Page 696 - Fundamentals of Water Treatment Unit Processes : Physical, Chemical, and Biological
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Oxidation                                                                                        651


                                                                 100
                                                                                            2+
                                                                        200 μg/L        C(Mn , raw)= 200 μg/L
                     100                                                                C(CIO 2 )=0.85 μg/L
                                2+
                            C(Mn , t=0)=60 μg/L  TOC= 3.4 mg/L         Dissolved Dissolved  Colloidal
                                                pH= 7.0                                 pH =7.4, T =5°C
                                                                  80
                                                T =9°C
                      80                                                          Particulate
                                          Permanganate—0.36 mg/L  60
                    C(Mn 2+ ) ( μg/L)  60                        C(Mn 2+ ) (μm/L)  40            Particulate


                      40

                                                                         Colloidal  Dissolved  Dissolved  Colloidal  Particulate  Dissolved  Colloidal  Particulate
                      20                   Ozone—1.5 mg/L         20       Particulate               Dissolved
                                         Chlorine dioxide—0.5 mg/L                             Colloidal
                      0                                           0
                        0    100   200   300   400   500   600        Raw      Pre   Post   Settled  Filtered
                                                                              - rapid  -rapid
                                        Time (s)
                                                                              -mix   -mix
                   (a)                                         (b)               Stage in treatment
            FIGURE 20.3  Results from experiments to reduce Mn 2þ  (from in-house research program at Fort Collins WTP reported by Gregory (1996,
            1997). (a) Bench-scale kinetic results comparing ClO 2 , KMnO 4 , and ozone as oxidants, and (b) profile of Mn species across pilot plant
            treatment train following oxidation by ClO 2 (1.5 times stoichiometric amount).

                                                               undergo oxidation at temperatures, 2008C < T(reactor) <
                                     T (°C)
                      –200  –100  0  100  200  300  400  500   3008C, which is the basis for wet-oxidation (as exemplified by
                 300                                           the Zimprot process) operated under subcritical conditions but
                                                   Super-      which requires residence times, 20 < u(reactor) < 50 min,
                                                    critical
                 250                Critical point             achieving destruction efficiencies of only 70%–95% in total
                                   (374°C, 218 atm)            organic carbon (TOC). Under supercritical conditions, however,
                 200    Solid        Liquid                    u(reactor) < 1 min, and destruction efficiencies are >0.9999
                Pressure (atm)  150                            thus the oxidation can occur under homogeneous, that is, single
                                                               fraction. In addition, oxygen is completely soluble in SCW and
                                                               phase, conditions (meaning that there is no mass-transfer across
                 100                             Gas           agas–water interface). Thus, SCWO is highly efficient. The
                       Triple point:                           SCWfunctions as a carrier fluid,asa solvent for the feedmaterial
                      (T TP =0.01°C,                           and reaction products, and as a reactant with organic materials
                  50  P TP = 0.006 atm)
                                            Boiling point      (Modell, 1985, p. 97).
                                                                  If the oxidation occurs in an adiabatic reactor, that is, no
                   0
                    0   100  200  300  400  500  600  700  800  heat-transfer across the system boundaries, the heat of com-
                                                               bustion is retained within the fluid, raising the temperature. If
                                     T (K)
                                                               the concentration of carbon is higher than 2%–5%, the heat
            FIGURE 20.4  Phase diagram for water showing critical point.  of oxidation is sufficient to bring the reactor temperature to
            (Adapted from Silberberg, M., Chemistry—The Molecular Nature  T(reactor) > 5508C. The heat generated may be recovered for
            of Matter and Change, Mosby-Year Book, Inc., St. Louis, MO,  raising the temperature of the inflow stream. Except as noted,
            1996, p. 451.)                                     this section was based on an article by Timberlake et al.
                                                               (1982, pp. 1, 2) and a comprehensive summary of the
            0.05< r(water, T > 5008C) < 0.1 g=mL and the dielectric con-  SCWO process by Modell (1988).
            stant is less than 2 and inorganic salts are only sparingly soluble.
                                                               20.2.3.3  Characteristics of Supercritical Water
            Whereas many organic compounds tend to form a high molecu-
            lar weight char at temperatures below 3508C, at supercritical  Relevant to Engineering
            conditions the same organics are reformed to gases, for example,  Some of the characteristics of SCWO were given by Jain
            CO 2 ,H 2 ,CH 4 ,CO 2 , and volatile organic liquids, for example,  (1993) are as follows:
            alcohols, aldehydes, and furans without producing any char.
            Materials as complex as wood can be completely dissolved  1. Supercritical water has high dissolving power, exhi-
            and reformed in SCW. These products then can be subjected to  biting the characteristics of a nonpolar organic
            oxidation; for example, aqueous solutions of organics will  solvent (Gloyna and Li, 1995, p. 183). Organic
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