Page 365 - Fundamentals of Water Treatment Unit Processes : Physical, Chemical, and Biological
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320                            Fundamentals of Water Treatment Unit Processes: Physical, Chemical, and Biological



            11.6.1 TURBINE FLOCCULATORS                        1930s. They are widely used, especially in small plant situ-
                                                                                 3
                                                               ations e.g.,  0.876 m =s (20 mgd) plant capacity. They are
            The use of axial flow and turbine impellers of the Rushton
                                                               viewed with disfavor by some (Burns and Roe, 1971, pp. 4–6)
            type (Sections 10.3.3.4, 10.4.2.5, and Glossary of Chapter 10)
                                                               because of lack of control of each of the unit processes. An
            for flocculation was investigated by Walker (1968), then
                                                               additional disadvantage is that the flow of water is likely to be
            president, Walker Process Equipment, who used a 1676 mm
                                                               distributed nonuniformly below the sludge blanket. The flow of
            (66 in.) Rushton impeller in a 12.2 m (40 ft) diameter by 4.6 m  water willseek its own path of least resistance through the sludge
            (15 ft) tank with 1.52 m (5 ft) depth of submergence. The
                                                               blanket, thus creating a channel of higher velocity flow leaving
            circulation patterns for the axial flow impeller was up and
                                                               much of the sludge blanket an inert mass. The advantage in
            around with return flow to the impeller eye. While Walker
                                                               their use is that three unit processes, i.e., rapid mix, floccula-
            was striving for uniform turbulence, the tests showed that the
                                                               tion, sedimentation, are combined in one unit with consequent
            large eddies that predominated in the reactor volume were not
                                                               smaller size than the three unit processes as separate units.
            efficient in flocculation, i.e., consistent with later theory.
                                                               11.6.2.1  Principles
            11.6.2 SOLIDS CONTACT UNITS                        The processes in a solids contact unit start in the rapid mix
                                                               where the coagulant chemicals and the raw water are mixed and
            Solids contact units, sometimes called ‘‘sludge-blanket clari-
                                                               collide with floc particles pumped into the reactor from the
            fiers,’’ contain rapid mix, flocculation, and settling in one unit;
                                                               sludge blanket, as shown in Figure 11.19. The flow then enters
            Figure 11.19 is a schematic diagram. As seen, the raw water
                                                               the flocculator where further collisions between particles occur
            flows into a rapid mix basin with coagulant flow being injected
                                                               due to reduced turbulence in the flow. The flocculated particles
            into the rapid mix. The flow from the rapid mix passes through a
                                                               then enter the sludge blanket and presumably flow upward
            flocculation zone and then is forced through the sludge blanket
                                                               through the blanket to collide with previously formed floc
            with upflow through the clarification zone and into radial over-
                                                               particles, thus growing in size and settling more readily.
            flow troughs, which flow into a gullet around the periphery of
                                                                  As to the size of floc particles in the floc blanket, Tambo
            the clarifier. The sludge blanket is fluidized floc particles and is
                                                               and Hozumi (1979, p. 441) mention 0.3   d(floc) max   0.5 mm
            maintained at a designated level by means of sludge wasting
                                                               (300–500 mm) with incoming microfloc sizes 5   d(micro-
            from the sludge pocket. A ‘‘picket fence’’ thickener of vertical
                                                               floc)   10 mm. The contacts are between particles with
            bars attached to a rotating shaft helps to increase the density of
                                                               these size differences. Equation 11.1 is applicable to the
            the sludge before it leaves the sludge pocket. Each manufacturer
                                                               collision frequency within the floc blanket. The decline in
            has its own variation of the kind of system shown in Figure
                                                               concentration of microflocs with distance in the blanket is
            11.19. Applications include drinking water treatment and chem-
                                                               (Tambo and Hozumi, 1979, p. 446) given by
            ical treatment of secondary-treated wastewaters. The latter may
            include lime as the chemical for phosphate reduction.
              The solids contact technology was developed by equip-                 C     kz
                                                                                      ¼ e                 (11:31)
            ment manufacturers and the units have been in use since the             C o
                                 Gullet                         Inner shaft
                                         Radial trough             Outer shaft
                 Effluent flow
                                   Clarified                  Rapid mix
                                    upflow                                                          Alum
                                             Flocculator                                              Raw
                           Water flow
                                                                                                    water flow
                                                                   Impeller
                            Sludge blanket



                             Scrapter      Thickener
                                           Sludge pocket
                                                                             Sludge flow
            FIGURE 11.19 Solids contact clarifier—generic schematic (EPA Manual, 1971).
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