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9.10                        CHAPTER NINE


        on  the  roof.  If funds  are  available,  a  permanent  lighting  system  increases  visibility and
        eliminates hazards  associated  with portable  lighting.
           Because  of high-humidity  conditions,  the lighting design must  incorporate  corrosion-
        resistant  materials  such  as  aluminum  and  stainless  steel.  Lighting units  must  include in-
         tegral  gaskets  and  methods  of sealing  wire penetrations  to minimize moisture  within the
         units.  Conduit  systems  must  use corrosion-resistant  materials.
           Lighting units  must be mounted  in a  manner  that  minimizes damage  from high water
         levels or from  operating  cleaning  equipment.  Lighting  levels on  the  order  of  10  fc  (100
         lm/m 2) provide  sufficient light to  allow efficient and  safe operations.
         Ventilation.  Little  consideration  was  given  to  ventilation  in  older,  covered  slow  sand
         filters.  Usually  ventilation  consisted  of open  hatches  with  portable  ventilators  installed
         during  maintenance  operations.  Although  portable  units  increase  ventilation,  the  actual
         rates  are generally below  those required by  code when  engine-driven equipment is being
         operated  inside  the filter unit.
           For newer installations,  ventilation rates for motorized equipment must be designed to
         protect  operators  and  should  be  similar to those provided in parking  garages.  Rates  must
         be set according to expected emissions of motorized equipment operated within the basin.
         The number of air changes required  is generally governed by state  or federal regulations.
         Filter Roofing System.  Selection  of  a  filter  roofing  system  must  consider  capital  ex-
         pense,  long-term reliability, headroom,  availability of material,  and  site conditions.  Cast-
         in-place  systems  are  generally the  most expensive but  are the most  durable.  Precast con-
         crete  slabs  are  less  expensive  than  cast-in-place  but  have  a  slightly  shorter  life  span.
         Systems  constructed  of  wood  or  steel  experience  significant  deterioration  or  corrosion
         problems  and  require  replacement  within  a  relatively short  time.  Obviously, the replace-
         ment  expense  versus  initial capital  expense  must  be  evaluated in design.
           Methods  of covering the roof system  include shingles, metal roofing, single-ply mem-
         brane, built-up roofing, and earthen fill. Again, each system has  specific capital costs, and
         not all are usable  with each roof support  system.  An  earth cover system  can help blend  a
         facility into  its  surrounding  but  requires  a  strong  support  structure  to carry  the load.

         Filter-to-Waste  System.  The  design  of a  slow  sand  filter should  provide  the  ability to
         discharge  filtered water to waste.  The filter-to-waste system  allows the operator to check
         effluent  quality  after  a  filter cleaning  and  before  bringing  the  filter back  on  line.  It also
         provides  a  method  to "cleanse" filter media  after resanding  or other major reconstruction
         work.
           The filter-to-waste system must be designed to avoid a potential cross-connection. The
         ideal  system  includes  an  air  gap  on  the  filter effluent to  the  drain  pipe.  However, many
         regulators  allow  a  hard  piped  connection  to  a  drain  system,  with  valving to direct water
         to  finished  water  storage  or to  waste.  In  the  latter case,  it  is normally  required to install
         the  filter-to-waste  line at  an  elevation below  the  filtered water  line and  to provide an  air
         gap  at the  ultimate  discharge  point to  minimize potential  contamination.
        Filter Draining.   At  some point  in  the  filter cycle,  head  losses  increase  to  such  a  level
        that  filter production  is unacceptably  low,  and  the  filter must  be  taken  off-line for clean-
        ing.  Because the rate is so low through the filter and the hydraulics  between adjoining fil-
        ters  may  not  allow  significant  drop  in  filter level to  occur,  some  form  of separate  drain
        should  be provided.
           This  drain  should  generally  be  installed  to  discharge  filter supernatant  either back  to
        the  source  or to  a  lagoon.  The  drain  can  also  be  connected  to  the  filter-to-waste  system
        through  an  air  gap,  or it may  be  installed  as  a  separate  system.  Cross-connection  to the
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