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OXIDATION AND DISINFECTION              10.11


           Oxidizing agents, or oxidants, used in water treatment include chlorine, chlorine diox-
         ide,  permanganate,  oxygen,  and ozone.  The  appropriate  oxidant for  achieving  a  specific
         water quality objective depends on a number of factors,  including raw  water quality,  spe-
         cific contaminants,  and local chemical  and power  costs.  For critical applications,  the de-
         signer should insist on bench- or pilot-scale evaluations of treatment alternatives to select
         the best approach  and determine  appropriate  design  criteria.


         Iron  and  Manganese  Removal
         Iron and manganese have secondary MCLs  (SMCLs)  of 0.3  and 0.05  mg/L,  respectively.
        These  SMCLs  have been considered as  safe limits to avoid the staining of plumbing fix-
        tures  and  laundry,  but  experience  shows  that  lower  levels  are  desired  to  avoid  difficul-
        ties.  Targets  of <  0.1  mg/L  iron  and  <  0.02  mg/L  manganese  should  be  normal  water
        quality  goals.
           Dissolved iron and manganese are normally in the reduced  state (Fe II and Mn II) and
        can be removed by oxidizing to Fe III and Mn IV, where they will precipitate as Fe(OH)3
        and  Mn(OH)2.  Precipitates  are  subsequently  removed  in  sedimentation  and/or  filtration
        steps.  Several  oxidants  are  available for this process,  namely,  chlorine,  chlorine dioxide,
        ozone,  and  potassium  permanganate.  They  are  also  removed  through  conventional  lime
        softening treatment. The  stoichiometric requirements for each oxidant are given in Tables
         10.6 and  10.7. Most oxidants also react with organics in the water,  so some testing is nor-
        mally  required  to determine the appropriate  dose.
           Small well  water systems with excessive levels of iron and manganese often apply  an
        oxidant,  provide  a  period  of  detention  for  the  reaction  to  take  place,  and  then  remove
        the  precipitated iron  and  manganese  with  a  pressure  filter.  Figure  10.5  illustrates  such  a
        system.
           Chlorine is  an effective oxidant  for iron,  and  oxidation  to Fe(OH)3  proceeds  rapidly.
        It is not as effective for manganese removal, however,  at normal pH  conditions. Chlorine

        TABLE 10.6  Oxidation of Manganese

                                                     Alkalinity
                                          Oxidant,   used,  mg/mg   Sludge,*  lb/lb
                    Reaction            mg/mg Mn 2+    Mn 2+     (kg/kg) Mn 2+
        A. Oxygen                          0.29         1.80        1.58
           2MnSO4  +  2Ca(HCO3) 2 +  02
           =  2MnO2  +  2CASO4 +  2H20  +  4CO2
        B.  Chlorine                       1.29        3.64         1.58
           Mn(HCO3)2  +  Ca(HCO3)2 +  C12
           =  MnO2 +  CaCI2 -  2H2 O +  4CO2
        C.  Chlorine dioxide               2.46        3.60         1.58
           Mn(HCO3)2  +  2NaHCO3  +  2C102
           =  MnO2 +  2NaCIO2 +  2H20
           +  2CO2
        D. Potassium permanganate          1.92         1.21        2.64
           3Mn(HCO3)2  +  2KMnO4
           =  5MNO2 +  2KHCO3 +  2H20
           +  4CO2
          *Sludge weight based on MnO2 as the precipitate. It is highly probable that portions of the sludge will consist
        of MnOOH and MnCO~.
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