ABSTRACT
Several activated carbons differently pretreated (de-ashed, oxidized, reduced, wetted, frozen, and dried) were investigated using static (equilibrium adsorption of nitrogen and benzene) and dynamic (tert-butylbenzene (TBB)) adsorption methods. Treatments of carbons at relatively mild conditions leading to not great changes in their textural characteristics affect the TBB breakthrough concentration because of changes in the chemistry of the surfaces (oxidized or reduced) and the presence of water in airstream or pre-adsorbed on carbon beds. Oxygen-containing functionalities at a carbon surface change condition of competitive adsorption of nonpolar TBB and polar water molecules. Calculations of distribution functions of adsorption potential (A), energy (E), Gibbs free energy (Delta G) of adsorption of benzene and TBB and effective adsorption (first-order) rate pseudoconstant beta e over different ranges of relative exit TBB concentration c(t)/c(0) (from approximately 10(-5) to 0.01-0.4) reveal nonlinear effects caused by the size of carbon granules, the pore size distributions, the presence of water, oxidation or reduction of the surfaces and other treatments resulting in distribution functions f(y) with nonzero intensity in relatively broad ranges of the A, E, Delta G, and beta e values. There are many factors affecting the breakthrough parameters; therefore, simple linear relationships between these parameters and the structural characteristics (S(BET), S(DS), Vp, and V(DS)) are not observed.
ABSTRACT
The influence of organics on the structure of water adsorbed on activated carbons was studied using adsorption of nitrogen, benzene, and water, and by (1)H NMR spectroscopy with freezing out of bulk water with the presence of benzene-d(6) or chloroform-d. It was found that interactions of water with the activated carbon surface depend on both structural characteristics (contributions of micro- and mesopores, pore size distributions) of adsorbents and chemical properties (changed by oxidation or reduction) of the adsorbents. Moreover, the interfacial behavior of water is affected by water-insoluble organics such as benzene and chloroform. Changes in the Gibbs free energy of water adsorbed on carbons exposed to air, water, chloroform-d, or benzene-d(6) are related to textural properties of adsorbents and the degree of their oxidation. Since chloroform-d and benzene-d(6) are strongly adsorbed on activated carbons and immiscible with water they replace a significant portion of adsorbed water in micropores, on the walls of mesopores, and in the transport pores of carbons causing changes in the Gibbs free energy and other characteristics of water.
