  of 2  gpm/ft 2 (5  m/h).  Subse-
        quent investigations have shown similar results for mixed-media filters (Laughlin and Du-
        vail,  1968;  Westerhoff,  1971;  Conley,  1972).  Recent  research  has  pushed  the  filtration
        rates  for deep-bed  filters  to  as  high  as  10 to  12  gpm/ft 2 (24  to  30  m/h);  however,  poly-
        mer filter aids  and  deeper  coarse bed  filters were required to  achieve these rates  and  the
        raw  water  quality  was  excellent.  Extended  pilot  studies  and  regulatory  consultation  are
        recommended  when  filtration rates  above 4  gpm/ft 2 (10  m/h)  are proposed.
           Chemicals used in conjunction with high-rate granular media filtration are limited pri-
        marily to metal  salts or cationic polymers  as primary  coagulants.  Primary  coagulants  are
        ideally fed into  rapid  mixing basins  preceding  flocculation.  Whether  clarification is  also
        required depends  on the quantity of suspended  solids, metals,  and algae in the source wa-
        ter.  Primary  coagulants  are  intended  to  produce  agglomerations  of natural  and  chemical
         solids.  Nonionic  or  anionic  polymers  are  often  added  with  the  coagulant  as  a  coagulant
         aid  to  assist  in  strengthening  and  growth  of  these  agglomerations  during  flocculation.
         These same polymers can also be added  as a filter aid to the filter influent water or to the
         washwater  to increase the  strength  of adhesion  between media  grains  and  floc in coarse-
        to-fine filters. Proper pretreatment and mixing is essential to filter performance,  especially
         at higher filtration rates  (AWWA Research Foundation,  1992).  Pretreatment may also in-
         clude  aeration  or  introducing  an  oxidant  if an  objective of water  treatment  is to  remove
         iron or manganese.
           A  filter  aid  polymer  can  improve  floc  capture,  provide  better  filtered  water  quality,
         and  increase  filter  runs  with  higher  head  loss  before  turbidity  breakthrough.  Filter  aid
        polymers  are  not  generally  used  with  fine-to-coarse  filters  because  they  promote  rapid
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