Clay Minerals (1994) 29, 17%189 THE COMPETITIVE ADSORPTION OF METHYLENE BLUE ON TO MONTMORILLONITE FROM BINARY SOLUTION WIH THIOFLAVIN T, P R O F L A V I N E AND ACRIDINE YELLOW. STEADY-STATE AND DYNAMIC STUDIES C. BREEN AND B . ROCK* Materials' Research Institute, Sheffield Hallam University, Pond Street, Shefffield S1 1WB, UK (Received 17 February 1993; revised 28 September 1993) A B S T R A C T : Methylene blue (MB) has been used as a probe molecule to examine how the uptake dynamics and the equilibria between this dye and the surface of Na +- and H +- montmorillonite were affected by the presence of a second dye~To prevent spectral interference, the yellow dyes thioflavin T, TFT, proflavine, PFH, and acridine yellow, ACY, were chosen to compete with MB for the exchange sites. The MB was initially adsorbed as trimer (MB +)3 and then redistributed via collisions between clay particles until equilibrium was reached. At equilibrium in the clay/MB systems, the protonated species (MBH2+) predominated at low loadings (1-5% CEC), whereas at higher loadings the trimer (MB+)3 was the major species. The presence of the second, competing dye slowed the approach to equilibrium, significantly reduced the amount of MBH2+ formed and provided evidence for the monomeric MB +, dimeric (MB+)2, and trimeric (MB+)3 forms of MB. Moreover, the presence of PFH and ACY, which are structurally similar to MB, resulted in more dimeric character in the aggregated form of MB compared to the aggregate formed in the presence of the structurally dissimilar TFT. The adsorption of methylene blue (MB), which is a cationic dye, on to srnectite surfaces has been the subject of considerable investigation due to the utility of the p h e n o m e n o n in determining the presence of smectites (Taylor, 1985), their cation exchange capacity, C E C , (Rytwo et al., 1991) and surface area (Hang & Brindley, 1970). M o r e o v e r , the aggregation behaviour of this dye, the spectral properties of which are summarized in Table 1, on the mineral surface has been revisited several times since the early study by Bergmann & O ' K o n s k i (1963), most recently by Cenens & Schoonheydt (1988), and Yariv et al. (1990). A large n u m b e r of dye molecules aggregate in aqueous solution to minimize their hydrophobic interaction with water and this impairs their utility in photochemical applications. Consequently, if, as some workers suggest (Hang & Brindley, 1970), it were possible to form ordered monolayers of dye molecules on the surface of minerals then this may provide access * Current Address: Domino Amjet Ltd., Bar Hill, Cambridge CB3 8TU, UK to concentrations of m o n o m e r , with its attendant photochemical properties, which are not normally available in aqueous solution. Pursuit of this goal has inspired several recent studies into the adsorption of dye molecules on the surface of clays in addition to those concentrating on methylene blue. Monomeric, dimeric and protonated forms of proflavine (PFH) have been distinguished in clay suspensions (Cenens et al., 1. Band positions (~max) and extinction coefficients (e) of methylene blue (Cenens & Schoonheydt, 1988) TABLE In aqueous solution Species ~'max (nm) E (din3/ mole. cm) MB + 664 95,000 MBH2+ (MB+)2 741 605 697 580 76,000 t32,000 22,000 110,000 (MB+)3 9 1994 The Mineralogical Society Adsorbed on clays k..... (nm) 6_53 673 763 596 718 570 ~ (dm3/ mole. cm) 100,000 116,000 86,000 80,000 30,000 114,000 180 C. Breen and B. Rock + H3C~CH3 HzN/ ~ "-.N--~~ H methylene blue "-NH2 acridine yellow H 2 N ~ N H 2 H H3C~S\ ~L..~L~~ / / ~ - - ~ ~ N(cH3)2 I CH3 proflavine thioflavin T Fl6. 1. Structural formulae of the dye molecules. 1987) a n d in the solid state ( S c h o o n h e y d t et al., 1986). In contrast, the competitive a d s o r p t i o n , a n d resulting p r o p e r t i e s , of mixed-dye clay systems h a v e received little a t t e n t i o n . A v n i r et al. (1986) r e p o r t e d t h a t the clay host facilitated long r a n g e electronic e n e r g y t r a n s f e r f r o m a d o n o r molecule, r h o d a m i n e 6 G , to various fluorescent cationic dyes, acting as acceptors. T h e r e was a m a r k e d e n h a n c e m e n t of energy t r a n s f e r from the d o n o r to the acceptor in the p r e s e n c e of clay c o m p a r e d to a q u e o u s solution, b u t the fluorescence of r h o d a m i n e 6 G was r e d u c e d due to q u e n c h i n g by t h e acceptor. Margulies et al. (1988) studied the competitive a d s o r p t i o n of M B a n d thioflavin T (TFT) f r o m aqueous solution a n d fitted m a t h ematical models to t h e i r a d s o r p t i o n isotherms. U n f o r t u n a t e l y , they did n o t t a k e a d v a n t a g e of the excellent p r o p e r t i e s of M B as a p r o b e molecule, described in detail by C e n e n s & S c h o o n h e y d t (1988), to confirm the data derived from t h e i r model. It is interesting to n o t e that the same workers h a v e s h o w n t h a t clay l o a d e d with dyes such as T F T a n d proflavine ( P F H ) are able to p h o t o s t a b i l i z e insecticides in which t h e active g r o u p is also p h o t o l a b i l e (Margulies et al., 1988). W e h a v e studied the c o m p e t i t i v e a d s o r p t i o n of M B from a q u e o u s binary solution with T F T , P F H a n d acridine yellow ( A C Y ) on to N a +- a n d H +exchanged, low-iron m o n t m o r i l l o n i t e . O u r interp r e t a t i o n s are b a s e d u p o n the effect t h a t the second dye has o n the very i n f o r m a t i v e spectral signature of the p r o b e molecule, M B . T h e c o m p e t i n g dyes, the structural f o r m u l a e for which are given in Fig. 1, w e r e c h o s e n because: (i) they a b s o r b in the r a n g e 412-430 n m a n d thus do n o t interfere with the wide spectral r a n g e of M B a n d its aggregates (570-770 n m ) ; M B , P F H a n d A C Y are structurally similar to each o t h e r w h e r e a s T F T is dissimilar, thus the effect of c o m p e t i n g dye s t r u c t u r e can b e studied: a n d (iii) the a d s o r p t i o n of P F H a n d T F T o n to clay has b e e n studied previously ( C e n e n s et al., 1987; Margulies et al., 1988) thus e n a b l i n g cross c o m p a r i s o n . EXPERIMENTAL T h e Texas b e n t o n i t e , d o n a t e d by English C h i n a Clays I n t e r n a t i o n a l , h a d a C E C of 100 m E q / 1 0 0 g clay. T h e n o m i n a l l y < 2 ~tm fraction was separated by s e d i m e n t a t i o n a n d a small p o r t i o n used w i t h o u t c o n v e r s i o n to t h e N a + - f o r m . X-ray fluorescence analysis of a fused glass b e a d of this m a t e r i a l indicated t h a t the e x c h a n g e cations were 80% C a 2+ a n d 20% N a +. This sample is subsequently r e f e r r e d to as Ca2+/Na +. T h e r e m a i n d e r of t h e < 2 ~tm fraction was c o n v e r t e d to the N a +f o r m by washing t h r e e times with 1 M NaCI. T h e resulting suspension was r e p e a t e d l y w a s h e d with d e i o n i z e d w a t e r ( p H --5.0) a n d centrifuged at 20,000 r p m until t h e residual conductivity was < 2 0 ~tS. T h e centrifugate was r e - s u s p e n d e d in deionized w a t e r a n d the < 0 . 3 ~tm fraction was collected by centrifugation. T h e resultant suspension, which h a d a clay c o n t e n t of 5 g d m -3, was divided into two portions. O n e p o r t i o n was used as the stock Competitive adsorption of dyes on clays N a + - e x c h a n g e d f o r m whilst the o t h e r p o r t i o n was stirred for 2 h at 20~ after the a d d i t i o n of sufficient 2 mol d m 3 H 2 S O 4 to give an H + c o n c e n t r a t i o n of 0.15 mol d m -3 (30 C E C ) . A f t e r acid t r e a t m e n t , this H + - m o n t m o r i l l o n i t e was w a s h e d with d e i o n i z e d w a t e r until the p H of the s u p e r n a t a n t was > 4 . B r e e n (1991) has s h o w n t h a t a Texas b e n t o n i t e t r e a t e d in a similar m a n n e r retains its structural integrity. P r e p a r a t i o n of clay-dye s u s p e n s i o n was identical to the m e t h o d of C e n e n s & S c h o o n h e y d t (1988) in which t h e c o n c e n t r a t i o n of M B was m a i n t a i n e d at 2.5 x 10 -6 mol d m -3 to p r e v e n t dye aggregation in solution prior to a d s o r p t i o n o n to t h e clay. T h e a m o u n t of dye available to the clay was increased by r e d u c i n g the a m o u n t of clay p r e s e n t in suspension. Initial studies i n d i c a t e d t h a t low loadings of dye o n H + - m o n t m o r i l l o n i t e , w h i c h w e r e realized by a h i g h c o n c e n t r a t i o n of clay in suspension, r e q u i r e d t h e use of a m o r e c o n c e n t r a t e d buffer solution t h a n t h a t used by C e n e n s & S c h o o n h e y d t (1988). T h u s all the d y n a m i c a n d a d s o r p t i o n studies w e r e carried o u t in solutions which c o n t a i n e d 10 cm 3 of a 0.1 tool d m -3 s o d i u m acetate/acetic acid buffer at p H 4 a n d 10 cm 3 of 10 -5 mol d m -3 dye solution to which was a d d e d sufficient w a t e r to e n s u r e t h a t after a d d i t i o n of clay suspension t h e final v o l u m e was 40 cm 3. In competitive studies, 10 cm 3 of a 10 5 mol d m 3 solution of the s e c o n d dye ( T F T , A C Y , P F H ) was a d d e d a n d t h e a m o u n t of w a t e r r e d u c e d by the s a m e a m o u n t to m a i n t a i n a total v o l u m e of 40 cm 3. All t h e m i x t u r e s were p r e p a r e d in n e w p o l y e t h y l e n e vessels to minimize adsorption in cracks. O n c e p r e p a r e d , t h e samples were placed in a n orbital shaking b a t h , o p e r a t i n g at 250 r p m , at 25~ for a m i n i m u m of 16 h, sufficient for equilibrium to b e established u n d e r these experim e n t a l conditions. S u b s e q u e n t to recording the spectra of t h e clay-dye suspensions the a m o u n t of M B in the s u p e r n a t a n t was d e t e r m i n e d , after r e m o v i n g t h e clay by c e n t r i f u g a t i o n at 20,000 r p m for 100 min, using visible spectroscopy. A b s o r p tion spectra of M B a n d mixed-dye clay suspensions were r e c o r d e d in the r a n g e 300-800 n m against p u r e w a t e r with a Phillips P U 8 7 2 0 spect r o p h o t o m e t e r . T h e spectra of t h e p u r e clay suspensions were s u b t a c t e d f r o m those of t h e c o r r e s p o n d i n g clay-dye materials to o b t a i n the spectra of a d s o r b e d dye only. This s u b t r a c t i o n e l i m i n a t e d t h e b a c k g r o u n d due to light scattering by t h e clay particles. 181 RESULTS Figure 2 illustrates t h e striking c o n t r a s t b e t w e e n the a b s o r p t i o n spectra of a 2.5 • 10 -6 tool d m -3 solution of M B in t h e a b s e n c e of clay (Fig. 2a), a n d in the p r e s e n c e of sufficient clay to give M B loadings of 1% a n d 50% of the C E C (Figs. 2b,2c, respectively). This d i a g r a m shows quite clearly t h a t M B was n e i t h e r p r o t o n a t e d n o r did it exhibit any m e t a c h r o m i c b e h a v i o u r in t h e b u f f e r solution utilized, a n d this was the case for TFT, A C Y a n d P F H also. U s i n g t h e a s s i g n m e n t s of C e n e n s & S c h o o n h e y d t (1988), given in T a b l e 1, it is clear t h a t w h e n e q u i l i b r i u m is r e a c h e d at a loading of 1% C E C the M B is all in the M B H 2+ form, ~ - m a x = 770 n m , (Fig. 2b), w h e r e a s at a loading of 50% C E C the trimeric f o r m of M B , (MB+)3; Xmax = 570 n m , d o m i n a t e s t h e s p e c t r u m (Fig. 2c). Dynamic studies Figure 3 indicates h o w t h e a b s o r p t i o n s p e c t r u m for M B o n H + - m o n t m o r i l l o n i t e at 2.0% of the C E C varied as a function of time. Two m i n u t e s after a d d i n g the r e q u i r e d a m o u n t of clay suspension to t h e b u f f e r e d dye solution, m o s t of t h e dye was p r e s e n t as a d s o r b e d t r i m e r (Xmax = 570 rim). A f t e r 5 m i n agitation, an a p p r e c i a b l e a m o u n t of M B H 2+ (X. . . . = 770 n m ) h a d b e e n f o r m e d , a n d this b a n d c o n t i n u e d to increase at t h e expense of t h e t r i m e r b a n d at 570 n m . This b e h a v i o u r was 0.30 a b i i I o ~ 0.15 ! I c u~ az < 0 400 J 600 i00 ),/nm FIG. 2. Absorption spectra for 2.5 x 10 6 mol dm 3 methylene blue buffered at pH 4 in the absence of clay (a), and in the presence of sufficient H+-montmorillonite to give a loading of 1% CEC (b), and 50% CEC (c), respectively. C. Breen and B. Rock 182 0.3 H+.-H B a 1.0 =o 0.2 8 0.5 r-. r'~ r 0 o3 ,.0 < m5% 0.1 b 0 200 ' b I ~00 I00 400 H+--H B+TFT 1.0 I00 600 3~0 Timelmin klnm Fl6. 3. Time dependence of the visible spectrum of methylene blue on H+-montmorillonite at a loading of 2.0% of CEC (a) 2 min, (b) 5 min, (c) 35 min, (d) 130 min and (e) 410 rain. o b s e r v e d with all the samples which e x h i b i t e d a b a n d for M B H 2+ at e q u i l i b r i u m including those using N a + - m o n t m o r i l l o n i t e a n d mixed M B / d y e sytems. A d j u s t i n g the solution c o m p o s i t i o n s accordingly it was d e t e r m i n e d that, within the accuracy of t h e e x p e r i m e n t , the rate of M B H 2+ f o r m a t i o n increased with increasing clay c o n t e n t b u t was i n d e p e n d e n t of t h e a q u e o u s dye concentration. Figure 4 shows h o w the a b s o r b a n c e of the M B H 2+ b a n d at 770 n m , n o r m a l i z e d to the a b s o r b a n c e value at equilibrium, varied with time in single a n d mixed dye systems. T h e rate at which M B H 2+ was f o r m e d d e c r e a s e d with increased dye loading, which p r o b a b l y reflects the c o n c o m i t a n t decrease in clay c o n c e n t r a t i o n necessary to achieve these higher loadings. F u r t h e r m o r e , the rate of f o r m a t i o n of M B H 2+ was slower on the less acidic N a + - m o n t m o r i l l o n i t e a n d was markedly r e d u c e d in the p r e s e n c e of a second, c o m p e t i n g dye (Fig. 4b). A t t e m p t s to fit the rate data to simple first- a n d s e c o n d - o r d e r kinetic f o r m u l a t i o n s which considered b o t h t h e p r e s e n c e and a b s e n c e of an equilibrium, w h e r e appropriate, were unsuccessful. Equilibrium studies--single dye adsorption Figure 5 shows t h a t as the loading of M B increased from 5% to 50% of the C E C , the ~ 0.5 m5+5% o 2'6o 360 Time/min FIG. 4. Time dependence of the absorbance of the MBH 2+ band (770 nm) for the systems (a) H+-montmorillonite/ methylene blue and (b) H+-montmorillonite/methylene blue/thioflavin T. 0.30 0 .e 0.15 o,?, %CEC so o.. /.X ~ /7'x / \/I 12. s 600 600 BOO k/nm FIG. 5. Variation of the visible absorption spectrum of methylene blue on H+-montmorillonite as a function of the equilibrium dye toadings indicated. 183 Competitive adsorption of dyes on clays intensity of t h e characteristic M B H 2+ b a n d at 770 n m d e c r e a s e d a n d t h a t of t h e trimer, (MB+)3, at 570 n m increased. Careful inspection of the relative p e a k intensities a n d t h e a s y m m e t r y of p e a k s indicated t h a t as t h e loadings i n c r e a s e d m o n o m e r i c (kma• = 660 n m ) a n d dimeric species (X~nax = 596 n m ) occurred. F o r e x a m p l e , C e n e n s & S c h o o n h e y d t (1988) r e p o r t e d t h a t the relative a b s o r b a n c e s of the b a n d s at 7 7 0 , 6 8 0 a n d 620 n m , which are v i b r o n i c c o m p o n e n t s of a d s o r b e d M B H 2+, are 1.00 : 0.52 : 0.17, respectively. T h u s , w h e n the ratio of the b a n d s at 770 n m a n d 680 n m was n o t --2 : 1, t h e n t h e additional intensity n e a r 680 n m was t a k e n to indicate t h e p r e s e n c e of M B + n e a r 660 nm. M o r e o v e r , an assymetry o n t h e high w a v e l e n g t h side of the 570 n m , (MB+)3, b a n d was a t t r i b u t e d to a small a m o u n t of d i m e r , (MB+)2, b e c a u s e its a b s o r b a n c e was t o o high to b e a t t r i b u t e d to t h e M B H 2+ vibronic c o m p o n e n t at 620 nm. T h e close proximity of t h e a b s o r p t i o n b a n d s of the m o n o m e r , d i m e r a n d p r o t o n a t e d species of T F T , A C Y a n d P F H p r e c l u d e d any definitive resolution of the a b s o r p t i o n b a n d s in the 400-460 nrn range. T h u s the changes in ~-max for the principal a b s o r p t i o n b a n d s a n d t h e i r respective a b s o r b a n c e values for the clay/TFT a n d clay/MB/ T F T systems are illustrated in Fig. 6. H o w e v e r , as t h e p r i m e objective was to study the effect of t h e second dye o n the a b s o r p t i o n s p e c t r u m of M B , n o a t t e m p t was m a d e to ascribe changes in p r o t o n a tion a n d / o r aggregation to t h e s e variations a l t h o u g h this has b e e n c o n s i d e r e d by o t h e r s ( C e n e n s et al., 1987; C o h e n & Yariv, 1984; G r a u e r et al., 1987). t 70 I:= r x E e< " I 0 g 0.0 o 50 [TFT]o/%CEC 100 Vv 0.0 Equilibrium studies--mixed dye adsorption T h e c o m p e t i t i v e a d s o r p t i o n studies were carried o u t using e q u i m o l a r c o n c e n t r a t i o n s of M B plus the s e c o n d dye (TFT, A C Y , P F H ) in which t h e final a q u e o u s c o n c e n t r a t i o n of each dye was 2.5 X 10 _6 mol d m 3. T h e dye loadings in these b i n a r y systems will b e p r e s e n t e d s u b s e q u e n t l y as (1 + 1)% which d e n o t e s 1% loading of M B a n d 1% loading of t h e second dye. Figure 7 c o m p a r e s t h e a b s o r p t i o n s p e c t r u m of M B a n d T F T , b o t h p r e s e n t at 12.5% C E C , a d s o r b e d o n H + - m o n t morillonite with M B a l o n e o n the same a d s o r b a t e at loadings of 12.5% a n d 25% C E C . Clearly, the a m o u n t of M B H 2+ f o r m e d in the p r e s e n c e of 50 [TFT] o / ~ CEC 100 FIG. 6. Variation of (a) k..... and (b) absorbance as a function of loading of thioflavin T (TFF) alone and in binary mixture with methylene blue (MB) on Na +- and H § montmorillonite. A H+/TFT; (3 Na+/TFT; 9 H+/TFT/ MB; (1 Na+FFFT/MB; [] dual point. In the binary systems, the abscissa represents the equimolar amount of each dye present in the initial mixture. e q u i m o l a r a m o u n t s of M B a n d T F T was significantly less t h a n t h a t f o r m e d at e i t h e r 12.5% or 25% loading in the p r e s e n c e of M B alone. M o r e o v e r , the a b s o r p t i o n b a n d n e a r 600 n m in 184 C. Breen and B. R o c k the M B / T F T system was red shifted c o m p a r e d to the single dye system and the relative intensities of the bands at 690 and 770 nm (which should be in the ratio of 2 : 1 in the absence of m o n o m e r , MB +) indicated that, in contrast to when MB was adsorbed alone, there was m o n o m e r present. The spectrum for the second dye in the region 400--460 nm did change slightly with loading (Fig. 6) but the change was not sufficient to warrant replotting the spectrum at each loading. After careful consideration of many single and mixed-dye systems in the presence of clay it was determined that the extinction coefficients reported by Cenens & Schoonheydt (1988) were applicable and thus permitted the calculation of the amount of M B H 2§ formed. Figure 8 shows, as anticipated, that the acid-treated clay contained m o r e sites capable of protonating MB + to M B H 2+ than both the sedimented Ca~+/Na + and the Na+-form. These observations are in good agreement with data reported by other workers for the synthetic mica-montmorillonite, Barasym (Cenens & Schoonheydt, 1988) and Cu 2§ exchanged montmorillonite (Yariv & Lurie, 1971). Clearly, the presence of the second dye severly reduced the amount of M B H 2+ formed as illustrated in Fig. 7. T h e r e was a small, but significant, difference between the a m o u n t of M B H e+ formed in the presence of T F T and A C Y , whilst P F H suppressed the protonation of MB to 1% of the C E C for the H+-montmorillonite. 2 ~ 10 m ~: 5 50 100 [H B+]o/%CEC FIG. 8. Variation of [MBH2+] with methylene blue loading for a selection of single and binary dye systems in the presence of Na +- and H+-montmorillonite. Inset: Expanded portion detailing the results for Na+-montmoril lonite. A H+/MB; 9 (Ca2+/Na+)/MB; C) Na+/MB; 9 H+/ MB/TFT; 9 H+/MB/ACY; 9 Na+/MB/ACY. In the binary systems the abscissa represents the equimolar amount of each dye present in the initial mixture. Further information concerning the adsorption behaviour of MB in the binary dye systems can be obtained from a study of the kroax value for the band near 580 nm. Cenens & Schoonheydt (1988) were able to attribute absorption bands near 600 nm and 570 nm to dimer, (MB+)e, and external trimer, (MB+)3, respectively. Consequently, a plot of km,x, in the 570-620 nm region, vs. % C E C should provide evidence concerning the state of aggregation of MB. Figure 9 uses the H +0.30 m o n t m o r i l l o n i t e / M B / T F T system to illustrate both the spectral quality in the binary dye systems and how, as the loading increased, the intensity of the band at 580 nm increased whilst that at 770 nm decreased ( c f Fig. 5). The inset in Fig. 9 shows that at low loadings of MB and TFT, the rr dominant MB aggregate was, following Cenens & Schoonheydt's assignments (1988), the dimer 0 (k~n~x = 595-605 nm). H o w e v e r , as the MB and t,"n T F T loadings both approached 12.5% of the <~ CEC, ~'maxm o v e d to a value diagnostic of the HB trimer before increasing again as the loading m o v e d to higher values. A t loadings above (50 + 50)% C E C , both MB and T F T were determined in the supernatant; thus, the values of ~ m a x n e a r /+00 600 800 620 nm were probably influenced by unabsorbed, aqueous phase MB + m o n o m e r , which exhibits Xlnm two bands in the absorbance ratio 1 : 2 at 618 and FIG. 7. Comparison of the visible absorption spectra for methylene blue alone and in binary mixture with thioflavin 664 nm, respectively. T on H+-montmorillonite at the loadings indicated. Figure 10a builds on Fig. 9 and compares how 0~25.0% 0.1s 12.5%HB+12.S%TFT //~/I' 185 Competitive adsorption of dyes on clays 630 030 62~F ' e,~. / r o W 0.15 0 rt~ E 600 x .< i:: 400 570i BOO ~/nm FIG. 9. Variation of the visible absorption spectrum of 600 0 methylene blue from binary solution with thioflavin T as a function of dye loading on H+-montmorillonite. Inset: The variation of ~.maxfor the aggregated form of methylene blue as a function of dye loading. the value of ~-rnax, for the a g g r e g a t e d forms of M B , in the region 560~530 n m varied with dye loading for b o t h the single a n d b i n a r y dye systems in the p r e s e n c e of H + - m o n t m o r i l l o n i t e . H o w e v e r , these values should n o t b e c o n s i d e r e d i n d e p e n d e n t l y of the c o r r e s p o n d i n g a b s o r b a n c e values which are plotted in Fig. 10b. In the a b s e n c e of a s e c o n d dye, n o a d s o r b e d (MB+)3 was o b s e r v e d until the loading o n H + - m o n t m o r i l l o n i t e e x c e e d e d 5 % C E C (Fig. 5), a n d this b e h a v i o u r is reflected by t h e o p e n triangles in Fig. 10a,b. T h u s , up to a M B loading of 25% C E C , any aggregate p r e s e n t was the e x t e r n a l t r i m e r (Xmax = 570 n m ) . A b o v e this loading the Xma• value b e g a n to increase a l t h o u g h the a b s o r b a n c e value stabilized. In the p r e s e n c e of a s e c o n d dye t h e initial values for b o t h ~ m a x a n d a b s o r b a n c e were higher, reflecting the p r e s e n c e of aggregated M B . Figure 8 s h o w e d t h a t the a m o u n t of M B H 2+ f o r m e d in the p r e s e n c e of a second dye varied as T F T > A C Y > P F I - I . This same s e q u e n c e was e v i d e n t h e r e insofar as t h e m i n i m u m in the kmax vs. % C E C curve follows t h e sequence TFT<ACY<PFH. Incidentally, t h e m a x i m a n e a r 600 n m in t h e spectra for H +montmorillonite/ACY/MB and H+-montmoril l o n i t e / P F H / M B were m u c h b r o a d e r t h a n t h o s e for H + - m o n t m o r i l l o n i t e / T F T / M B . This m a y indicate t h a t at loadings below (25 + 25)% t h e r e was significantly m o r e (MB+)2 p r e s e n t w h e n t h e dye ~ ~ ' 50 100 [H B+]o/%GEe m ,--~ 0.1 (~ t.--O ~ -- I ~0.05 A:l < 0 I I 50 I ~00 [H B+10/%CEC FIG. lO. Variation of (a) ~-max and (b) absorbance for the aggregated form of methylene blue (MB) as a function of loading of MB alone (ZS) and in binary mixture with thioftavin T (V), acridine yellow (&) and proflavine ([3) on H+-montmorillonite. In the binary systems the abscissa represents the equimolar amount of each dye present in the initial mixture. in c o m p e t i t i o n with M B was A C Y or P F H t h a n w h e n T F T was used. A t loadings in which b o t h M B a n d the second dye were in excess of 50% of the C E C , t h e value of ~-maxwas influenced by t h e p r e s e n c e of the a q u e o u s M B b a n d at 660 n m . V e r y similar o b s e r v a t i o n s were m a d e w h e n the 186 C. Breen and B. R o c k a b s o r p t i o n spectra of b i n a r y dye mixtures were recorded after equilibration with Na + - m o n t m o r i l l o n i t e . T h e equilibrium loadings of t h e dye molecules r e c o r d e d in b o t h the single dye/clay systems a n d the mixed-dye/clay systems are p r e s e n t e d in T a b l e 2 a n d it is i m m e d i a t e l y obvious t h a t the loadings always e x c e e d e d the C E C of t h e clay (100 m E q / 1 0 0 g clay). In general Na+-clay a d s o r b e d 5 - 1 0 % m o r e dye t h a n H+-clay a n d t h e a m o u n t of single dye a d s o r b e d increased as ACY>MB>TFT>PFH. In the c o m p e t i t i v e e x p e r i m e n t s M B was always a d s o r b e d in slight p r e f e r e n c e to T F T and P F H , b u t t h e r e was little distinction b e t w e e n the a m o u n t of M B a n d A C Y adsorbed. DISCUSSION B o t h the d y n a m i c a n d e q u i l i b r i u m studies cond u c t e d here confirm t h a t M B t e n d e d to aggregate on the clay surface e v e n t h o u g h the a q u e o u s c o n c e n t r a t i o n (2.5 • 10 - 6 mol d m 3) was m u c h lower t h a n t h a t n o r m a l l y r e q u i r e d for m e t a c h r o matic b e h a v i o u r . In water, M B readily forms dimers at c o n c e n t r a t i o n s as low as 10 -5 mol d m -3. T h u s the clay, w h e t h e r it was in the Na +- or H + - f o r m , exerted a c o n c e n t r a t i n g effect u p o n M B as suggested by previous investigators ( B e r g m a n n & O ' K o n s k i , 1963; C e n e n s & S c h o o n h e y d t , 1988). M o r e o v e r , the clay in this study p r o d u c e d little e v i d e n c e of a d s o r b e d m o n o meric M B +, in the single clay dye systems, which TABLE2. Maximum adsorption capacities (mEq/100 g clay) for single and binary dye mixtures adsorbed on clay. Exchange cation MB 158(95) - Na + TFT ACY TOTAL 73(90) - 185 96 158 145 185 171 196 - - 140 131 178 170 184 145(110) - - 98(20) 100 140 - H+ 1 3 1 - 93 91 - - 77 - 178 93 Values in parentheses from Margulies et al. (1988) contrasts with b o t h t h e earlier cited work a n d o t h e r studies in these l a b o r a t o r i e s o n different clays. G r e a t e r difference was initially e x p e c t e d b e t w e e n the a g g r e g a t i o n b e h a v i o u r of M B o n the N a +- a n d H + - e x c h a n g e d forms since a difference in tactoid size, a n d / o r floc s t r u c t u r e h a d b e e n anticipated. H o w e v e r , B a n i n & S h a k e d (1969) r e p o r t e d t h a t freshly p r e p a r e d H + - m o n t m o r i l l o nite is well dispersed a n d each tactoid c o n t a i n e d only o n e or two plates, which m a y explain w h y t h e H + - f o r m used in this study s h o w e d little t e n d e n c y to form visible flocs. M o r e o v e r , it was necessary to use a higher ionic s t r e n g t h buffer (0.025 mol d m -3) in these studies, c o m p a r e d to t h a t utilized by C e n e n s & S c h o o n h e y d t (1988) b e c a u s e of the acidity of the H + - f o r m . It is c o n c e i v a b l e t h a t this c o m p r e s s e d the thickness of the d o u b l e layer to the same e x t e n t in b o t h cationic forms a n d thus controlled the initial surface available for adsorption of M B . Finally, it is p e r t i n e n t to n o t e t h a t the dye itself m a y control the available surface. X i a n g et al. (1992), using scanning e l e c t r o n microscopy, h a v e o b s e r v e d g l o b u l a r particles (ca. 5 ~tm in d i a m e t e r ) in air-dried samples of Ca2+-exchanged m o n t m o r i l l o n i t e in which 50% of the exchange cations have b e e n replaced by m e t h y l viologen. S c h o o n h e y d t & H e u g h e b a e r t (1992) h a v e recently s h o w n t h a t , at low loadings o n N a +L a p o n i t e , M B molecules are a d s o r b e d o n the first sites t h a t they e n c o u n t e r d u e to t h e i r e x t r e m e l y high affinity for the clay surface. If aggregates of clay platelets occur, it was suggested that adsorption would occur p r e d o m i n a n t l y o n the e x t e r n a l surface of these aggregates, followed by: (i) slow m i g r a t i o n of the M B molecules o v e r the surface to assume an e q u i l i b r i u m distribution, (ii) rearr a n g e m e n t of t h e clay aggregates; or (iii) simult a n e o u s occurrence of b o t h p h e n o m e n a . Schoonh e y d t & H e u g h e b a e r t (1992) p r e f e r r e d process (ii) b e c a u s e V i a e n e etal. (1987, 1988) s h o w e d t h a t the r e o r g a n i z a t i o n of the fluorescent p r o b e [3-(1pyrenyl)propyl]trimethylammonium, a much b u l k i e r cation, o v e r t h e surface o c c u r r e d o n a time scale of 500-1000 s. T h e rate of f o r m a t i o n of M B H 2+ on b o t h N a + - m o n t m o r i l l o n i t e a n d H +m o n t m o r i l l o n i t e in this study was linearly d e p e n dent o n clay c o n c e n t r a t i o n , b u t i n d e p e n d e n t of dye c o n c e n t r a t i o n . T h e r e f o r e , given (i) the high ionic s t r e n g t h used h e r e a n d (ii) t h a t p r e l i m i n a r y studies indicated t h a t the rate of M B H 2+ formation increased w h e n the suspensions were s h a k e n , it is clear t h a t the aggregated dye molecules m u s t Competitive adsorption of dyes on clays c o m e into contact with p r o t o n sites a n d b e transfel?red. I n d e e d the o b s e r v a t i o n s m a d e in this study are c o m m e n s u r a t e with a m e c h a n i s m in which the a g g r e g a t e d dye molecules o n t h e external surface c o m e into contact with p r o t o n s o n basal surfaces of s e p a r a t e particles w h e n t h e aggregates collide with o t h e r aggregates or particles. If r e d i s t r i b u t i o n of (MB+)3 o c c u r r e d by migration within, or r e a r r a n g e m e n t of, a single floccule t h e n the rate of M B H 2+ f o r m a t i o n would b e i n d e p e n d e n t of clay c o n c e n t r a t i o n . M o r e o v e r , since n o free M B + was o b s e r v e d at the low loadings used for t h e d y n a m i c studies a n d the rate of M B H e+ f o r m a t i o n was i n d e p e n d e n t of the initial M B c o n c e n t r a t i o n , t h e n clearly a d s o r b e d t r i m e r was i n v o l v e d in the distribution process. Clearly, as Fig. 2 shows, n o M B is p r o t o n a t e d in the a b s e n c e of clay at p H 4 a n d thus the clay m u s t b e the source of p r o t o n s . F u r t h e r m o r e , N a +m o n t m o r i l l o n i t e has fewer p r o t o n sites t h a n H +m o n t m o r i l l o n i t e a n d the rate of f o r m a t i o n of M B H 2+ was slower o n N a + - r n o n t m o r i l l o n i t e at t h e same M B loading. T h u s the n u m b e r of available p r o t o n s was a crucial factor as would b e a n t i c i p a t e d if t h e floc structure is a s s u m e d to b e identical. T h e c o n c e p t of dye t r a n s f e r b e t w e e n dyel o a d e d and dye-free particles was first suggested by Yamigishi & S o m a (1981) to explain t h e i r results for n-alkylated acridine orange. T h e s e w o r k e r s were able to describe this t r a n s f e r process by simple s e c o n d - o r d e r kinetics in which the initial c o n c e n t r a t i o n s of dye a n d clay were n o t identical. In this study, with the e x c e p t i o n of very low dye loadings, a n e q u i l i b r i u m was established usually involving the trimer, d i m e r a n d M B H 2+ , a l t h o u g h at i n t e r m e d i a t e loadings, some e v i d e n c e for the the m o n o m e r was also o b t a i n e d (vide infra). C o n s e q u e n t l y , n o single kinetic f o r m u l a tion would b e e x p e c t e d to fit the data at all loadings. H o w e v e r , as stated previously, n o success was a c h i e v e d in fitting data at low loadings to any realistic formulation. Figures 7-10 p r e s e n t and s u m m a r i z e the way in which the M B molecules were p r o t o n a t e d a n d aggregated w h e n a d s o r b e d on the clay from b i n a r y mixtures with TFT, A C Y a n d P F H . It is impractical to p r e s e n t all the spectra resulting from the c o m p e t i t i v e a d s o r p t i o n systems, b u t Fig. 10 serves to s u m m a r i z e t h e aggregation b e h a v i o u r of M B in these systems. H o w e v e r , n o 187 single diagram can s u m m a r i z e t h e f o r m s in which M B was o b s e r v e d , a n d t h e r e f o r e T a b l e 3 is included to m e e t this r e q u i r e m e n t . N o t e t h a t t h e a m o u n t of m o n o m e r o b s e r v e d was always small a n d identified only b e c a u s e the 680 n m b a n d a t t r i b u t e d to M B H 2+ was m o r e i n t e n s e t h e n a p p r o p r i a t e a n d t h e d i m e r b a n d s n o t e d for b i n a r y solutions c o n t a i n i n g A C Y a n d P F H were b r o a d a n d p r o b a b l y included a c o n t r i b u t i o n f r o m trimer. Clearly, t h e p r e s e n c e of the second dye decreases t h e a m o u n t of M B H 2+ o b s e r v e d a n d the obvious i n t e r p r e t a t i o n is t h a t the s e c o n d dye c o m p e t e s effectively for the available p r o t o n s . U n f o r t u n a t e l y , it is n o t possible to confirm this b y scrutinizing the spectral shifts of the second dye, as C e n e n s et al. (1987) h a v e shown. T h e y only o b s e r v e d t h e p r o t o n a t e d f o r m of proflavine, PFH22+, ()v.... = 458 n m ) at 0.3% loading b e c a u s e it is n o r m a l l y s w a m p e d by the d i m e r b a n d at 430 n m and the m o n o m e r b a n d at 453 nm. A n o t h e r possibility is t h a t the dye molecules aggregate the clay particles m a k i n g the p r o t o n sites less accessible to t h e i n c o m i n g dye molecules. I n d e e d , p r e l i m i n a r y studies of the t r a n s f e r kinetics of a d s o r b e d (MB+)3, which has b e e n allowed to equilibrate o n the clay surface, to freshly a d d e d dye-free clay indicated t h a t the process was m u c h slower t h a n those r e c o r d e d in Fig. 4. This suggests t h a t the e q u i l i b r a t e d t r i m e r was relatively inaccessible, unlike the initial t r i m e r which was easily r e d i s t r i b u t e d (Fig. 3). This would suggest t h a t e q u i l i b r a t e d (MB+)3 TABLE 3. Summary of the differm~t forms of methylene blue (MB) observed during the competitive adsorption onto H+-clay from binary solution with thioflavin T (TFT), proflavine (PFH) and acridine yellow (ACY). Adsorbed monomer M, dimer D, trimer T, and protonated monomer P. % LOADING MB/TFT MB/ACY MB/ACY 0.5 + 0.5 1.0 + 1.0 2.5 + 2.5 5.0 + 5.0 8.3 + 8.3 12.5 + 12.5 25.0 + 25.0 37.5 + 37.5 50.0 + 50.0 P D,T,P M,D,T,P M,D,T,P M,D,T,P M,D,T,P Ms,D,T,P Ms,D Ms,D M,D,P M,D,P M,D,P M,D,P M,D,P M,D,P M,D,P M,D,P M,D,P M,D,P M,D,P M,D,P M,D M,D M,D MS,D Ms = MB monomer centrifugation. M,D detected in solution after 188 C. Breen and B. Rock ~max value, resides o n the internal surfaces of a c a r d - h o u s e structure consisting of individual particles or tactoids, similar to the structures suggested by Yariv et al. (1991) except t h a t the p l a n e of the dye molecules lie parallel to the p l a n e of t h e basal surface. Figure 11 illustrates h o w ~-max for the aggregated form of M B varied with time for single a n d mixed-dye systems and thus gives an insight into the m e c h a n i s m for dye distribution o v e r the available surface. O n H + - m o n t m o r i l l o n i t e , at 1% a n d 2% loadings of M B , t h e r e was a gradual red shift in k .... with time which was a t t r i b u t e d to the d i s a p p e a r a n c e of the 570 n m b a n d of t h e t r i m e r a n d the increase of the M B H 2+ b a n d at 618 n m . T h e kma• value was c o n s t a n t at 5% loading because, unlike the case at 1% a n d 2 % C E C , the t r i m e r was p r e s e n t at equilbrium. T h e v a r i a t i o n of ~-max with time in the M B f l T ' F binary m i x t u r e exhibited the most m a r k e d time d e p e n d e n c e (Fig. 10b). A t a loading of (1 + 1 ) % , the b a n d shifts from a value diagnostic of the t r i m e r to t h a t for the dimer. A t a loading of (2 + 2 ) % , the shift was in the same direction b u t not so m a r k e d , w h e r e a s w h e n the loading was increased to (5 + 5 ) % , the 610 a H+-MB 600 a l t h o u g h red-shifted slightly, r e m a i n e d characteristic of t h e trimer. T h e variation in w a v e l e n g t h was m i n i m a l in t h e M B / A C Y system a n d t h e final value of ~-max was r e a c h e d very rapidly (Fig. 10c). H o w e v e r , this rapid a t t a i n m e n t of t h e e q u i l i b r i u m value for ~maxm a y mask subtle c h a n g e s in the relative a m o u n t s of d i m e r a n d t r i m e r b e c a u s e this b a n d was quite b r o a d . N o n t h e l e s s , it is satisfying to note t h a t the final values of ~'maxo b t a i n e d in t h e kinetic studies were identical to t h o s e f o u n d in the equilibrium e x p e r i m e n t s e v e n t h o u g h they were p e r f o r m e d using different samples. T h e results f r o m the kinetic a n d e q u i l i b r i u m studies c o n v e r g e to p r o v i d e the following picture of the a d s o r p t i o n a n d r e d i s t r i b u t i o n m e c h a n i s m . T h e majority of M B molecules are initially a d s o r b e d as t r i m e r o n the e x t e r n a l surfaces of the clay a n d t h e r e f o r e the a q u e o u s c o n c e n t r a t i o n of M B has little influence o n the r e d i s t r i b u t i o n dynamics at low loadings. In contrast, the q u a n tity of clay p r e s e n t at low loadings of M B has a significant role to play in providing a large n u m b e r of p r o t o n sites. T h e t r i m e r is redistrib u t e d by t r a n s f e r f r o m o n e particle or floc to b H+--MBITFT I C H+-M B/A C Y F 0 [] [] E 590 .<E 580 560 F , , 100 200 I 0 300 0 I 100 200 Time/min 300 0 I I 100 200 300 FIG. 11. Variation of ~nlax for the aggregated form of methylene blue as a function of time for methylene blue alone (a), methylene blue in binary solution with thioflavin T (b), and acridine yellow (c) on H+-montmorillonite. O = 1% or (l + l)%, 9 = 2% or (2 + 2)%, [] = 5% or (5 + 5)%. Competitive adsorption of dyes on clays a n o t h e r particle o r floc. T h e p r e s e n c e of t r i m e r , dimer, m o n o m e r a n d M B H 2+, in varying amounts, suggests the following t e n t a t i v e mechanism: (MB+)3 + H + ___>(MB+)2 + M B H 2+ (MB+)2 + H + ~ M B + + M B H 2+ M B + + H + ~ M B H 2+ T h e M B aggregate o b s e r v e d at i n t e r m e d i a t e loadings of a b i n a r y mixture of M B a n d T F T o n H + - m o n t m o r i l l o n i t e has c o n s i d e r a b l e trimeric c h a r a c t e r , w h e r e a s in the p r e s e n c e of A C Y a n d P F H this aggregate is a mixture of b o t h d i m e r a n d t r i m e r resulting in a b r o a d a b s o r p t i o n b a n d c e n t r e d n e a r 600 n m . REFERENCES AVNIR D., GRAUERZ., HUPPERTD. & ROJANSK!D. (1986) Electronic energy transfer on clay surfaces. Rhodamine 6G to cationic acceptors. New J. Chem. 10, 153-157. BANIN A. & SHAKEDD. (1969) Particle size and surface properties of acidic montmorillonite. Proc. Int. Clay Conf. Tokyo, 1, 669~582. BERGMAN K. & O'KONSKI C.T. (1963) A spectroscopic study of methylene blue monomer, dimer and complexes with montmorillonite. J. Phys. Chem. 67, 2169-2177. BREEN C. (1991) Thermogravimetric study of the desorption of cyclohexylamine and pyridine from acid-treated Wyoming bentonite. Clay Miner. 26, 473-486. CENENS J. & SCHOONHEYDT R.A. (1988) Visible spectroscopy of methylene blue on hectorite, Laponite B and Barasym in aqueous suspension. Clays Clay Miner. 36, 214-224. CENENS J., VLIERS D.P., SC~OONnEYDT R.A. & DE SCHRYVERF.C. (1987) Spectroscopic study of the surface chemistry of proflavine on clay minerals. Proc. Int. Clay Conf. Denver, 352-358. COHEN R. & YARIV S. (1984) Metachromasy in clay minerals. Sorption of acridine orange by montmorillonite. J. Chem. Soc. Faraday Trans. L 80, 1705-1715. GRAUER Z., GRAUER G.L., AVNIR D. & YARIV S. (1987) Metachromasy in clay minerals. Sorption of pyronin Y by 189 montmofillonite and Laponite. J. Chem. Soc. Faraday Trans. I. 83, 1685-1701. HANG P.T. & BRINDLEY G.W. (1970) Methylene blue adsorption by clay minerals. Determination of surface areas and CEC. Clays Clay Miner. 18, 203-212. MARGULIESL., ROZENH. & COHENH. (1988) Photostabilisation of nitromethylene heterocycle insecticide on the surface of montmorillonite. Clays Clay Miner. 36, 159-164. MARGULIESL., ROZEN H. & NIR S. (1988) Model for the competitive adsorption of organic cations on clay. Clays' Clay Miner. 36, 270-276. Rvrwo G., SERBANC., NIR S. & MARGVLIESL. (1991) Use of methylene blue and crystal violet for determination of exchangeable cations in montmorillonite. Clays Clay Miner. 39, 551-555. SCHOONHEYDTR.A. & HEUGHEBAERT(1992) Clay-adsorbed dyes: methylene blue on Laponite. Clay Miner. 27, 91-100. SCHOONHEYDTR.A., CENENSJ. & DE SCHRYVERF.C. (1986) Spectroscopy of proflavine adsorbed on clays. J. Chem. Soc. Faraday Trans. L 82, 281-289. TAYLORR.K. (1985) Cation exchange in clays and mudrocks by methylene blue. J. Chem. Tech. Biotechnol. 35A, 195-207. VIAENEK., CAIGUIJ., SCHOONHEYDTR.A. & DE SCHRYVER F.C. (1987) Study of the adsorption on clay particles by means of a fluorescent probe. Langmuir 3, 107-111. V1AENEK., CRUTZENM., KUNIYMAB., SCHOONHEYDTR.A. & DE SCHRYVERF.C. (1988) Study of the adsorption of organic molecules on clay colloids by means of a fluorescent probe. Prog. Colloid Polymer Sci. 266, 242-246. XIANG Y., VILLEMUREG. & DETELLIER C. (1992) Observation by scanning electron microscopy of globular particles of calcium-montmorillonite and of montmorillonite exchanged with methylviologen or tris(hipyridyl) ruthenium(u). Clays Clay Miner. 40, 362-364. YAMAG1SHIA. & SOMAM. (1981) Aliphatic tail effects on adsorption of acridine orange cation on a colloidal surface of montmorillonite. J. Phys. Chem. 85, 3090-3092. YARIVS. & LURIED. (1971) Metachromasy in clay minerals. Part I. Sorption of methylene-blue by montmorillonite. Israel J. Chem. 9, 537-552. YARIVS., NASSERA. & BAR-ONP. (1990) Metachromasy in clay minerals. J. Chem. Soc. Faraday Trans. L 86, 1593-1598.
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