Colloids and Surfaces A: Physicochem. Eng. Aspects 259 (2005) 173–177 Preparation and dispersive behaviors of reduced charge smectite Chia-Chi Su, Yun-Hwei Shen ∗ Department of Resources Engineering, National Cheng Kung University, Tainan, Taiwan, ROC Received 21 July 2004; accepted 14 February 2005 Available online 17 March 2005 Abstract A series of reduced charge smectites (RCS) with gradually decreasing cation exchange capacity (CEC) were prepared by controlling the amount of Li used to saturate SAz-1 to study the dispersive characteristics of RCS in water and provide insight into the influence of the layer charge density on delamination of smectite in water. Results indicated that being well deliminated in water, high-CEC smectie suspension resulted in small flocs with fluffy structure after coagulation presumably due to a more porous type of coagulation with intense face-to-edge and edge-to-edge interactions of platelets. High-CEC smectie also resulted in suspension with higher viscosity due to the presence of larger number of particles and secondary electroviscous effect. Finally, this study demonstrated the possibility of tailor-made smectite suspensions with suitable dispersive properties for particular applications. © 2005 Elsevier B.V. All rights reserved. Keywords: Reduced charge smectites; Layer charge; Delamination; Rheology 1. Introduction Smectite, a 2:1 clay mineral, is characterized mainly by an Al-octahedral sheet placed between two Si-tetrahedral sheets. The isomorphous substitution of Al3+ for Si4+ in the tetrahedral layer and Mg2+ for Al3+ in the octahedral layer results in a net negative layer charge on smectite. This charge imbalance is offset by exchangeable cations (typically Na+ and Ca2+ ) at the smectite surface. Na+ and Ca2+ are strongly hydrated in the presence of water and facilitate smectite expansion after wetting. The layer charge and its distribution are among the most important characteristics of smectite leads to a complex colloidal system which lends itself to a variety of applications such as organoclay [1,2], polymer-clay nanocomposites [3], coagulation aid [4] and drilling fluid [5]. The layer charge of smectites can be modified by the fixation of small exchangeable cations, such as Li in the structure [6]. Li cations migrate from the exchange sites in the gallery into the layers upon heating and consequently the residual negative layer charge is reduced [7–9]. Both temperature and duration of heating affect Li-fixation in reduced charge smectite (RCS) [10]. ∗ Corresponding author. E-mail address: [email protected] (Y.-H. Shen). 0927-7757/$ – see front matter © 2005 Elsevier B.V. All rights reserved. doi:10.1016/j.colsurfa.2005.02.010 The preparation of a series of reduced charge smectites provides an opportunity to tailor-made smectite suspensions with suitable dispersive properties for particular applications. Some authors [11,12] claim that as the layer charge of smectite increases, the cohesion energy that holds the lamellae closer also increases so that the dispersion of smectite in water become more difficult, resulting in larger particles. However, other researchers [13–15] found an increased number of non-swelling interlayers in RCS that caused a decreased specific surface area and increased particle size of smectite in water. In this work we address the dispersive characteristics of a series of prepared RCSs in water and provide insight into the influence of the layer charge density on delamination of smectite in water. 2. Materials and methods 2.1. Preparation of reduced charge smectites (RCS) A reference Ca-saturated smectite (SAz-1) obtained from the Clay Source Repository were used as received. The cation exchange capacity (CEC) was 110 mequiv./100 g clay. Three Li-saturated SAz-1 samples were prepared by ion exchange 174 C.-C. Su, Y.-H. Shen / Colloids and Surfaces A: Physicochem. Eng. Aspects 259 (2005) 173–177 of 15.0 g-SAz-1 with 250 ml-LiCl solutions containing Li ions equivalent to 135, 240 and 1170% of SAz-1’s CEC (0.9, 1.6 and 7.8 M of Li ions) respectively for 2 h at room temperature followed by centrifugation and washing with distilled water several times, and freeze-dried. RCS samples were prepared by heating Li-saturated SAz-1 s for 24–72 h at temperatures of 100, 130, 160, 200 and 300 ◦ C, respectively. The CEC of the prepared RCS was determined by the ammonium acetate method at pH = 7 [16]. 2.2. Hydrodynamic particle size distribution of RCS The hydrodynamic particle size distribution of RCS was determined by the Andreasen pipette method [17]. In this method the concentration of solid changes occurring within a settling suspension of RCS are followed by drawing off definite volumes by means of a pipette and from these the hydrodynamic size distribution may be found. Suspensions (0.3% by weight) of RCS in distilled water were prepared after ultrasonic disaggregation treatment for 60 min. 2.3. Visible spectra of MB-RCS suspension Suspensions (0.05 wt.%) of RCS in distilled water were prepared after ultrasonic disaggregation treatment for 60 min. Water and methylene blue (MB) solution (10−3 mol/l) were added with stirring to obtain MB-RCS suspensions with final MB concentrations of 5 × 10−5 mol/l. Spectra of MB-RCS dispersions were measured using a UV-VIS spectrophotometer (Jasco V-530) 2 min, 60 min and 24 h after mixing of the MB solution with the smectite suspension. 2.4. Coagulation of RCS suspension For the RCS coagulation test, a weighted sample of smectite was stirred in 500 ml of distilled water within a 600 ml beaker, fitted with four 0.25 in. wide baffle plates and 1 in diameter propeller, for 10 min. The suspension was then adjusted to pH 6.5 and further conditioned for 2 min. After conditioning, different amounts of a cationic polyelectrolyte, polydiallydimethylammonium chloride (PDADMAC), were then added to the suspension, while the propeller was rotated at 300 rpm. After 3 min of rapid mixing, the sample was stirred for a further 7 min at 30 rpm, then left to settle for 45 min. The residual turbidity in the suspension was measured by a turbidimeter (HANNA HI93703). The volume of settled flocs (sludge volume) was measured in 100 ml graduated cylinders. distilled water were prepared after ultrasonic disaggregation treatment for 60 min. 3. Results and discussion Effects of the amount of saturating Li+ used, heating temperature and heating time on the preparation of RCS were explored. Three Li-saturated SAz-1 samples were obtained by ion exchange of SAz-1 with LiCl solutions containing Li ions equivalent to 135, 240 and 1170% of SAz-1’s CEC, i.e. RCS135, RCS240 and RCS1170, respectively. Fig. 1 shows the effect of heating temperature on the CEC of Li-exchanged samples saturated with different amount of Li+ . Increasing the treatment temperature caused a more extensive reduction of CEC values in RCS240 and RCS1170 series with a sharp decrease occurring after heating at 160 ◦ C. The temperature of 160 ◦ C seems to be a threshold value of treatment temperature to produce significant CEC reduction for the preparation of RCS in this study. Previous studies [18,19] indicated that the CEC-reduction of SAz-1 exchanged with 1 M LiCl and heated for 24 h at 150–200 ◦ C ranged from 87 to 79%. The CEC of RCS135 shown only a moderate decrease with increasing treatment temperature presumably due to the inadequate amount of Li+ on the exchange sites in the gallery available to diffuse into the layers upon heating. Upon heating at 200 ◦ C for 24 h the CEC of RCS135, RCS240 and RCS1170 were reduced to 83, 53, and 22 mequiv./100 g, respectively. Alternatively, RCS with different layer charge can be prepared at the same heating temperature from Lisaturated SAz-1 sample by varying the treatment time. Heating at 160 ◦ C from 24 to 72 h, the CEC of RCS135 decreased gradually from 83 to 67 mequiv./100 g. Longer heating time apparently allowed more Li+ ions in the gallery diffuse into the layers. A suitable series of RCS samples were prepared for the following experiments. The hydrodynamic particle size distributions of RCS with different CEC in water were determined by the Andreasen 2.5. Rheological measurements The rheological behavior of the dispersions was measured in a Brookfield HBDV-III rheometer with cone-plate adapter at 25 ◦ C. The measurement required 0.8 ml of each dispersion. Suspensions of RCS with different solid content in Fig. 1. Effect of heating temperature on the CEC of various Li-exchanged samples. C.-C. Su, Y.-H. Shen / Colloids and Surfaces A: Physicochem. Eng. Aspects 259 (2005) 173–177 175 Fig. 2. The hydrodynamic particle size distribution of various RCSs. pipette method. The suspensions of RCS with different CEC form particles with different size in suspension due to their layer charge. Several authors [11,12] proposed that as the layer charge increases, the cohesion energy that holds the lamellae closer also increases so that the dispersion of smectite in water becomes more difficult, resulting in larger particles and smaller interlamellar spacing. However, results form Fig. 2 indicated an opposite trend that particle size of smectite in water decrease with increasing layer charge or CEC. Apparently, smectite with lower CEC forms tactoids, groups of aligned layers, in water presumably due to weaker electrostatic repulsive force between layers. Smectite with higher CEC was better deliminated in water and resulted in tactoids with smaller number of layers and smaller particle size. Komadel et al. [14] reported that the decrease of layer charge of smectite by Li-fixation causes the collapse of expandable interlayers and the subsequent development of pyrophyllitelike (unexpandable) layers. The presence of non-swelling layers is also accountable for the increasing particle size of RCS with lower CEC. Fig. 3 shows the time evolution spectra of the suspensions containing MB and RCS with different CEC. The distances between the adsorbed dye cations (MB) were controlled by the layer charge [20–24]. Short distances between the MB, adsorbed on the untreated smectite with the highest layer charge, enable a high extent MB agglomeration (570–590 nm) [20–24]. The spectra of RCS with a CEC of 121 mequiv./100 g show an absorbance peak only at 570 nm (Fig. 4a) indicating the dominance of MB agglomerates. On the other hand, spectra of RCS with a CEC of 83 and 53 mequiv./100 g (Fig. 4b and c) demonstrated the dominance of monomeric MB (650–675 nm) and the appearance of protonated or J-aggregates MB (770 nm) [20–24]. Lower charge smectite apparently decreased the amount of MB agglomerates in favor of monomeric (650–675 nm) and protonated or J-aggregates MB (770 nm). In this case, larger distances between the neighboring negatively charged sites suppressed the formation of MB agglomerates. The spectra of RCS Fig. 3. The time evolution spectra of the suspensions containing MB and RCS with different CEC. with a CEC of 83 mequiv./100 g show a significant change with time. The increasing intensity of the band assigned to monomeric MB (650–675 nm) indicates the continuous formation of monomeric MB. It is also interesting to notice that the 770 nm band, assigned to protonated or J-aggregates MB, decreases for RCS with a CEC of 53 mequiv./100 g. The disappearance of this band with decreasing charge can be interpreted as a consequence of less water autoionization and/or suppressed formation of J-aggregates at the surface of low charge density as previously reported [22]. Apparently, the change in spectra of MB-RCS suspensions reflect very sensitively the difference in the layer charge or CEC of RCSs prepared in this study. Smectite coagulation tests were run to explore dispersive state for different RCS suspension. Fig. 4 presents a comparison of the coagulation of suspensions of RCS with different CEC using a cationic polyelectrolyte, PDADMAC. Optimum 176 C.-C. Su, Y.-H. Shen / Colloids and Surfaces A: Physicochem. Eng. Aspects 259 (2005) 173–177 Fig. 5. The shear stress–shear rate curves of various RCS dispersions. Fig. 4. Coagulation of RCS suspensions with PDADMAC: (a) residual turbidity and (b) sludge volume as a function of PDADMAC dosage. PDADMAC dosages for the coagulation of RCS with a CEC of 83 and 121 mequiv.100 g suspensions were 2 and 20 mg l−1 PDADMAC, respectively (Fig. 4a). The optimum PDADMAC dosages for the coagulation of RCS suspensions did not increase proportional to the increasing CEC of RCS. This result indicated that even a small difference in CEC may cause a profound variation in the dispersive state of RCS suspensions. In addition, Fig. 4b indicated a distinct difference among volume of settled flocs (sludge volume) for different RCS suspensions. The coagulation of smaller layer charge RCS (CEC = 53 and 83 mequiv./100 g) suspensions produced sediment consisted of large aggregates with compact structure and small sludge volume (less than 20 ml). In contrast, coagulation of high layer charge RCS (CEC = 121 mequiv./100 g) suspension resulted in large volume of settled flocs (more than 30 ml) consisted of small aggregates with fluffy structure. It is possible that smaller layer charge RCS has a tendency to form aggregates of aligned (face-to-face interaction) smectite platelets in suspension and resulted in large flocs with compact structure after coagulation. However, coagulation of better delaminated high layer charge RCS suspension resulted in small flocs with fluffy structure presumably due to a more porous type of coagulation with intense face-to-edge and edge-to-edge interactions of platelets. Apparently, the sludge volume after coagulation for different RCS suspensions reflected the dispersive state of RCS suspensions. The shear stress-shear rate curves of the concentrated RCS dispersions (23–33 wt.%) are shown in Fig. 5. Low layer charge RCS (CEC = 53 mequiv./100 g) suspensions display Newtonian flow behavior with a constant viscosity. Higher layer charge RCS (CEC = 83 and 121 mequiv./100 g) suspensions has an initial yield stress at low shear rates, and afterwards presents pseudoplastic or shear-thinning type behavior at higher shear rates. Fig. 6 shown change in viscosity determined at various shear rates as a function of CEC of RCS. Clearly, the viscosity of RCS suspension increases with increasing CEC of RCS. Dispersing in water sheets of low layer charge RCS are not well deliminated. Instead, several smectite sheets combine to form tactoids, groups of aligned sheets, in water. This produces a small number of particles in water, so that the viscosity is reduced. Another possible cause of the high viscosity for suspensions of high layer charge RCS is the secondary electroviscous effect [25]. Rand et al. Fig. 6. Change in viscosity determined at various shear rates as a function of CEC of RCS. C.-C. Su, Y.-H. Shen / Colloids and Surfaces A: Physicochem. Eng. Aspects 259 (2005) 173–177 [26] explained that the extended diffuse ionic layers around the particles restrict their movement and enhance both the shear stress and yield value. Reduced layer charge reduces the thickness of the diffuse ionic layers, increases the translational and rotational freedom of the particles and decrease viscosity. 177 number of particles and secondary electroviscous effect. Finally, this study demonstrated the possibility of tailor-made smectite suspensions with suitable dispersive properties for particular applications. References 4. Conclusion Heating Li-saturated smectites reduced the net negative layer charge due to fixation of Li within the layers in smectite. A series of reuced charge smectites with gradually decreasing CEC were prepared by controlling the amount of Li used to saturate SAz-1 in this study. 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