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ACTIVATED CARBON PROCESSES              '14.'13

         hausted.  Breakthrough curves are important to the designer because they define the rela-
         tionship between the physical and chemical parameters  of the  carbon system  (e.g.,  flow
         rate, bed size, carbon exhaustion rate), the determination of the number of beds or columns,
         their arrangement (either series or parallel), and treatment plant effluent requirements.
           EBCT.  EBCT is calculated as the volume of the empty bed (occupied by the GAC)
         divided by the volumetric flow rate of water through the carbon. Alternatively, EBCT can
         be defined as the depth  of GAC divided by the linear velocity of water flowing through
         the carbon bed. Note  that EBCT is a false-residence time.
           EBCT is used instead of detention time because of the ease  of calculation. An actual
         detention time would have to account for the porosity of the bed, a variable that changes
         with  carbon  size  and type.  EBCT  can be  varied by  changing the  bed  depth  at  constant
         flow  or by changing flow  with  constant bed depth.  Together,  the  design EBCT  and the
         design flow rate define the amount of carbon to be contained in the adsorption units.
           Longer EBCTs  can  delay  breakthrough  (to  a  point)  and improve  carbon usage  rate;
         shorter EBCTs can expedite breakthrough.  Thus the time of GAC operation between re-
         placement or regeneration depends on the EBCT.  For most water treatment applications,
         EBCTs range between 5  and 25  min. In addition, a  factor having a  greater  influence on
         operating costs  than EBCT  is volume throughput,  which  is the number of bed  volumes
         of water processed before the breakthrough concentration is reached.
        Adsorber  Volume  and Bed Depth.  After the  EBCT has  been determined,  carbon vol-
        ume and bed depth can be selected. The adsorber design volume depends on bed volume
        and the amount of freeboard (excess vessel capacity beyond design operating levels). Free-
        board can range up to  about 50%  for fixed and expanded bed systems.  If bed expansion
        is unnecessary, a freeboard of 20%  to  30%  may be adequate to allow for proper bed ex-
        pansion during backwashing.
           No  freeboard  is  needed  for  upflow  pulsed  beds.  An  economic evaluation is  usually
        made of capital and operating costs to compare carbon columns of various depths.

        Surface Loading Rate.  The surface loading rate for GAC filters is related to the design
        flow  of a particular treatment plant.  Surface loading rates  are defined in the  same man-
        ner as  for  conventional granular media filters.  The  surface  loading rate  is  the  rate  of  a
        volume of water passing through a given area of GAC filter bed, usually expressed as cu-
        bic meters per square vector (m3/m 2) or gallons per minute per square foot (gpm/ft2). Sur-
        face loading rates for GAC filters range from 2 to 10 gpm/ft 2 (5 to 24 m/h), although rates
        of 2 to 6  gpm/ft 2 (5 to  15 m/h) are more commonly used as design criteria.
           Surface loading should be kept high for those compounds where the mass transfer rate
        is  controlled by  the  rate  of transfer of the  chemical from the  bulk liquid to  the  interior
        pores of the GAC. Typically this is the case for highly adsorbable compounds (e.g., many
        SOCs).  When mass transfer is controlled by the rate of adsorption (and transport) within
        the  GAC  particle,  surface  loading  is  not  important.  This  is  the  case  with  most  less-
        adsorbable compounds, Figure 14.4 illustrates the relationship between hydraulic loading
        and pressure drop for several brands of GAC.
        Backwashing Requirements.  A  GAC filter bed is backwashed using the  same general
        procedures typically used for backwashing conventional granular gravity filters. If GAC
        is  installed as  a  sand filter replacement,  a  redesign of the  backwash  supply  system,  in-
        cluding the  rate  of flow  control and washwater  troughs  height,  is often necessary.  This
        redesign  is  necessary  because  of  the  difference  in  particle  density  between  GAC  and
        sand---about 1.4  and 2.65  g/cm 3, respectively.  If GAC  is used  as  a  simple replacement
        for anthracite coal as a filter medium and the granular sizes are similar, the backwash sys-
        tem may be adequate because particle densities are nearly identical.
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