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Anionic clays exchange reactions

The dispersion and solid-state ion exchange of ZnCl2 on to the surface of NaY zeolite by use of microwave irradiation [17] and modification of the surface of active carbon as catalyst support by means of microwave induced treatment have also been reported [18]. The ion-exchange reactions of both cationic (montmorillonites) and anionic clays (layered double hydroxides) were greatly accelerated under conditions of microwave heating compared with other techniques currently available [19.]... [Pg.349]

Gilbert, M. and R. van Bladel. 1970. Thermodynamics and thermochemistry of the exchange reaction between NHJ and Mn " in a montmorillonite clay. J. Soil Sci. 21 38-49. Kingston, F. J. 1970. Specific adsorption of anions on goethite and gibbsite. Ph.D. dissertation, University of Western Australia, Perth. [Pg.116]

Let us examine the process of diffusion in clays at the first stage of their consolidation, before the moment when m = 0. We will suppose that the diffusion solution contains cations of the same type, as cations of the exchanging complex of clay meaning that there is no ion exchange reaction. We will also suppose that in every point of environment the equilibrium between the solution in transport pores and the solution between clay particles is established immediately (its parameters we will be marked by the overline). Like this we will successively build the model of diffusion in clays in a local equilibrium approach. The conditions of equilibrium of cations (index 1) and anions (index 2) of two solutions are the equality of the chemical potentials, =. Pi= where... [Pg.448]

Diquat and paraquat are readily adsorbed from aqueous solutions by soil particles 40, 41, 42, 43, 44, 45, 46, 47), montmorillonite (30, 41, 48, 49, 50, 51, 52, 53, 54, 55, 56), kaolinite 41, 50, 52, 53, 54, 55), vermiculite 29, 30, 49,56), biotite 29, 30), muscovite 29, 30), phlogo-pite (29), muck 46, 48, 51), and cation exchange resins 48, 57). Only small or insignificant amounts were adsorbed by charcoal and anion exchange resins 48, 51, 53). The compounds were adsorbed to cation exchange substances through cation exchange reactions for diquat by clay minerals (Equation 1). [Pg.65]

FIGURE 9.17 Chemical reactions showing anion exchange, reactions with hydrous oxides or ligand exchange, fixation by silicate clays, and precipitation. [Pg.340]

The adsorption and redox of metal complexes on clay-modified electrodes were examined by Yao et al. [94]. The species adsorbed on a saponite clay film by the exchange with a hydrated sodium ion in the clay film were identified from the mass change and absorbance change of the metal complexes in solution as follows [Ru(bpy)3] +1/2S04 for racemic body, [Ru(bpy)3] + and [Ru(bpy)3] " l/2S04 for enantiomers, and [Ru(NH3)6] +-S04 . The EQCM results revealed that one [Ru(bpy)3] + molecule was eliminated from the clay film when three [Ru(bpy)3] + ions were oxidized [95]. The charge balance during the redox reactions was accomplished by the transport of S04 and Na" " in the cases of [Ru(NH3)6] + and [Fe(CN)6] . The adsorption and redox of [Fe(CN)6] on an anionic clay-modified electrode (hy-drotalcite) were also examined [96]. [Pg.6548]

As proposed in Figure 3.19, ion-exchange reactions might result in the formation of clay anions and metallocene cations (soft ions), and sodium and chloride ions (hard ions). The ion exchange of metallocenium cations with clay surfaces is also discussed by Mariott et al. [83, 84]. [Pg.75]

The main classes of catalysts used for heterogeneous WHPCO reaction are clays and anionic clays (hydrotalcites), metal-ion exchanged zeolites and mesoporous silica containing transition metals, and doped metal oxides. Although some other transition metals have been also used (Mn, V), most catalysts contain iron and/or copper as the active elements. Leaching of the active metal is also a significant problem in this case. While different types of catalysts have been reported, only a few of them have been effectively proven to have a stable activity in long-term continuous experiments or at least in several repeated batch tests. Between the stable catalysts, Fe- and Cu-PILC (pillared clays) materials " have the best combination of activity and stability. However, the limited quantity of active elements (around 2% wt. of iron or copper) necessary to achieve stable performances, limits the overall activity. [Pg.277]

Conductive electrodes based on metal oxide, e.g., indium-tin oxide (TTO), are widely used in electrochemistry as a support for surface modification with the goal to develop sensors with electrochemical transduction or combined spectroscopic and electrochemical responses or electrochemiluminescence. Inorganic thin films can also be prepared from the assembly of two-dimensional layered inorganic solids, such as cationic clays and layered double hydroxides (LDHs, also defined as anionic clays). These materials can be used to preconcentrate species on the basis of ion-exchange reactions and applied to heavy metal determination or for the detection of organic pollutants. [Pg.437]

The coulombic attraction for anions and cations due to the positive and negative charges of allophane that may arise from the dissociation of H" from Si—OH groups or OH from A1—OH groups between pH4 and 7. This is the normal cation exchange reaction that applies to all clay minerals. However, in the case of allophane the reaction is pH-dependent the lower the pH the lesser the amount of cation adsorbed, and vice versa for anions. [Pg.383]

Many mineralogic reactions involve exchange of cations or anions. Hence, geochemists commonly need to determine equilibrium lines in terms of activity ratios. Consider, for example, the reaction at 25 °C between the clay kaolinite [Al2Si205(0H)4] and the mica muscovite. The RXN commands... [Pg.177]

Feldspar, among many natural substances such as termite mount-clay, saw dust, kaolinite, and dolomite, offers significant removal ability for phosphate, sulfate, and color colloids. Optimization laboratory tests of parameters such as solution pH and flow rate, resulted in a maximum efficiency for removal of phosphate (42%), sulfate (52%), and color colloids (73%), x-ray diffraction, adsorption isotherms test, and recovery studies suggest that the removal process of anions occurs via ion exchange in conjunction with surface adsorption. Furthermore, reaction rate studies indicated that the removal of these pollutants by feldspar follows first-order kinetics. Percent removal efficiencies, even under optimized conditions, will be expected to be somewhat less for industrial effluents in actual operations due to the effects of interfering substances [58]. [Pg.447]

The fluoride ion chemisorbs on clays and oxides by ligand exchange of surface OH", a reaction favored at low pH and on oxide and silicate minerals of low crystallinity. Fluoride, a hard base, has a particular affinity for a hard acid. Soluble AP -fluoride cationic and anionic complexes are quite stable, and can dominate the speciation of dissolved aluminum in low-humus soils. The mobility of A1 can be increased by the presence of F soluble complex formation with A1 may explain the rather high solubility and mobility of F in acid soils. [Pg.332]

The adsorption of biomolecules onto carriers that are insoluble in water is the simplest method of immobilization. An aqueous solution of the biomolecules is contacted with the active carrier material for a defined period of time. Thereafter the molecules that are not adsorbed are removed by washing. Anionic and cationic ion exchange resins, active charcoal, silica gel, clay, aluminum oxide, porous glass, and ceramics are being currently used as active material. The carrier should exhibit high affinity and capacity for the biomolecule and the latter must remain active in the adsorbed state. The carrier should adsorb neither reaction products nor inhibitors of the biocatalyst. [Pg.51]

The anion exchange mechanism in Table 4.3 is the analog of the reaction in Eq. 4.45, wherein the signs of the valences are reversed B symbolizes a carboxylate group (COO ) and M is replaced by a univalent, inorganic anion that forms outer-sphere complexes with protonated surface hydroxyl or amine groups. This mechanism is not observed often, possibly because of the weakness of the surface complexes involved, but it should be prominent in acidic soils whose clay fraction comprises primarily metal oxides. [Pg.144]


See other pages where Anionic clays exchange reactions is mentioned: [Pg.73]    [Pg.271]    [Pg.423]    [Pg.232]    [Pg.160]    [Pg.63]    [Pg.163]    [Pg.96]    [Pg.4042]    [Pg.387]    [Pg.381]    [Pg.471]    [Pg.97]    [Pg.383]    [Pg.31]    [Pg.130]    [Pg.164]    [Pg.345]    [Pg.244]    [Pg.33]    [Pg.36]    [Pg.205]    [Pg.297]    [Pg.645]    [Pg.157]    [Pg.100]    [Pg.121]    [Pg.321]    [Pg.927]    [Pg.196]    [Pg.252]    [Pg.390]   
See also in sourсe #XX -- [ Pg.142 , Pg.143 , Pg.144 ]

See also in sourсe #XX -- [ Pg.142 , Pg.143 , Pg.144 ]




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