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INTAKE FACILITIES                   4.17

                  TABLE 4.5  Location  and Spacing  of Ports

                      Criterion             Suggested  location
                  Vertical  spacing   10-15  ft (3-5 m) maximum
                  Depth  above bottom   5-8 ft (1.5-2.4  m)
                  Depth below  surface   Variable
                  Intermediate  ports   Best water quality,  avoidance  of pollution
                  Ice avoidance      20-30 ft (6-9 m) below  surface
                  Wave action        15-30 ft (5-9 m) below surface




         rameters  throughout  the  depth  of the  water  source  should  also  be  considered  as  an  ele-
         ment  of the  intake facility design.
           Experience has  shown  that  the  final number  and  spacing  of inlet ports  is  affected by
         the  specific conditions  to be  encountered,  as  shown  in Table 4.5.
           There is typically a wide variation of water quality,  with respect to depth,  in stratified
        lakes.  At Shasta  Dam  in northem  California,  turbid  water behind  the dam became  strati-
        fied within several weeks after a major storm. The most turbid  water settled near the bot-
        tom, and the water became progressively less turbid toward the surface.  These, and other,
        studies  confirm the value of intake tower designs  that  include multilevel inlet ports.  Oc-
        casional  adjustment  of the depth  of draft can often substantially  improve chemical, phys-
        ical,  and  biological  water  quality  parameters.  These  improvements  are  reflected  in  en-
        hanced  treatment  performance  and  reduced  treatment  costs.
           Intake ports  should be selected to achieve reliable delivery of water while minimizing
        the inclusion of unwanted  material or contaminants.  Table 4.6 provides a  summary  of de-
        sign criteria for exposed  intakes.
           The intake tower shown in Figure 4.12 is located in Monroe Reservoir, the water sup-
        ply  source  for Bloomington,  Indiana.  Two  intake  cells,  each  equipped  with  three  intake
        ports, provide variable depth withdrawal capability. Bar and traveling screens protect four
        vertical, wet-pit pumps.  The design capacity of the intake system is 48 mgd (182  ML per
        day).
           Various  inlet designs  for  submerged  intakes  avoid sediment,  sand,  and  ice problems.
        Inlets are best located in deep water with inlet velocities less than 0.5 ft/s (15 cm/s),  with
        a  preferred  range  of 0.2  to  0.3  ft/s  (6.1  to  9.1  cm/s).  Inlet  structures  are  typically  con-
        structed  of wood  or other nonferrous  materials  with  low  heat  conductivity  that  are  less
        susceptible  to  ice  deposits.  Submerged  intakes  may  be  constructed  as  "cribs"  surround-
        ing an upturned,  bell-mouth inlet connected  to  an  intake  pipeline.  The  crib is often  con-
        structed  as  a polygon,  built of heavy timbers  bolted together,  weighted  and protected  by



             TABLE 4.6  Exposed  Intake Design  Criteria
                 Criterion                      Remarks
             Port velocity      0.20-0.33  ft/s (6-10 cm/s); 0.50 ft/s (15 crn/s) maximum
             Ports              Multiple;  three minimum
             Water level variation   Design  capacity  at minimum level; operating  deck
                                above 500-year  flood level
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