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ACTIVATED CARBON PROCESSES              14.25

         cannot be completely exhausted.  This prevents any contaminant breakthrough  into the ef-
         fluent that may cause  effluent water quality  standards  to be  exceeded.
           The performance of pulsed beds is affected by suspended  solids or biodegradable com-
         pounds  that cause extensive biofilm growth on the activated carbon,  so that the bed must
         be backwashed.  Backwashing  leads  to mixing  of the  fresh  activated  carbon  at the top  of
         the  bed  with  spent  activated  carbon  deeper  in  the  bed  and  destroys  some  of the  benefi-
         cial countercurrent effect. Additionally, some activated carbon fines may be produced dur-
         ing upflow that  may require removal by  a  subsequent  process.
           Another characteristic of the pulsed bed  system is that a  steady-state  constant  effluent
         concentration  (assuming  a  constant influent concentration)  is achieved. In fixed beds,  ef-
         fluent concentration  gradually  increases  with time.
        Adsorber  Design.  Various  adsorption  vessels  can  be  considered  by  the  designer.  The
        design depends on the size of the plant,  type of adsorber selected, mode of operation,  and
        number  of adsorber  units.  Adsorption  units  are  typically  cylindrical  steel  vessels  (pres-
        sure  or gravity flow) or cast-in-place  concrete rectangular  structures  (gravity flow only).
        The type of vessel used depends  on plant  size and  specific site constraints.  Basic charac-
        teristics  of typical adsorbers  are presented  in Table  14.6.  The  four fundamental  adsorber
        types  are
        •  Open-top  steel,  gravity flow
        •  Enclosed  steel,  gravity flow
        •  Enclosed  steel, pressure  flow
        •  Open-top  concrete,  gravity flow
           Treatment plants  of 10 mgd  (38 ML per day)  or less usually select pressure  steel ves-
        sels, although many designers prefer open-top beds to allow the operator to see the back-
        wash.  Larger  plants  usually have open-top  concrete tanks.  Other features  that  differenti-
        ate the individual adsorbers are the details of internal hardware,  such as liquid distributors
        and  collectors, carbon  bed  support  methods,  underdrains,  and  backwashing  apparatus.
           Adsorber  sizing is based  on flow rate,  hydraulic  loading,  and  EBCT.  These  variables
        determine the adsorber volume, depth,  cross-sectional area,  and number  of individual ad-
        sorber  vessels.  Once these quantifies  are known,  adsorber  design can proceed.

        TABLE 14.6  Basic Characteristics  of Adsorbers

         Adsorber  type   Material   Volume*  range,  ft 3  Diametert   Remarks
        Steel, gravity   Lined carbon   6,000 to 20,000   20 to 30 ft  Field-fabricated  by welding or
        flow        steel                            bolting  preformed  steel plate;
                                                     mounted  on concrete  slab
                                                     foundation
        Steel, pressure  Lined carbon   2,000 to 50,000   Up to  12 ft
                                                     Shop-fabricated;  over-the-road
        flow        steel; stainless
                                                     transportation  constraints  limit
                    steel                            size
        Concrete,   Standard   1,000 to 200,000  Usually
                                                     Field-constructed;  designs  vary;
        gravity flow   reinforced           rectangular   2:1 length-to-width  ratio is
                                                     common
          *To convert ft 3 to m 3, multiply by 0.0283.
          tTo convert ft to m, multiply by 0.3048.
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