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ION EXCHANGE  APPLICATIONS  IN WATER  TREATMENT   12.11

         rant  termination  of  the  service  cycle.  Therefore,  barium  removal  by  ion  exchange  is
         achieved by  ordinary  softening,  and  the process  is designed  as  an ordinary  softener.
           When  sulfate  is present,  barium  solubility  is  limited  to  the  parts  per billion  range.  If
         sulfates  are present  in the  raw  water,  it is  probable  that  barium  is present  only  as  a  sus-
         pended solid and therefore cannot be removed by ion exchange at levels above a few parts
        per billion.
           The  barium  form  of the  resin  is  more  difficult to  regenerate  than  the  hardness  form.
        Therefore  barium  will tend  to  accumulate  on the resin,  especially at  lower salt dose  lev-
        els.  During  the  initial  (first  time use)  exhaustion  cycle, barium  continues  to  load  on  the
        resin  after hardness  breakthrough  by displacing previously exchanged  hardness  (calcium
        and  magnesium)  ions.  Later,  when  the  resin  bed  is  regenerated,  the  barium  is  less  effi-
        ciently displaced  from  the  resin  than  the  hardness  ions.  The  ratio  of barium  to  hardness
        left  on  the  resin  after  regeneration  will be  substantially  higher  than  that  in  the  influent
        water. The barium will be pushed toward the bottom of the resin bed, where it could cause
        leakage in the next service cycle. The regenerant dose level should be high enough to pre-
        vent barium  buildup  in the resin  bed.
           If a  significant amount  of barium  is exchanged  onto  the resin  during  the  service cy-
        cle,  there  is  the  potential  for barium  fouling  from  precipitation  of barium  sulfate.  Ap-
        preciable  amounts  of sulfate  either in  the  dilution  water  or  in  the  regenerant  salt  itself
        will  cause  precipitation  of the  barium  in  the  resin,  which  will  foul  the  resin.  Barium-
        fouled  resins  can  be  cleaned,  but  the  cleaning  process  is  slow  and  involves  corrosive
        chemicals  such  as  hydrochloric  acid.  It  is  usually  necessary  to  use  external  vessels  to
        treat  the  fouled  resins  to  avoid  corrosion  of  the  softener.  In  any  case,  the  cleanup  of
        barium-fouled  resins  is  difficult  and  not  usually  practical.  One  method  of  cleaning
        barium-fouled  resins  is  to  soak  the  resin  bed  in  10%  hydrochloric  acid.  This  converts
        sulfates to bisulfates, which are more soluble. The process usually requires several hours
        and  vigorous  agitation  before  giving measurable  improvement.  It  is  often  less  expen-
        sive to  discard  and  replace  the resins  when  performance  drops  below  acceptable  levels
        due  to barium  fouling.

        Combined Softening  and Decationization.  Waters  containing hardness  and appreciable
        levels  of  alkalinity  can  be  partially  demineralized  and  fully  softened  by  having  two
        columns  of strong  acid cation resins  operated  in parallel.  One column is in the hydrogen
        form,  and  one is in the  sodium form,  the two  effluents  are blended  at a ratio determined
        by  the untreated  water  composition.  The  overall effect is  partial  demineralization,  alka-
        linity reduction, and softening. Through proper control of the blend ratios, the pH is main-
        tained  at acceptable  levels.

        Barium Removal by Hydrogen Form Weak Acid Dealkalizers.  Barium can also be re-
        moved  by  using  a  weak  acid  cation  resin.  The  resin  can be  used  in  either the  hydrogen
        or  the  sodium  form.  The  use  of weak  acid  resins  in  the  hydrogen  form  for  softening  is
        limited to removing hardness  associated with alkalinity. This process is usually employed
        for alkalinity reduction  and limited to waters  that have high hardness-to-alkalinity  ratios.
        The  effluent  will have  a  reduced  and  somewhat  variable  pH.  Initially  the  resin  will re-
        move all cations  in exchange for hydrogen and will produce  a very low pH. Very quickly
        the  resin  will cease  exchanging  for  monovalent ions  such  as  sodium.  Then  more  gradu-
        ally,  some alkalinity will start to  slip through,  eventually followed by hardness,  and  then
        barium.  The pH will rise gradually.  The reaction of the hydrogen form weak acid resin is
        usually limited to divalent cations  associated  with the alkalinity content of the water.  Al-
        kalinity  in the  water  will be  converted  to  carbon  dioxide,  which  is  a  gas,  by  the  hydro-
        gen  ions.  The  carbon  dioxide  will have  to  be  removed.  The  most  common  methods  of
        COz removal are  air stripping  and  deaerating  heaters.
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