Sky Journal of Soil Science and Environmental Management Vol. 4(1), pp. 016 - 019, March, 2015 Available online http://www.skyjournals.org/SJSSEM ISSN 2315-8794© 2015 Sky Journals Full Length Research Paper Absorption capacity and time effect on polarity evaluation of various solvents using natural bentonite clay mineral Obi C.* and Okoye I. P. Physical Chemistry Unit, Department of Pure and Industrial Chemistry, Faculty of Chemical Sciences, University of Port Harcourt, P.M.B. 5323, Choba, Port Harcourt, Rivers State, Nigeria. Accepted 26 November, 2014 The rates of absorption of various solvents onto different weights of natural bentonite clay mineral were investigated at room temperature. A column technique was adopted in the absorption process. The physicochemical properties of the clay mineral were determined using the pH drift method, ethylene glycol monoethylether method and atomic absorption and emission spectrophotometer. The results reveal that the bentonite clay mineral took longer time to absorb polar solvents (1020 – 3660 s) while non – polar solvents were 3 -1 faster (120 – 600 s). The result reveal that water has the highest absorption capacity of 2.1 cm g . The degree of polarity was observed in the order: water > ethanol > acetone > methyl chloride > petroleum spirit. The absorption experiment proved that bentonite is a hydrophilic clay mineral. This research is a preliminary approach to highlight the steps in the removal of hazardous wastes from landfills. Key words: Bentonite, absorption, polarity, solvents, characterization. INTRODUCTION Clay is a naturally occurring aluminium silicate composed primarily of fine - grained minerals (Grim, 1953). Bentonite is a rock formed of highly colloidal and plastic clays composed mainly of montmorillonite (smectite group) (Lagaly, 1995). The industrial application of bentonite clay depends on the composition of their clay and non-clay minerals. The clay minerals in bentonite are smectite such as montmorillonite, beidellite, saponite, hectorite, etc (Grim, 1968). On the other hand, the nonclay minerals include silica (for example, quartz and opals), feldspars, zeolites, carbonates, sulphites, sulphides, sulphates, oxides and hydroxides (More and Reynolds, 1997). Two types of bentonite clays exist according to swelling and non-swelling properties. Sodium bentonite is of swelling type while calcium bentonite is non-swelling. Sodium and calcium bentonite are distinctly characterized by high ratio of their dominant *Corresponding author. E-Mail: [email protected]. Tel: +234-8036682351. exchangeable base. Intermediate type bentonite may have either sodium or calcium base dominant but in low or nearly equal ratios mixed (Togan, 2006). The special properties of bentonite clay minerals include ability to form thixotrophic gels with water, ability to absorb large quantities of water and a high cation exchange capacity. These properties of bentonite clay minerals are derived from the crystal structure of the smectite group, which is an octahedral alumina sheet between two tetrahedral silica sheets (2:1) (Yang and Ding, 2007; Bahranowski, 1998; Brown and Anderson, 1983). Variations in interstitial water and exchangeable cations in the interlayer of clay affect the properties of bentonite and thus the commercial applications of the different types of bentonite clay minerals (Sergio et al., 2006). The exchangeable cations are positively charged species that are reversibly adsorbed to negatively charged clay surfaces (Brown and Anderson, 1983). The resultant equilibrium concentrations of the cations and their compositions will enhance the polarities of the different Obi and Okoye leachates (solvents) in clay. The adsorption kinetics of clay minerals has intrigued soil scientists for over a century. Most investigators have been interested in the total exchange capacity and equilibrium exchange relationships, but few have studied the rate of cation exchange on clay minerals (Inglezakis et al., 2003; Obi and Okoye, 2014). In addition, literature has shown little information concerning the impact of clay in polarity studies. Hence, the aim of this study is to evaluate the rate of absorption of various solvents on natural bentonite clay mineral and possibly determine their degree of polarity. MATERIALS AND METHODS 17 for each of the bentonite weights. Water (5 ml) was added onto the bentonite via a pipette and immediately, the time for the last drop of water was measured using a stop watch. The same process was repeated for each of the solvents at different bentonite weights. The 3 absorption capacities (cm /g) of the solvents were determined using the equation 2: (2) Where qe is the absorption capacity of the solvents in 3 3 cm /g, Vi is the initial volume in cm , Ve the equilibrium 3 3 volume in cm , VT is the total volume in cm and M is the mass of absorbent in grams. Collection and preparation of absorbent Natural bentonite clay mineral used in this study was obtained from Ezinachi clay deposit in Okigwe, Imo State, Nigeria. The sample was washed with water, dried and sieved to remove other impurities and particles. It was then ground to powder in a mortar and allowed to pass through 250 µm sieve to form a homogeneous powder. Characterization of the absorbent Characterization of absorbents The physical and metal oxide compositions of sample clay mineral as determined are presented in Tables 1 and 2. Absorption Studies The point of zero charge (PZC) of the bentonite clay mineral was determined using the pH drift method (Eggleston and Jordan, 1998). The specific surface area (SSA) of the clay mineral was determined using the ethylene glycol monoethylether (EGME) method (Amy and Alan, 2002) and the equation below was used for the calculation: SSA = RESULTS AND DISCUSSIONS (1) Where W F is final weight of clay – solvent slurry in g, W S is the initial weight of the clay sample in g, 0.000286 is a constant known as the weight of EGME required to form a monomolecular layer on a square meter surface in 2 g/m . The chemical composition of the clay mineral was determined by atomic absorption and emission spectrophotometer (Okoye and Obi, 2011). Absorption Studies The rates of absorption of the solvents were carried out isothermally using burette clapped on a retort stand, calibrated beaker and pipette. Cotton wool was placed at the bottom of the burette. Different weights of the natural bentonite (1.0 g, 1.5 g, 2.0 g, 2.5 g and 3.0 g) were put into the burette. Each 5 ml of water, ethanol, acetone, methyl chloride and petroleum spirit were measured out The rates of absorption of the various solvents are presented in Figure 1. The result revealed that the natural bentonite clay took longer time to absorb water. This could be due to the presence of only O – H bonds which makes it extremely polar. Ethanol absorption was close to water indicating that it is also polar. Equally acetone was also polar. The result further revealed that the rate of absorption of methyl chloride and petroleum spirit was faster. This could be due to the absence of O – H bond, thereby making it extremely non-polar. The kinetic dynamics of these solvents could be as a result of their varying densities and dielectric constants. Therefore, the degree of polarity is given as: water > ethanol > acetone > methyl chloride > petroleum spirit. The result revealed that water has the highest absorption capacity of 2.1 3 -1 cm g .The result obtained was similar to the work done by Brown and Anderson, (1983) on the effects of organic solvents on the permeability of clay soils. Conclusion The study of effect of time on the polarity properties of water, ethanol, acetone, methyl chloride and petroleum spirit using natural bentonite clay mineral have shown that the clay mineral is hydrophilic in nature. This property makes it suitable in the paint and pharmaceutical industries. The bentonite clay could equally be used in the screeding of walls. In addition, the 18 Sky. J. Soil. Sci. Environ. Manage. Table 1. Physical properties of the sample clay mineral. 2 pH 6.2 SSA(m /g) 30.00 Specific gravity 1.96 Point of zero charge 4.5 Moisture (%) 1.82 Table 2. Metal oxide composition and loss in ignition of the sample clay mineral. Metal oxide % Mass SiO2 50.45 Al2O3 30.34 Fe2O3 2.78 CaO 0.10 MgO 0.23 Na2O 0.07 K2O 0.87 TiO2 0.01 MnO 0.08 Ignition loss 11.54 Figure 1. Effect of time on the absorption of the solvents at 298 K. Where A represents petroleum spirit, B methyl chloride, C is acetone, D is ethanol and E is water. rate at which it absorbs non-polar solvents is faster than polar solvents. ACKNOWLEDGEMENTS Authors would like to thank Mr. Peter NT of the Department of Pure and Industrial Chemistry, University of Port Harcourt, Rivers State for his laboratory assistance. Competing interests Authors declare that there is no competing interest. REFERENCES Amy BC, Alan JL (2002). Determination of surface area of fine – grained soils by the ethylene glycol monoethylether (EGME) method. Geotech. Testing J. 25: 3 – 9. Bahranowski R (1998). Structure and texture of copper doped alumina – pillared montmorillonites. Mineralogia Poloni – Ca., 29(1): 55 – 65. Brown KW, Anderson DC (1983). Effects of organic solvents on the permeability of clay soils. United States Environmental Protection Agency, Research and Deveolpment, EPA – 600/S2 – 83 – 016, 1 – 2. Eggleston CM, Jordan G (1998). A new approach to pH of zero charge measurement. Geochimica et Cosmochimica Acta, 62: 1919 – 1923. Grim RE (1953). Clay mineralogy, 2nd ed., New York, McGraw – Hill. 596. Grim RE (1968). Clay mineralogy, McGraw – Hill, New York. Lagaly G (1995). Surface and interlayer reactions: Bentonites as Obi and Okoye adsorbents. Clays controlling the environment. Prooceedings of the 10th International Clay Conference, Adelaide, Australia, CSIRO Publishing, Melbourne. 137 – 144. Inglezakis VJ, Loizidon MD, Grigoropoulou HP (2003). Ion exchange of Pb2+, Cu2+, Fe2+ and Cr3+ on natural clinoptilolite: Selectivity determination and influence of acidity on metal uptake. J. Colloid Interface Sci., 261: 49 – 54. More DM, Reynolds Jr RC (1997). X – Ray diffraction and identification and analysis of clay minerals, 2nd Ed., Oxford University Press, New York. Obi C, Okoye IP (2014). Kinetic Evaluation of Naphthalene Removal Using Acid – Modified and Unmodified Bentonite Clay Mineral. J. Appl. Sci. Environ. Manag., 18(1): 153 - 159. 19 Okoye IP, Obi C (2011). Synthesis and characterization of Al – Pillared Bentonite Clay Minerals. Res. J. Appl. Sci., 6(7 – 12): 447 – 450. Sergio M, Musso M, Medina J, Diano W (2006). Alumina – pillared of a montmorillonite clay: Textural properties as a function of the starting mineral particle size. Azo J. Mat. 2: 1. Togan U (2006). Behavior of bentonite suspensions in non – aqueous media. An M.Sc Thesis, Middle East University. 7 – 9. Yang CN, Ding AL (2007). Removal of Ni2+ from containing wastewater by bentonite of Handan. J. Hebei U. Eng., 244: 63 – 64.
© Copyright 2025 Paperzz