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ISRN Electrochemistry
Volume 2013 (2013), Article ID 959128, 7 pages
http://dx.doi.org/10.1155/2013/959128
Research Article

Cyclic Voltammetric Investigations of Thiazine Dyes on Modified Electrodes

Department of Chemistry, University of North Bengal, Raja Rammohanpur, Darjeeling 734 013, India

Received 18 December 2012; Accepted 6 January 2013

Academic Editors: R. Kizek, G.-R. Li, and A. A. Moya

Copyright © 2013 Amitabha Chakraborty et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract

Electrochemical behavior of five progressively alkylated thiazine dyes has been investigated at glassy carbon/montmorillonite and glassy carbon/zeolite electrodes. Quantitative characteristics, associated with the positions of peak potentials ( and ) and current ratios (), are measured with scan rates. The peak current observed in the modified electrodes is dependent on both the porosity and nature and number of sites involved in partitioning the complex into film. The values of diffusion coefficient for different dyes have been calculated from electrochemical data. It is suggested that in clay-modified electrode along with physical diffusion the process of electron hopping seems to be most likely.

1. Introduction

Cyclic voltammetry (CV) is an important electroanalytical method used to analyze the electronically activated molecules and its corresponding chemical reactions. In other words, the CV response may provide necessary information to the kinetics along with the identification of side and final products of different electrochemical reactions [1]. Nanocrystalline thin films of various metal oxides, namely, SnO2, ZnO, and TiO2 with highly porous structure have drawn the interest of different researchers during the last few decades because of their use in different photochemical cells as photosensitive semiconductor electrodes [25]. These electrodes are being used in controlled analysis of some ions and some electroactive biological species, because of their use and selectivity [6, 7]. It has been found that dye-modified electrodes exhibit better electrochemical activity in comparison to that of bare electrodes [8]. A large number of electrochemists show their attention to the clay-modified electrodes due to the unique layered structure of the clay and its ion exchange properties. Different techniques, namely, covalent attachment and polymer-film casting on electrodes are generally employed for the modification in electrochemical and polyelectrochemical studies of dye-incorporated clay-modified electrodes. In an early work Kamat [9] observed a quasi-reversible oxidation wave of thionine in a clay-modified electrode which is comparable to the reversible wave of the same species in an unmodified electrode. The conclusion was that the dye continued its electrochemical identity even in the clay film. Other researchers also observed similar electrochemical behavior to modified electrodes coated with dyes [10, 11].

For a diffusion type cyclic voltammogram of a dye in a clay-modified electrode the peak current is linearly dependent on (where is the scan rate). It is suggested that in modified electrodes the process of charge transport takes place either by physical diffusion of the electroactive molecule or by electron exchange (hopping) [9]. On the other hand, in a review on clay-modified electrodes, Fitch [12] observed that one of the attractive features of clays for their use in electrode modification is the high reactivity of the clay surface with organics. Thus, in some cases it is found difficult to localize an organic substrate in close proximity to the electrode to enhance an electrochemical process. Inoue and Yoneyama [13] capitalized on this feature in the study of electropolymerization of aniline in the clay support. Following the same rationale, Rusling et al. [14] attempted to combine the adsorption of organics with the cation exchange capacities (CEC’s) of clays to enhance the electroreduction of the aryl halogen in dibromobenzene. Recently, inorganic clays have been observed useful because of their unique structure as well as typical adsorption characteristics and chemical stability [15]. Some researchers also used CoPc-CPE, a dye-modified electrode, to determine bisphenol A (BPA), an important substance that is supposed to influence various hormonal activities in human body [16]. It has been stated that, in comparison to the bare electrode, oxidation overpotential reduces at CoPc-CPE, while oxidation potential is found to be increased. It was also reported that [17] a clay-modified electrode exposed to [D-Ru(phen)3]2+ showed no increase in currents on exposure to additional solutions of [D-Ru(phen)3]2+ but showed an increase in current on exposure to [L-Ru(phen)3]2+. The conclusion was that the primed []2+ clay accommodated the L form of the complex via stereoselective packing. However, the determination of electrochemical behavior of ferrocyanide and ferricyanide ions at clay-modified Pt electrodes were determined in presence of cationic dyes suggested that in every case the clay-film structure plays the major role in determining the rate of definite redox processes [18]. In addition to the clay minerals another inorganic potential modifier is zeolite which also attracts researchers to the different electrochemical processes in zeolite-coated electrodes [19, 20].

Keeping in mind the electrochemical importance of dyes in modified electrodes we have chosen five progressively alkylated thiazine dyes, namely, thionine (Th), azure A (AA), azure B (AB), azure C (AC), and methylene blue (MB) to investigate their electrochemical behavior at glassy carbon/montmorillonite and glassy carbon/zeolite electrode in presence of 0.1 M H2SO4.

2. Experimental

All the dyes under investigation were procured from Aldrich Chemical Co. (USA) and found to contain colored impurities. Detail method of purification of the dyes has already been described previously [21]. The fraction of montmorillonite clay minerals having size less than 2 μm was isolated by the usual method of dispersion and sedimentation [9]. The fraction thus collected was treated several times with dilute HCl and after removing the acid, warmed with 6% H2O2 in water bath to remove trace of any organic matter present. Excess H2O2 was decomposed by heating the samples in a water bath. The iron present in the clay minerals was then removed by treating the clay samples with sodium metabisulphite and dithionate in acetate buffer solution at 60°C followed by centrifugation, washing, and so forth as recommended elsewhere [22]. Finally, the clay residues were washed to dispersion and dialyzed. The clay suspension was then converted into the Na form by stirring an approximately 2% suspension of clay minerals with ion exchange resin (Dowex 50 w × 80) in its Na form for about four hours. Na clay (pH = 7) thus formed was used for the study. The zeolite, ZSM-5 (Si/Al 30, surface area = 400 m2/g), was used as received for the preparation of suspension.

Colloidal Pt was obtained by refluxing chloroplatinic acid (0.168 g/lit) in a mixture of 1 : 1 water and ethanol containing 3% polyvinyl alcohol [23]. Colloidal suspensions are prepared from Na montmorillonite and ZSM-5 using the method employed by Kamat [9]. In that respect 10 g of Na montmorillonite or ZSM-5 was dispersed in 100 mL of water. The suspensions were then centrifuged for one hour at 6000 rpm, and the supernatants were taken. The clay and zeolite contents in the supernatant colloidal suspensions were measured to be as 8.0 and 7.0 g/lit, respectively.

The casting of the clay and zeolite on the glassy carbon electrode (GCE) (diameter 3.2 mm, BAS, USA, part number MF2012) was done in the following way as suggested by Ghosh and Bard [24]. Montmorillonite or zeolite suspension is mixed with colloidal Pt in 1 : 2 ratio, and 0.1 mL of the mixed suspension was placed over the previously cleaned GCE. After drying properly the electrode was finally dipped into the concentrated (1 × 10−3 M) dye solution for 15 to 20 minutes. The modified electrodes formed in this fashion were then washed with water.

CV experiments were performed with a BAS cyclic voltammograph (USA, model CV-27) equipped with three-electrode system connecting with a Houston - recorder (Model-100). The three electrodes used in the experiments were a working glassy carbon electrode, a Pt-auxiliary electrode, and a saturated calomel reference electrode. All the experiments were carried out with 25 mL dye solution at different scan rates. 0.1 M H2SO4 or 0.1 M KCl solution has been used as supporting electrolyte with a fixed temperature of ()°C.

3. Results and Discussion

The electrochemical behavior of five thiazine dyes (Figure 1) on a bare GCE has already been reported elsewhere [25]. But in clay-modified electrodes thiazine dye cation seem to be adsorbed strongly by clay minerals. It was suggested that the planer structure of these dye molecules exhibit a particularly strong interaction to the expanded clays lattice [26]. Thus it may be expected that the electrochemical reactions are well manifested in electron/ion transfer reactions where the strong acid H2SO4 has been used directly for intercalating the clay.

959128.fig.001
Figure 1: Structures of thiazine dyes: (a) Thionine, (b) Methylene Blue, (c) Azure A, (d) Azure B, and (e) Azure C.

There are different proposed mechanisms by which clay adsorbed each dye [27, 28]. In our present work the thiazine groups of dyes which are cationic or basic in nature perform electron donor-acceptor interactions between clay and dye moiety [29]. Normally the current plotted against potential will have a peak shape if linear diffusion to the electrode surface occurs and the peak current can be described by Randles-Seveik equation [25, 30]: where represents the peak current in amperes. The other parameters are electrode area, , diffusion coefficient, , and concentration of the electroactive species, . In the above equation and , respectively, designates the scan rate and number of electrons involved in the redox process. But when the electrochemical experiment is carried out at a modifying layer, the same relationships hold, except the area of the conductive channel, which now play a very important role in defining the observed diffusion behavior [31, 32]. It should be mentioned that for the present purpose we use and to represent cathodic and anodic peak current respectively. The representative cyclic voltammograms of GCE/clay-dye systems is shown in Figure 2.

959128.fig.002
Figure 2: Cyclic Voltammograms of Thionine at montmorillonite modified electrode with scan rates (a) [112] 5, 10, 20, 40, 60, 100, 150, 200, 250, 300, 400 and 500 mV·s−1 and (b) representative cycling with scan rate 100 mV·s−1 in presence of 0.1 M H2SO4.

A close look to the CV responses suggest that for dye molecules electrochemical identity remains unaltered in both the clay and zeolite films. Since high concentration of acid is always present during intercalation, it is assumed that with dye cations the acid molecules are also trapped by the clay surfaces [29]. Current observed in the modified electrodes depends on the porosity of the clay films along with the nature and number of sites responsible for partitioning the complex into the film. On the other hand, the porosity may be affected by the initial preparation of the film as well as its bathing solution. Ghosh and Bard [24] obtained swollen (porous) films by drying clay in the presence of polyvinyl alcohol (PVA) where the presence of PVA was thought to force clay into a swollen configuration suitable for charge transport through the film. In the study of GCE/montmorillonite-dye and GCE/zeolite-dye electrodes PVA and colloidal Pt in the films may play an important role to attain better electrochemical activity. But the electrode processes in absence of any colloidal Pt in the films did not give well-defined anodic or cathodic peaks, which restricts further analysis of the results. However, the montmorillonite-modified and zeolite-(ZSM-5-) modified electrodes, when made conducting in presence of colloidal Pt, exhibit quasi-reversible redox wave of the dyes (the shapes of the cyclic voltamograms at the zeolite-modified electrodes is more close to reversible waves), which are comparable to the reversible waves in water at slow scan rates. Quantitative electrochemical characteristics are given in Tables 1 and 2 for montmorillonite-modified and zeolite-modified GCE respectively.

tab1
Table 1: Electrochemical data for cyclic voltammetry of dyes (5 × 10−5 M) at modified (montmorillonite) GCE in the presence of  0.1 M H2SO4.
tab2
Table 2: Electrochemical data for cyclic voltammetry of dyes (5 × 10−5 M) at modified (ZSM-5) GCE in the presence of  0.1 M H2SO4.

From the CV response curves one may characterize the reversibility or irreversibility of a redox reaction [1]. An electrochemical reaction is considered reversible when it simultaneously satisfies the two criteria, namely, (i) ’s satisfy the equation , where is the Faraday constant and other parameters bear their usual meaning, and (ii) the ratio of which should be equal to unity. For scan rates above 100 mV·s−1, is a linear function of (Figure 4). But at slower scan rates the plots of versus deviate significantly. Moreover, except thionine, the current output for all other dyes is substantially less in clay-modified electrodes than that in zeolite-modified electrode. This suggests that the observed cyclic voltammograms at the modified electrodes are of diffusion type only at high scan rates. The diffusion type CV responses for the present experiment suggest that the charge transport with in the clay film of the modified electrode may be either by electron diffusion or by electron-hopping process.

At high pH, the nature of the voltammograms changed appreciably (a representative voltammogram of azure B in aqueous medium is shown in Figure 3). Both oxidation and reduction peaks appear at still higher negative potential values. For example, the anodic and cathodic peaks are at −0.06 and −0.16, −0.03, and −0.33 and 0.03 and 0.08 volt for thionine, azure B, and methylene blue, respectively, at pH 6.0 (in 0.1 M KCl), whereas such peaks appear at −0.28 and −0.57 (pH 10.5), −0.21 and −0.52 (at pH 9.9) and −0.2 and −0.38 (pH 9.3), respectively, for these dyes at high pH values.

959128.fig.003
Figure 3: Cyclic voltammograms of aqueous azure B solution (1.0 × 10−4 M) at pH 9.9 with scan rates [18] 40, 60, 80, 100, 150, 200, 250, 300 mV·s−1.
959128.fig.004
Figure 4: Plot of cathodic peak currents as a function of (scan rates)1/2 for Thionine at modified GCE.

Other researchers had also observed the pH dependence on oxidation of promethazine [33]. But similar process for chloropromethazine was completely independent within the same pH region. It was suggested that for every dye molecules in its oxidized form reduces the values of amino groups which eventually causes deprotonation of the same. Similarly in case of thiazine moiety one can be argued that deprotonation takes place at higher pH. On the other hand at lower pH the amino groups along with the ring nitrogen atom are supposed to be protonated. Dependence of electrochemical behavior on pH of azure A and azure C is similar. At high pH the enhanced irreversibility in the redox processes coexists with different adsorption characteristics. The anodic prepeaks of thionine are absent at low pH whereas they are well defined at high pH indicating strong adsorption of the oxidation product. The voltammograms of azure B (shown in Figure 3) are, however, rather deformed with the overlapping of adsorption and cathodic peaks. An ill-defined anodic prepeak is also observed. At high pH on the other hand, methylene blue gives pre- and postpeaks for both oxidation and reduction processes indicating that both dye and leucodye are strongly adsorbed at high pH values.

Apparent observed diffusion coefficient, (from current measurements in voltammograms), of thionine in clay-modified electrode film is of the order of 1014 cm2·s−1. The concentration of the dye within the film has been found as 0.17 mol·lit−1. This concentration was measured from the optimum dye intake capacity of montmorillonite as shown elsewhere [26] and measuring the amount of clay in the film (by gravimetric estimation). A rough estimate of thickness of the film was made (by density measurement and gravimetry) and found to be nearly 16 micron. The errors introduced by film swelling because of hydration have not been corrected in this occasion. In fact, both physical diffusion and the process of electron hopping contribute to for each dye in modified electrodes. Thus one may relate with the actual physical diffusion coefficient () involving a concentration term by the following relation: where corresponds to the electron transfer rate constant and refers the distance between electroactive centers. Compared to bare glassy carbon electrode [25], where diffusion coefficients for the dyes are of the order of 106 cm2·s−1, the higher value of in clay supports the fact that as well as physical process the diffusion occurs via electron hopping. Figure 2 shows a continuous potential cycling as a function of peak height at 100 mV·s−1. However, as the number of cycles increases, peak current differences between successive cycles become less and less prominent. So, the differences in peak currents between the first and the second cycles are seem to be most prominent. Probably a high concentration of dye layer is formed at the vicinity of the modified electrode surfaces through ion exchange of comparatively loosely bound dye molecules by the background electrolyte. This layer is diffused away rapidly within the first cycle time and becomes less and less significant in subsequent cycles. However, this phenomenon is less significant in zeolite-modified electrode as shown by the representative plots of versus in Figure 4. The values of , which are prominent in electrode processes of azure C, azure A, and azure B on montmorillonite modified-electrode, may stem from a coupled chemical reaction involving Fe(III) ions in the lattice position of clay sample. These Fe(III) ions are shown to be active in various redox reactions on clay surface [34] and may compete with electrode reaction in oxidizing leucodyes to the corresponding thiazine dyes resulting in decrease in the anodic peak current.

4. Conclusion

The observed cyclic voltammograms of thiazine dyes at the modified electrodes are of diffusion type only at high scan rates which in turn suggests that the charge transport may take place either by physical diffusion or by electron hopping within the clay film. Compared to bare GCE higher value of in clay supports the fact that along with physical process the diffusion occurs mainly via electron hopping.

Acknowledgments

The authors are grateful to Dr. T. D. Smith, Department of Chemistry, Monas University, Australia, for kindly providing zeolite (ZSM-5) as gift sample. Financial support received from the University Grants Commission, New Delhi, through the Special Assistance Program to the Department of Chemistry, University of North Bengal, is also gratefully acknowledged.

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