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CHAPTER            9

                      SLOW           SAND          AND

               DIATOMACEOUS                          EARTH
                             FILTRATION




                                Michael  V.  Broder
                                 Hazen and Sawyer,  PC
                                 New York, New  York

                                 John  C. Byron
                                Stearns  & Wheler, LLC
                                 Cazenovia,  New York











        Although rapid sand filters predominate, the  two  types  of filters  covered  in this  chapter
        may be effective in many applications where source water quality permits. In general, the
        combined costs of constructing and operating slow sand and diatomaceous earth (DE) fil-
        ters  may  be considerably less  than  the  cost  of rapid  sand  filtration plants  for  the  same
        capacity.
           The  principal mechanisms for  separation of solids  in all porous  media filters  are  at-
        tachment and straining or entrapment. Because of the relationship of the somewhat large
        pores  in rapid sand filter media compared  with particulates,  the primary mechanism for
         separation is attachment. In the case of slow  sand and DE filters, however, the pore-par-
        ticulate size relationship results in more  substantial separation by entrapment.
           During the initial operation period of slow sand filters, the separation of organic mat-
        ter and other solids generates a layer of biological matter on the surface of the filter me-
        dia.  Once  established,  this  layer  is  the  predominant filtering mechanism.  Solids  are  re-
        moved  from  water  by  a  DE  filter as  the  source  water  flows  through  a  precoat  layer of
        powderlike DE.
           For all practical purposes, most solids are separated at the surface of the media in both
         actions. Because of the small pore size of the media, particulate separation is ideal for re-
        moving the cysts of Giardia  and Cryptosporidium.  In most situations, neither type of fil-
        ter requires previous conditioning of the raw  water.
           In general, application of slow sand and DE filtration should be limited to source wa-
        ters with turbidity levels less than 5 ntu. Where particulates are dominant (rather than or-
        ganic matter) both types of filters may be used with water of up to  10-ntu turbidity. If ei-
        ther type of filter is used on water with higher turbidity, filtrate quality will generally be
        acceptable, but the more rapid buildup of solids on the filter results in rapid loss of head
         and shortened length of filter runs.


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