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Clay Minerals (1976) 11, 331. NOTE C O M M E N T S ON T H E PAPER ' S U R F A C E ACIDITY OF I M O G O L I T E A N D ALLOPHANE' INTRODUCTION Very recently Henmi & Wada (1974) measured the surface acidity of montmorillonite by using Hammett indicators. As the Hammett acidity function, Ho, includes the activity of surface hydrogen (Br/3nsted) acids only (Benesi, 1956), three fundamental conditions must be fulfilled for the measurement of surface acidity of montmorillonite with Hammett indicators; (i) montmorillonite surfaces must act as proton donors, (ii) the proton transfer on clay surfaces must strictly only be a function of relative acidities/basicities of montmorillonite surfaces and the indicator base, and (iii) the phenomenon of acid colour development must be only due to protonation. Unfortunately, none of the three conditions is fulfilled in montmorillonite and consequently the measurement of its surface acidity by Hammett indicators is questionable. Surfaces of montmorillonite are basic. The centres of positive charge deficiency in montmorillonite are associated either with replacements in the octahedral layer or with replacements in the tetrahedral layer. In the first case the negative charge is distributed over at least the ten surface oxygens of the four silicon-oxygen tetrahedra whose apices are linked to a site of octahedral substitution, and, in the second, over at least the three surface oxygens coordinated to tetrahedral A13+. Consequently, the surface oxygens of montmorillonite are electron donors and are capable of hydrogen bonding with interlamellarly adsorbed polar molecules. In fact, in montmorillonite the negatively charged lattice groups are basic and act as proton acceptors. Because of the basicity of lattice groups there is a competition for the proton between the interlayer material(s) and the clay sheets. Therefore, it should not be surprising to note that on dehydration protons from H-montmorillonites (H3 O+, pKa = - 1.7) (Russell & Fraser, 1971), protonated urea (pKb = 13.82) (Mortland, 1966), anilinium ions (pKa = 4.6) (Yariv & Heller, 1973), and NH4+ (pKa = 9.25) (Russell & Farmer, 1964) migrate towards the lattice. If the observation of Johnson & Rumon (1965) (who found that proton transfer occurred between the acid and base only when the ApKa was about 3.75 or greater) holds true, then, these observations suggest that under dehydrated conditions montmorillonite lattices should have a pKa value of about 13. Whether this is true or not, strong bases like cyclohexylammonium ions (pKa = 10.64) (Yariv & Heller, 1973), ethylenediammonium ions (pKa = 10.65) (Cloos & Laura, 1972), and ethylammonium ions (pKa = 10-75) (Chaussidon & Calvet, 1965; Durand, Fripiat & Pelet, 1972) do not lose their protons even on heating under vacuum. The acidity of proton sources on montmorillonite surfaces is well known. In montmorillonite used by Henmi & Wada (1974) there are three sources of protons, e.g. hydrogen, NH4+- and interlamellar water. Theoretically NH4-montmorillonite 332 Note should transfer its proton only to bases having pKa much larger than 9-25. However, it has been observed that on montmorillonite the surface N H ~ (pKa = 9-25) transfers its proton to 3-aminotriazole (pKa = 4.17) (Russell, Cruz & White, 1968) and pyridine (pKa = 5.23) (Raman & Mortland, 1969). These observations have been explained by a mass effect. Since indicators are always applied in minimum possible amounts they can be protonated by a large concentration of protons even from sources with lower acidity, e.g. with higher pKa values. This fact jeopardizes the very concept of measurement of pH by obse;ving the colour of a protonated base on clay surfaces. H-montmorillonite should not protonate a base having a pKa less than - 1 . 7 . Moreover, it is worth considering that even on H-montmorillonite, Mortland (1966) could not observe protonation of N H 2 groups of urea (pKa = 13-82). The observation of Yariv, Heller & Kaufherr (1969) with aniline (pKa = 4-6) was similar. According to the prevailing view, the water associated with the exchangeable cations on montmorillonite surfaces acts as a proton source and its proton donating ability increases with increasing ionic potential (valence/ionic radius) of the central metal cation. Unfortunately, this is a misleading oversimplification of the many phenomena which occur simultaneously when organic bases are adsorbed on clay surfaces. In fact, reactions of metal cations with water are reactions of complex cation formation. Complex cation formation involves competition among the water molecules, the anions and the complexing agent (e.g. ligand) in the coordination sphere of metal cations. Water molecules are attached to a metal cation by donation of the unshared electron pair on the oxygen atom and in the absence of anions and complexing agent aquo-complexes (or hydrated cations) are formed. The exchangeable cations on clay surfaces form the pure aquo-complexes due to the absence of buffering anions in the adsorbed layer, the negative charge being inherent to the clay phase. However, the water in aquo-complexes cannot act as a proton source under all circumstances. When the complexing agent forms the stronger bond with the metal cation, the water molecules are replaced by the complexing agent and a real coordination or chelation complex is formed. On montmorillonite surfaces a variety of organic bases form coordination or chelation complexes with transition, alkaline earth and alkali metal cations depending on the degree of hydration of the system and basicity of the organic molecule (Laura & Cloos, 1970, 1975a, 1975b; Yariv et al., 1968 ; Yariv, Heller & Kaufherr, 1969; Mortland, 1966; Farmer & Mortland, 1965, 1966; Heller & Yariv, 1969). N o doubt the aquo-complexes are acids, but, the hydrolysis of aquo-complexes is not a 'spontaneous' ionization. Rather, the H + is 'pulled off' by an approaching base (Reutov, 1967). Therefore, the hydrolysis of an aquo-complex by an approaching base can be formulated as follows: [M(H 2O),] +" + n B ~ M(OH),, + nHB + Unfortunately, whenever there is a question of hydrolysis of aquo-complexes under the influence of a base most of the workers consider only the left hand side of the equation. But the reaction will also proceed further to the right on clay surfaces if Note 333 the hydroxide, M(OH)n, is removed as insoluble precipitate. This is especially true for trivalents and divalents and has been confirmed by Russell (1965) and Laura & Cloos (1975b). Consequently, the degree and extent of protonation of bases on montmorillonite saturated with trivalents and divalents might not be a true index of the acidity of the water coordinated to these cations. The development of acid colour occurs on basic surfaces too. Morton & Bolton (1953) observed that on organo-sodium reagents, potassium and sodium hydroxide surfaces, those azo indicators which have a replaceable hydrogen will give the acid colour, probably due to the replacement of the hydrogen of the azo indicator by the alkali-metal cation. In the experiments of Henmi & Wada (1974) this phenomenon cannot be completely excluded. Moreover, on montmorillonite saturated with alkali metal cations there is no protonation of NH 3 (Russell, 1965) and ethylenediamine (Laura & Cloos, 1975a). All the indicator bases used by Henmi & Wada (1974) have pKa lower than that of NH4+ and consequently are not expected to protonate on montmorillonite saturated with alkali metal cations. The number of acid sites in montmorillonite should be equal to its cation exchange capacity. The estimation of the number of acid sites by n-butylamine titration method involves the protonation of amine by proton sources on montmorillonite surfaces. n-Butylamine has a pKa = 10.61 and is expected to take all protons from H- and NH4-montmorillonite. Cloos, Laura & Badot (1975) observed a stoichiometric transfer of protons from NH4-montmorillonite to ethylenediamine (pKa = 10.65) even in aqueous suspension. In case of trivalent ions also there might be a supply of protons equal to cation exchange capacity, because in Al-montmorillonite AI(OH)3 is precipitated quantitatively (Russell, 1965) and the same could be expected for Fe-montmorillonite. However, from the pKa of aquo-complexes of divalent and monovalent ions (e.g. [Mg(H20)x] 2+ = 11.4; [Ca(H20)x] 2+ = 12-7; [Na(H20)x] + = 14-6) it is not expected that montmorillonites saturated with these cations could protonate n-butylamine. Any adsorption of protonated amine in these clays could be only due to preferential adsorption of the organic cations in interlamellar space as argued by Farmer & Russell (1967) and confirmed by Laura & Cloos (1975a, b). Moreover, Benesi (1957) found only 4 and 9 ~ adsorption of amine (of the total cation exchange capacity) on Na- and Ca-montmorillonite respectively. It would also have been very interesting if Henmi & Wada (1974) had determined the number of acid sites on Cu-montmorillonite by the amine titration method. Moreover, even if there is no precipitation of hydroxides on hydrolysis of aquocomplexes, hydroxyl will form inner-sphere complexes. HO OH 2 H20 OH 2 HO OH 2 H20 OH 2 \ / H20--A1--OH / \ \ / HO--Ca--OH / \ H20 OH 2 H20 OH 2 \ / HEO--Na---OH / \ In inner-sphere complexes, the negative ion (anion) is immediately adjacent to the cation. Thus, the charge of the cation is mainly neutralized by the anion itself and 334 Note the r e m a i n i n g water molecules are little affected irrespective o f the n a t u r e o f the central m e t a l cation. Consequently, it can be said t h a t the different exchangeable cations m a y affect differently only the degree o f dissociation o f c o o r d i n a t e d water b u t n o t the extent. Since the charge o f the exchangeable cations is i n v a r i a b l y equal to the c a t i o n exchange c a p a c i t y o f the clay, the available p r o t o n w o u l d never exceed t h a t limit even if every t y p e o f cation increases the degree o f dissociation o f coo r d i n a t e d water on clay surfaces. The p h e n o m e n o n o f p r o t o n a t i o n o f organic bases is very i m p o r t a n t to chemists, clay mineralogists a n d soil scientists. Short b u t informative reviews on this subject have been r e p o r t e d b y L a u r a (1974, 1975). R. D. LAURA D e p a r t m e n t o f Chemistry, University o f Georgia, Athens, G e o r g i a 30602, U.S.A. 2 April, 1976 REFERENCES BENESIH.A. (1956) J. Am. chem. Soc. 78, 5490. BENESIH.A. (1957) J. Phys. Chem. 61, 970. CX-IAUSSIDONJ. & CALVETR. (1965) J. Phys. Chem. 69, 2265. CLOOSP. & LAURAR.D. (1972) Clays Clay Miner. 20, 259. CLOOSP., LAURAR.D. & BADOTC. (1975) Clays Clay Miner. 23, 417. 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Faraday Soc. 61, 2284. RUSSELLJ.D. & FARMERV.C. (1964) Clay Miner. Bull. 5, 443. RUSSELLJ.D. & FRASERA.R. (1971) Clays Clay Miner. 19, 55. RUSSELLJ.D., CRUZ M.I. & WHrrE J.L. (1968) J. Agric. Food Chem. 16, 21. YARIV S. & HELLERL. (1973) Clays Clay Miner. 21, 199. YAmV S., HEELERL. & KAUVI-IERRN. (1969) Clays Clay Miner. 17, 301. YArUVS., HEELERL., SOF~RZ. & BODENI-IEIMERW. (1968) Israel J. Chem. 6, 741.