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12.10                     CHAPTER TWELVE

         costs  and  a  lower  waste  discharge  for  higher  equipment  costs;  these  will  be  discussed
         later.

         Ammonia

         Ammonia is a colorless gas that dissolves readily in water. It is commonly present in most
         water supplies  in trace quantities  as the ammonium ion due to degradation  of nitrogenous
         organic  matter.  It may  also be  present  due  to  the  discharge  of industrial  wastes.  Ammo-
         nia  reacts  with  water  to  form  ammonium  hydroxide,  which  dissociates  into  ammonium
         (NH4 +) cations  according  to the  following reaction:
                              NH3  +  H20  ~  NH4 +  +  OH-
                              NH4  +  (OH)  ~  NH4 +  +  OH-
         When  ammonia is present in concentrations  of a few parts  per million, the degree of ion-
         ization  of ammonia  is  a  function  of the  pH.  At  a  pH  below  8,  ammonia  is present  pri-
         marily  as  the  cationic  ammonium  ion.  At  a  pH  above  9.0,  ammonia  is  essentially  un-
         ionized and  is not efficiently removed by  salt cycle ion exchange.
           Strong  acid cation exchange resins,  such  as the kind  typically used  for softeners,  will
         exchange  sodium  for  ammonium  ions.  The  process  is  in  fact  a  standard  softener.  The
         cation  resin  has  a  higher affinity  for divalent  hardness  ions;  therefore  hardness  ions dis-
         place the ammonia,  which in turn  displaces  more sodium.  As the service cycle continues,
         the  hardness  ions  form  a  band  in  the  upper  portion  of the  resin,  and  ammonia  forms  its
         own band just beneath  the hardness.  Since ammonia removal is required,  ammonia is in-
         cluded  as an exchangeable ion along with the hardness  ions in sizing the system. The ser-
         vice cycle is ended  when  ammonia  levels in the  softened  water rise.  If the  service cycle
         is allowed to continue past  the  ammonia break,  the hardness  will continue  to load on the
         resin  and  displace  ammonia.  Ammonia  levels could  reach  concentrations  in the effluent
         equal  to the  total  hardness  plus  ammonia  concentrations  in the raw  water.  This could be
         much  higher than  influent ammonia  levels. When  this  occurs,  it is known  as dumping.
           Ammonia can also be removed by inorganic zeolites such as chabasite,  mordenite, and
         clinoptilolite. Some zeolites are more highly selective for ammonia than hardness  and are
         able  to remove it throughout  the  acceptable  pH  range  for potable  water  (6  to 9)  without
         the danger  of dumping.  Not having to remove hardness  gives them  very high throughput
         capacities  compared  to  strong  acid  cation  resins  for ammonia  removal  from  waters  con-
         taining  appreciable  levels of hardness.


         Barium

         Barium  is  an  alkaline  earth  metal  which  is  occasionally  found  in  groundwater  primarily
         in  Arizona,  Texas,  Michigan,  Vermont,  and  Florida.  Barium  is  also  present  in  trace
         amounts  in some surface waters with the highest levels occurring in the lower Mississippi
         basin.  Barium  is  very  toxic  when  ingested  as  a  soluble  salt--a  dose  of even  550  mg  is
         considered  lethal.
        Barium Removal by Softeners.   Barium is readily exchanged on to the strong acid cation
         exchange resins  in  softeners.  Barium  has  a  higher selectivity for cation  resins than either
         calcium  or magnesium  (hardness),  and  is removed throughout  the entire  softening cycle.
         It does  not begin to leak until after hardness.  The  increase  in barium  caused by hardness
         breakthrough,  though  small compared  to the hardness  leakage,  may  be  sufficient to war-
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