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14.28                    CHAPTER FOURTEEN


         •  Number  and  size of valves required
         •  Structural  considerations

           For purposes  of determining  the  optimum  number  of contactors,  estimates  of capital
         costs should be developed for various contactor configurations.  A  plot of the relative cap-
         ital cost as a function of the number of contactors aids in selecting the best configuration.
           Perhaps  the  most  important  factor  in  the  design  of a  GAC  adsorption  facility is  the
         type  of  underdrain  system  to  be  used.  Underdrains  must  perform  several  important
         functions:
         •  Collect water  at a  uniform rate  to ensure  GAC retention  in the contactor
         •  Prevent binding  or plugging of the collection system
         •  Distribute  water evenly over the entire  contactor  area
         •  Provide uniform  fluidization of GAC  at  a  low backwash  rate  during  transfer  of spent
           carbon  out of the  contactors  so that  carbon  moves to the points  of discharge


         Common  Operating  Problems

         Operating  problems  encountered  when  activated carbon  is used  as a filter medium or ad-
         sorber  are  similar  to  those  found  with  most  rapid  sand  or  dual-media  filters.  The  most
         common difficulties faced in operating  a  GAC facility that  the designer should be aware
         of when  preparing  a  design  include

         •  Effectively monitoring the  carbon  bed  depth
         •  Properly  backwashing  the carbon,  as  carbon  bed  density  and  depth  can  change  during
           backwashing
         •  Removing carbon  from the contactors  and  storage  tanks
         •  Transporting  the carbon
         •  Regenerating  the  carbon
         •  Maintaining  a  good-quality contactor influent
         •  Controlling contactor flow rate
         •  Controlling biological activity in the carbon  adsorber

         Monitoring  the Carbon Bed Depth.  A  means  must  be  provided  for continuously  moni-
         toring and measuring the levels in all storage vessels, including contactor and storage tanks
         (virgin, spent,  and regenerated carbon).  The designer must recognize that  slurry concentra-
         tions  and  flow rates  change  during the filling process.  When  carbon  is placed in an adsor-
         ber,  it typically has  a  density  of approximately  90%  of the  apparent  density  for random-
         packed  graded  media.  When  a carbon  column is first backwashed,  density  decreases from
         approximately 90%  to approximately  83%,  resulting  in a permanent  expansion of 8%.
           An  8%  expansion  in  a  24-in.  (60-cm)  filter is only  1.9  in.  (4.8  cm)  and  does not pre-
         sent  any  major  operating  problems.  However,  an  8%  expansion  in  a  15-ft-deep  (4.6-m)
        carbon bed entails a permanent expansion  of 14 in. (35  cm). This can create a major prob-
        lem when  one is trying  to closely control  the  surface  elevation of a  deep  bed.
           The problem of controlling surface elevation of deep bed, graded media is complicated
        further  by  the  fact that  the  bed  also  compacts  during  operation.  The  same  15-ft (4.6-m)
        column  could  see a  compaction  of 5  to  15  in.  (13  to  38  cm).  If surface  wash  sweeps  are
        used,  they must be placed to accommodate this expansion  and contraction  of the bed.  As
        noted,  conventional  surface  wash  sweeps  are not recommended.
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