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100   Industrial Wastewater Treatment, Recycling, and Reuse


          1916), originally, it was a theoretical equilibrium isotherm relating to the
          amount of gas adsorbed per unit mass of the adsorbent. It is based on a uni-
          form, monolayer, and finite adsorption site. The Langmuir adsorption iso-
          therm assumes that there is no interaction among molecules adsorbed on the
                                                                 1
          neighboring adsorption sites. The Langmuir constant, a L (mg g ) gives the
          theoretical adsorption capacity, while C e and q e have their usual physical
                           1
          meanings. b L (L g ) is another Langmuir constant whose value can be
          determined from the plot of C e vs. C e /q e .
             The Freundlich equation (Freundlich, 1906) is an empirical equation
          based on adsorption on heterogeneous sites. It is also one of the most com-
          mon two-parameter isotherms applied for wastewater treatment. It assumes
          that stronger binding sites are occupied first, and the strength of adsorption
                                                                         1
          decreases with the degree of occupation. The constant, K (mg g )
                1 1/n
          (L mg )    in the Freundlich expression, is related to the capacity of the
          adsorbent for the adsorbate; 1/n is a function of the strength of the adsorp-
          tion, and it indicates the affinity between the adsorbent and adsorbate. A
          value of 1/n below unity implies that the adsorption process is chemical;
          if the value is above unity, adsorption is more of physical process; the more
          heterogeneous the surface, the more the 1/n value approaches zero. The
          values of k for several priority pollutants (e.g., nitrobenzene, styrene, chlo-
          robenzene, bromoform) are in the range 60–360 mg/g and the values of
          1/n¼0.12–0.98 (Munter, 2000).
             The Dubunin-Radushkevich (Dubinin, 1960) is an empirical adsorp-
          tion isotherm that is now mostly applied for metal ion adsorption from
          an aqueous system. It is used to predict whether the adsorption is physi-
          sorption or chemisorption from its mean free energy per molecule of
                                 1
          the adsorbate, E (kJ mol ). The energy of adsorption is computed by
          the relationship
                                            1
                                          p
                                      E ¼ ffiffiffiffiffiffiffiffiffi
                                            2B D
             The D-R equation takes into account the temperature effect as the fac-
                                      1
          tor. In the isotherm, q D (mol g ) is the theoretical saturation capacity, B D
              2  2
          (mol J ) is a constant related to the mean free energy per mole of the
                                                               1
          adsorbate, and R is the molar gas constant (8.314 J K  1  mol ).
             The Redlich-Peterson model is a three-parameter isotherm model
          (Redlich and Peterson, 1959) compromising the features of both Langmuir
          and Freundlich. It can be applied over a wide range of concentrations for
          several solid-liquid adsorption equilibrium data.
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