Page 113 - Adsorbents fundamentals and applications
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98   ACTIVATED CARBON

                           100.0                                            m/e Range
                                                                             94 ± 0.5
                            92.9
                                                                             186 ± 0.5
                            38.8
                                                                             278 ± 0.5
                            19.6
                          Signal intensity  5.6                              378 ± 0.5
                                                                             462 ± 0.5
                             0.7

                             0.1                                             554 ± 0.5
                                                                             646 ± 0.5
                              0
                                                                             738 ± 0.5

                            RIC
                               0     10    20    30    40    50    60     70  Scan
                                    4:20  8:40  13:00  17:20  21:40  26:00  30:20  Time
                     Figure 5.14. Mass spectra for the irreversibly adsorbed phenol on Columbia carbon (extracted
                     by acetone). Not shown here are the spectra of the control solution of phenol in acetone, which
                     shows only the species of m/e = 94. The mass number 94 corresponds to phenol, and those
                     of multiples of 94 (minus H from −OH) correspond to polymers of phenol (C 6n H 4n+2 O n ,where
                     n = 2–7) (from Grant and King, 1990, with permission).


                     for these reactions. The catalytic activities of oxidized carbons for the oxidation
                     of SO 2 (to SO 3 )and NO to (NO 2 ) at ambient temperature in both gas phase and
                     aqueous phase are well known and have been studied extensively (Komiyama
                     and Smith, 1975; Py et al., 1995; Govindarao and Gopalakrishna, 1995; Rubel
                     and Stencel, 1997; Mochida et al., 1994; Mochida, 1997; Lisovskii et al., 1997;
                     Muniz et al., 1998; Mochida et al., 2000).
                       The effects of surface functionalities on adsorption of phenols have been stud-
                     ied extensively. However, in light of the findings of Grant and King (1990), such
                     effects need to be re-examined, that is, reversible and irreversible adsorption
                     should be treated separately.
                       A large body of experimental data is available in the literature on equilibrium
                     adsorption isotherms of organic compounds from aqueous solutions. Because
                     much of the data is for dilute solutions where no plateau is seen in the isotherm,
                     the data can be best fitted with the Freundlich isotherm:

                                                 q = KP  1/n                        (5.2)


                     The Freundlich isotherm constants for a few selected organic compounds are
                     given in Table 5.4. The Freundlich isotherm constants for adsorption of some
                     600 organic compounds and pollutants on activated carbon have been compiled
                     by Faust and Aly (1987).
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