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SLOW SAND AND DIATOMACEOUS EARTH FILTRATION      9.3

                TABLE 9.1  Source Water Quality Limitations  of Slow Sand Filters

                          Parameter               Recommended  limit
                Turbidity                      5 to  10 ntu*
                Algae                          200,000/Lt
                True color                     15 to 25 platinum  color units
                Trihalomethanes                50/zg/L
                Nonpurgeable  dissolved  organic carbon   2.5 mg/L
                UV absorbance~:                0.080 cm-l
                Dissolved  oxygen              >6  mg/L
                Phosphorus  (PO4)              30/zg/L
                Ammonia                        3 mg/L
                Iron                           < 1 mg/L
                Manganese                      < 1 mg/L

                  *Presence  of clay particles  must be determined.
                  tDependent on identification  of algal  species  and assumes covered filter.
                  :~Absorbance at wavelength of 254 nm.


        found that  some biological activity also extends deeper into the bed, where particulate re-
        moval is accomplished  by bioadsorption  and  attachment  to  the  sand  grains.


        Source Water Quality Considerations

        In  considering  whether  slow  sand  filtration  is  an  appropriate  treatment  method,  source
        water  quality  must  be  carefully evaluated.  If source  water quality  data  are not  available,
        pilot testing of the source water is essential to determine the applicability of the slow sand
        treatment  option.  Table 9.1  lists  source water quality parameters  with recommended lim-
        its  (Spencer  and Collins,  1991).
         Turbidity.  Both  the  level and  type  of turbidity  in  source  water  must  be  considered.  In
        general,  most  existing  slow  sand  plants  successfully  treat  source  water  turbidity  of less
        than  10  ntu  (Slezak  and  Sims,  1984),  which  is  recommended  for  an  upper  limit in  de-
         signing new  facilities.  Also  of some  importance  is  the  stability  of the  water.  Slow  sand
        facilities operate  more  efficiently if source  turbidity  is  relatively constant  and  generally
         --< 5.0  ntu.
           Of equal importance  is the nature  of particulates.  Source waters  that normally contain
        clay particulates  or that pick up clay after storm events will cause problems for slow sand
        filters.  This  difficulty for  slow  sand  filters  occurs  because  clay  penetrates  deep  into  the
        bed  or may  even carry  through  the  filter,  causing  an  immediate problem  of elevated fil-
        tered water turbidity and a long-term problem of filter clogging and reduced length of fil-
        ter runs.
        Algae.  In a  few instances,  it has  been  found  that  the presence  of certain  types  of algae
        actually  enhances  the  filtration  process  by  providing  greater  surface  area  for  biological
        activity. In general, however, the presence  of algae in the  source water reduces  filter run
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