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ISRN Analytical Chemistry

Volume 2014 (2014), Article ID 926213, 10 pages

http://dx.doi.org/10.1155/2014/926213
Research Article

Determination of Phenol and Chlorophenols at Single-Wall Carbon Nanotubes/Poly(3,4-ethylenedioxythiophene) Modified Glassy Carbon Electrode Using Flow Injection Amperometry

1Department of Chemistry, Addis Ababa University, P.O. Box 1176, Addis Ababa, Ethiopia

2Department of Chemistry and Chemical Technology, National University of Lesotho, P.O. Box 180, Mailroom 127, Roma, Lesotho

Received 28 February 2014; Accepted 19 March 2014; Published 16 April 2014

Academic Editors: P. Campíns-Falcó, F. Kandemirli, and J. J. Santana-Rodríguez

Copyright © 2014 Negussie Negash 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

Phenol and chlorophenols were investigated using single-wall carbon nanotubes (SWCNT) and poly(3,4-ethylenedioxythiophene) (PEDOT) composite modified glassy carbon electrode (SWCNT/PEDOT/GCE) as a detector in flow injection system. Optimization of experimental variables such as the detection potential, flow rate, and pH of the carrier solution (0.1 M sodium acetate) for the determination of phenol (P), 4-chlorophenol (CP), 2,4-dichlorophenol (DCP), 2,4,6-trichlorophenol (TCP), and pentachlorophenol (PCP) were performed. Under these conditions, analytical parameters were calculated from the calibration curve of measured amperometric responses as a function of concentrations of phenol and chlorophenols. The designed electrode exhibited very good analytical performance. The designed electrode was tested with 20 repetitive injections of each analyte and showed good operational stability. The analytical performance of the SWCNT/PEDOT/GCE electrode under flow through conditions was tested and was found to be impressive. The electrode showed a wider dynamic range for the detection of phenol and chlorophenols with low limits of detection compared with other enzymatic and nonenzymatic sensors. These results suggest that the method is quite useful for the analysis and monitoring of phenols and chlorophenols.

1. Introduction

Phenolic compounds include a large class of compounds that are common in nature and partly formed as a result of biodegradation of natural compounds. They are widely distributed in fruits and vegetables with a wide range of phenolic contents and species [1]. Phenolic compounds are also formed in a number of industrial processes and released to wastewater streams from these industries. Many phenols especially chlorophenols are used in the manufacture of chemicals that are used as preservatives for woods, textile, and leathers [2]. Phenol derivatives are known to be highly toxic to man and to aquatic organisms. They possess carcinogenic and immunosuppressive properties [3] and are highly resistant to biological degradation and persistent in the environment [2]. As a result the United States Environmental Protection Agency (EPA) and the European Union (EU) have included these phenolic compounds in their list of primary pollutants [4]. In fact the benefits related to consumption of phenolic-rich foods are associated with their antioxidant activities which are determined by their reactivity as hydrogen or electron donating agent [5, 6].

The applications of phenol and its derivatives represent potential source of pollution and affect aquatic organisms [7] including algae and aquatic spermatophytes. These toxic phenols and phenolic derivatives are released to the environment and their identification and quantification are of great importance in environmental monitoring.

Various analytical methods, such as liquid chromatography (LC), gas chromatography (GC), capillary electrophoresis, and fluorometry, have been reported for the determination of phenols and phenol derivatives [3, 5, 810]. These methods are sensitive, specific, and precise, but most of them are expensive and time consuming and require skilled technicians and some require derivatization procedures.

Electrochemical methods are the method of choice for the sensitive, rapid, and precise determination of phenol and its derivatives. Electrochemical oxidation of phenols and chlorophenols [11] and the use of electrochemical sensors as detectors in flow injection analysis [12] produced enhanced selectivity, sensitivity, and reproducibility of determinations. Amperometric methods mainly use electrochemical sensors and biosensors as detectors in FIA. Tyrosinase (Tyr) based sensors have been the most widely used amperometric biosensor for determination of phenols and were prepared in a number of matrices and conventional electrodes, including carbon paste [13], conducting polymers [14, 15], CNT conducting polymer composites [16, 17], self-assembled monolayer [18], and silica sol-gel composite [19]. Laccase based biosensors [20, 21] and horseradish peroxidase (HRP) [22] based electrochemical detectors coupled with flow injection system for the determination of phenol and phenol derivatives were also reported. In the investigated biosensors, the enzymes were either individually immobilized or composite multienzyme systems were immobilized on conventional electrodes to determine the phenolic compounds.

The use of enzyme modified electrodes significantly decreases surface fouling of electrodes. However, the high cost, the problem of immobilization process, low stability, and short operating time limit their practical application. Thus, modification of bare electrodes with nonbiological materials, such as conducting polymers, is an alternative to prevent electrode surface fouling [11, 23]. Poly(3,4-ethylenedioxythiophene), PEDOT, which is a relatively new and well-known conjugated polymer, has received relatively high attention because of its high electrical conductivity and excellent environmental stability. Thus, PEDOT has emerged as one of the most stable and promising electrode materials offering the possibility modification with different chemical groups for the determination of phenols, dopamine and ascorbic acid [24], paracetamol [25], N-acetyl-p-aminophenol and p-aminophenol [26], and niclosamide [27].

Carbon nanotubes have remarkable electrical properties, such as high specific surface area and chemical stability [2830], and can be used as electrode material to promote electron transfer between electroactive species and the electrode. Addition of CNT to conducting polymer, such as PEDOT, results in a significant increase in the mechanical properties and enhances electrical properties of the polymer by facilitating the charge transfer processes. Thus, in recent years, more and more attentions were inclined to the synthesis of conducting polymer/CNT composites that have special properties of the individual components in a synergistic manner [31, 32].

Although a number of electrode materials based on CNT-conducting polymer composite were used for the determination of phenol and its derivatives in batch system, few researchers investigated the use of CNT-conducting polymer composites as detectors in flow injection analysis. Glassy carbon electrode modified with multiwall carbon nanotubes dispersed in polyethylenimine composite was used as amperometric working electrode for flow injection determination of phenolic compounds [33].

The preparation of new composite materials that have distinct properties which were not observed in the individual components was the objective of this work. The study led to the development of SWCNT/PEDOT modified glassy carbon electrode (SWCNT/PEDOT/GCE) for the determination of phenol and chlorophenols. The modified electrode was used as an amperometric detector in flow injection system with improved qualities such as simplicity of electrode preparation, wider linear range, low detection limit, and good stability. To the best of our knowledge the modification and application of the SWCNT/PEDOT/GCE modified electrode as an amperometric phenol and chlorophenols detector had not been reported so far.

2. Experimental

2.1. Chemicals

SWCNT (mixture of metallic and semiconducting), 3,4-ethylenedioxythiophene (EDOT) monomer, and pentachlorophenol were from Adrich, 4-chlorophenol, 2,4-dichlorophenol, 2,4,6-trichlorophenol, and phenol were from Fluka (Buchs, Switzerland), acetic acid and DMF were from Merck, tetrabutylammonium perchlorate and acetonitrile were from Sigma-Aldrich, and other chemicals were from the Republic of South Africa. Helium gas (Air Products, RSA) was employed for the deaeration of the carrier solution of the flow system. All chemicals were of analytical grade and were used without further purifications. All solutions were prepared using ultrapure water of resistivity 18.2 MΩ-cm obtained from ELGA PURELAB Option-Q (UK) water purification system.

2.2. Instrumentation

Amperometric and Voltammetric measurements were performed using Epsilon Electrochemical Analyzer attached to BAS C2 cell stand (both from BASi instrumentation, USA). EDOT polymerization was carried out with BAS 100B electrochemical work station (BAS, USA). A conventional three-electrode cell was used for measurements, with a bare glassy carbon electrode (GCE) (3 mm diameter), SWCNT/PEDOT/GCE was used as the working electrode, Ag/AgCl (3 M NaCl) was used as a reference electrode, and a platinum wire was used as counter electrode. The flow system consisted of a BAS pump (Model PM-92E; USA), a sample injection valve, and a thin-layer electrochemical detector (BASi LC-4C, USA), with a flow-through cell. The electrochemical detector was connected to the Epsilon Electrochemical Analyzer. Two GCE modified with SWCNT/PEDOT (in series configuration) were used as working electrodes, while Ag/AgCl electrode (3 M NaCl) (RE-1; BASi) served as the reference electrode. The counter electrode was the bulk plate of the cell, made of stainless steel. The thickness of the layer in the cell was 0.0127 cm. The pH of the solutions was measured using HANNA HI 8314 pH-meter, while for electrode cleaning iS Integral Systems ultrasonic bath was used.

2.3. Preparation of Modified Electrode

Prior to surface modification, the bare glassy carbon electrode was polished with a 0.3 and 0.05 μm alumina slurry and washed with tap water several times and sonicated in ultrapure water bath for two minutes. Before electropolymerization, the polished electrode was pretreated using cyclic voltammetry cycling for 10 minutes between −0.9 and +1.5 V at 10 V s−1 containing 0.1 M tetrabutylammonium perchlorate in acetonitrile. Then the PEDOT was electrodeposited on the electrode in the above solution containing 10 mM EDOT by cycling the potential between −0.9 and +1.5 V. The PEDOT film was allowed to grow on the GC surface for ten successive scans as can be seen from the increasing anodic and cathodic peak current densities. The polymer film was washed with ultrapure water to remove the supporting electrolyte and unreacted monomer and dried. A PEDOT/SWCNT/GCE multilayer film is formed by casting of a 20 μL of the dispersed SWCNT in DMF (1 mg SWCNT: 1 mL DMF) over GCE and dried for an overnight and coated with the PEDOT [34]. In order to determine the optimum amount of polymer coating 5, 10, 20, 40, and 60 cycles of CV scans of PEDOT polymerization were carried out followed by casting of 20 μL of the dispersed SWCNT onto the PEDOT/GCE.

3. Results and Discussion

3.1. Electrochemical Behavior of Phenol at Bare and PEDOT Modified Glassy Carbon Electrodes

In the determination of phenol at bare glassy carbon electrodes (figure not shown) the oxidation peak decreased markedly with successive cycles due to the electrodeposition of nonconducting polymeric oxidation product of phenol as cited in the literature [23, 35]. The response disappeared totally after the third cycle owing to the adsorption of phenol oxidation products followed by electrode fouling. The bare GCE was then modified with PEDOT film. Figure 1 shows the repetitive cyclic voltammograms illustrating the continuous growth of the PEDOT on GCE surface. The thickness of the film was controlled by the number of cycles. The continuous increase of the current with the cycle number reveals the formation and expansion of a conducting phase at the electrode surface.

926213.fig.001
Figure 1: Repeated cyclic voltammograms of PEDOT film growth at a glassy carbon electrode in a solution of 0.1 M tetrabutylammonium perchlorate in acetonitrile containing 0.01 M EDOT, 10 V s−1 scan rate, and potential range −0.9–1.5 V.

Using cyclic voltammetry the response current for phenol oxidation at PEDOT modified electrode was investigated (see Figure 2). In contrast to the response of the bare GCE to phenol oxidation, the PEDOT modified electrode gave much pronounced current responses. Due to the electrocatalytic effect of the polymer, the shape and the response current are different from those of the bare GCE. The oxidation peak of phenol increased markedly with successive runs at the PEDOT/GCE and the response becomes reproducible after the tenth potential cycle as reported earlier [36]. It can be seen that the use of PEDOT coated GCE sensor also can overcome the problem of passivation.

926213.fig.002
Figure 2: Cyclic voltammogram of 1 × 10−4 M phenol (10 cycles) at PEDOT/GCE modified electrode in 0.1 M acetate buffer pH 7 and scan rate of 50 mV s−1

The GCE then was modified with PEDOT followed by coating with SWCNT. The excellent mechanical and electrical properties of carbon nanotubes help to transport electrons over long distances, and this quality gives the advantage of fabricating many polymer nanocomposites that have good mechanical and/or electrical properties [37]. The responses of 1 × 10−4 M phenol obtained at SWCNT/PEDOT/GCE multilayer film for different numbers of cycles of the film formation are shown in Figure 3.

926213.fig.003
Figure 3: The effect of polymer film thickness on the sensor response to 1 × 10−4 M phenol at SWCNT/PEDOT/GCE in 0.1 M acetate buffer, pH 6; other conditions are shown in Figure 2.

The lowest number of scans (5 cycles) gave broad voltammograms, while the upper scans (60 cycles) had low sensitivity and long response time due to slow penetration of the analyte molecule into the conducting polymer film. Hence the best combination, having large sensitivity and short response time, was selected to be 10 cycles of PEDOT polymerization over the bare electrode followed by casting of 20 μL dispersed SWCNT.

Cyclic voltammograms recorded for the oxidation of 1 × 10−4 M phenol at bare GCE, PEDOT/GCE, SWCNT/GCE, and SWCNT/PEDOT/GCE are shown in Figure 4. The peak current and the corresponding peak potential recorded for the bare GCE, PEDOT/GCE, SWCNT/GCE, and SWCNT/PEDOT/GCE are 4.63 μA and 0.851 V, 13.64 μA and 0.758 V, 22.60 μA and 0.683 V, and 25.05 μA and 0.701 V, respectively. This shows that the SWCNT/PEDOT/GCE produced significant increase in the peak current which is the result of incorporation of CNTs into the PEDOT polymer resulting in a synergic effect.

926213.fig.004
Figure 4: Cyclic voltammograms of 1 × 10−4 M phenol at GCE (a), PEDOT/GCE (b), SWCNT/PEDOT/GCE (c), and SWCNT/GCE (d); 0.1 M sodium acetate buffer solution, pH 6; scan rate of 50 mV s−1.

Efficiently dispersed SWCNTs establish a strong affinity with the surrounding polymer matrix and these principles were used to cast SWCNTs on the PEDOT polymer coated GCE. The designed electrode, SWCNT/PEDOT/GCE, has relatively good sensitivity to phenol oxidation and was used as a detector in the flow injection system for the determination of phenol and chlorophenols. Moreover in flow through systems the flowing carrier solution continuously cleans the surface of the electrode and removes reaction products and impurities from the electrode surface [38].

3.2. Flow Injection Analysis of Phenol and Its Derivatives at SWCNT/PEDOT/GCE
3.2.1. Experimental Variables for Flow Injection Analysis of Phenol and Chlorophenols

The electrochemical performance of GCE modified with elctropolymerized PEDOT and dispersed SWCNT was investigated for phenol and chlorophenols using 0.1 M sodium acetate carrier solution by flow injection analysis. The influences of the applied potential, flow rate, and effect of the pH on the amperometric signal of phenol and chlorophenols were studied.

To investigate the effect of modification of the electrode on the working potential, experiments were carried out on the bare GCE and SWCNT/PEDOT/GCE. As shown in Figure 5, similar trends of hydrodynamic responses (sigmoidal shape plots) for 1 × 10−4 M of phenol and chlorophenols were observed. The response for phenol oxidation at bare GCE shows a dramatic decrease of the current response as observed earlier [38] and at SWCNT/PEDOT/GCE the current signal increased in all cases, which can be justified by the facilitated electron transfer offered by SWCNT.

fig5
Figure 5: Effect of the applied potential on the flow injection response for 1 × 10−4 M 4-chlorophenol (CP), 2,4-dichlorophenol (DCP), 2,4,6-trichlorophenol (TCP), pentachlorophenol (PCP), and phenol (P) at bare GCE (A) and SWCNT/PEDOT/GCE (B); flow rate: 1.0 mL min−1; carrier solution: sodium acetate buffer (0.1 M); pH, 6.

As the flow rate affects the detection limit, sensitivity, and accuracy of the analysis, the effect of the flow rate on phenol and chlorophenols oxidation was investigated. Solutions of 1 × 10−4 M concentrations of each analyte were injected consecutively to the carrier solution (0.1 M sodium acetate) at flow rates ranging between 0.1 and 2 mL min−1. It was observed that the amperometric current responses increased with an increase in flow rate up to about 1.0 mL min−1 for phenol and chlorophenols. As the flow rate increases the dispersion decreases that results in decrease of the residence time and concurrently increases the sensitivity. At relatively higher flow rate (greater than 1.2 mL min−1) the amperometric current signal decreased, as shown in Figure 6, as previously observed for enzyme based FIA of phenols [38]. Such trends could be explained by the fact that as the sample passes faster through the electrode the smaller would be the fraction of the analyte that would be oxidized followed by a decrease in the amperometric signal. Also the electron transfer and mass transfer rate are not significantly different [18]. The optimum flow rate of the carrier solution for sharp peaks and high sensitivity observed were in the range of 0.9 to 1.2 mL min−1.

926213.fig.006
Figure 6: The amperometric current response of 1 × 10−4 M phenol (P), pentachlorophenol (PCP), 4-chlorophenol (CP), 2,4-dichlorophenol(DCP), and 2,4,6-trichlorophenol (TCP), at SWCNT/PEDOT/GCE modified electrode at different flow rates. Carrier solution: sodium acetate buffer (0.1 M); pH 7, applied potential: 0.725 V for phenol and 4-chlorophenol, 0.7 V for 2,4-dichlorophenol and 2,4,6-trichlorophenol, and 0.75 V for pentachlorophenol.

The pH of the carrier buffer solution used for the determination of phenol and its derivatives affects the amperometric peak current of the analytes. Figure 7 shows the influence of pH upon the response of 1 × 10−4 M phenol and chlorophenols at SWCNT/PEDOT/GCE in the pH range of 3–10. As can be seen from the figure, the current gradually increased with an increase in pH from 3 to 7. However, when the pH was further increased to 10 the peak current dramatically decreased. Therefore, considering the sensitivity of the determination of phenol and chlorophenols, optimum pH 7 for phenol, 4-chlorophenol, 2,4-dichlorophenol, and pentachlorophenol and pH 9 for trichlorophenol were chosen for the subsequent experiments.

926213.fig.007
Figure 7: Dependence of the current response of 1 × 10−4 M phenol (a), pentachlorophenol (b), 4-chlorophenol (c), 2,4-dichlorophenol (d), and 2,4,6-trichlorophenol (e) at SWCNT/PEDOT/GCE at different pH of 0.1 M acetate buffer carrier solutions at flow rate of 1.0 mL m−1 for phenol and pentachlorophenol, 1.1 mL min−1 for 4-chlorophenol, 2,4-dichlorophenol, and 2,4,6-trichlorophenol, applied potential as in Figure 6.
3.2.2. Sensor Performance

One of the most important performance parameters of a sensor is its operational stability. The operational stability of the SWCNT/PEDOT/GCE was investigated by measuring the current response of a series of 20 repetitive injections of 1 × 10−5 M phenol, 5 × 10−5 M 4-chlorophenol, 2 × 10−5 M 2,4-dichlorophenol, 2 × 10−5 M 2,4,6-trichlorophenol, and 5 × 10−5 M pentachlorophenol. The performance of SWCNT/PEDOT/GCE, as shown in Figure 8, is highly remarkable since after 20 continuous injections of the different phenolic analytes, the amperometric current response remains almost the same with standard deviation ranging from 0.47 to 1.82%, as shown in Table 1. This demonstrates the good stability of the SWCNT/PEDOT/GCE as a detector in flow injection system.

tab1
Table 1: Reproducibility of the stability measurements obtained at SWCNT/PEDOT/GCE in flow injection system.
fig8
Figure 8: Amperometric flow injection responses of chlorophenol (a) and stability plot (b) obtained for 20 repetitive injections of phenol (A), 2,4,6-trichlorophenol (B), 2,4-dichlorophenol (C), pentachlorophenol (D), and 4-chlorophenol (E) at SWCNT/PEDOT/GCE as amperometric detector pH 7 for phenol, 4-chlorophenol, and pentachlorophenol and 8 for 2,4-dichlorophenol and 9 for 2,4,6-trichlorophenol; other conditions are shown in Figure 7.

3.2.3. Analytical Performance of the SWCNT/GCE Detector in the Flow Injection System

Figure 9 demonstrates the amperometric current responses of 2,4,6-trichlorophenol with increasing concentrations. As shown in the figure, the electrochemical responses were sharp and consistent with rapid and efficient electron transfer processes. The amperometric peak current increased linearly with increase in the concentration of 2,4,6-trichlorophenol. The observed relationships were employed to construct reliable analytical calibration curves as shown by the inset of Figure 9, with regression equation of , where is the slope and is the intercept. The data obtained from the linear calibration curves under the optimum experimental conditions for each analyte are presented in Table 2. The evaluated analytical characteristics of the calibration plots show wide linear range of detections with low limits of detection (LOD). The detection limits were calculated based on the criterion, where is the slope of the calibration graph for each analyte and was estimated as the standard deviation of the responses obtained from the repetitive analyte injections at the lowest concentration.

tab2
Table 2: Characteristics of the calibration graphs for the different phenolic compounds.
926213.fig.009
Figure 9: Current versus time responses to the sequential injections of 2, 4, 8, 12, 16, 20, 24, 28, 32, 36, and 40 μM concentrations of 2,4,6-trichlorophenol (a)–(k); applied potential 0.700 V; flow rate 1100 μL min−1; carrier solution: 0.1 M acetate buffer pH 9. Inset: current (μA) versus concentration (μM).

The analytical performance of the SWCNT/PEDOT/GCE evaluated for the amperometric responses has been compared with other enzyme/enzymeless electrochemical sensors reported recently as shown in Table 3. Characteristics such as type of electrode, linear range, sensitivity, and limit of detection achieved were compared. In addition to the simplicity of the preparation of the sensor wider or similar dynamic ranges, low detection limits and comparable sensitivity were obtained compared to the recently reported sensors/biosensors, as shown in Table 3. Hence, it can be clearly deduced that the SWCNT/PEDOT/GCE detector offers advantageous compared with other reported sensors/biosensors.

tab3
Table 3: Comparison of analytical performance of the calibration curves of SWCNT/GCE with different modified electrodes.
3.2.4. Interference Study

In order to evaluate the selectivity of the developed sensor, possible interferences in the detection of phenol at SWCNT/PEDOT/GCE were investigated by the addition of various ions and compounds to the carrier solution (0.1 M acetate buffer solution, pH 7) containing 5 × 10−6 M phenol. Hundred fold additions of common ions such as Na+, K+, Ca2+, Mg2+ Cu2+, Cl, , and have no effect on the amperometric response of the designed electrode. The addition of two fold 2-nitrophenol, 4-nitrophenol, and pentachlorophenol did not interfere with the determination of phenol. As the optimum conditions of these compounds are similar due to their similarity in the oxidation of phenolic OH group, the effect from 4-chlorophenol, 2,4-dichlorophenol, and 2,4,6-trichlorophenol is significant. The result suggests that this proposed method has good selectivity towards the determination of phenol and chlorophenols. However the analysis of phenols and chlorophenols needs separation prior to analysis.

3.2.5. Analytical Applications

In order to evaluate the validity of the proposed method phenol was taken. The SWCNT/PEDOR/GCE was applied for tape water samples which were prepared by adding 3 μM of phenol. The results are given in Table 4. When increased concentrations of phenol were injected to water sample quantitative recoveries of 99.14–102.87% were obtained. These results confirm that the designed detector can successfully be used for the quantitative determination of phenol and chlorophenols in flow injection system.

tab4
Table 4: Recovery study.

4. Conclusion

An electrochemical detector based on SWCNT/PEDOT modified GCE for the analysis of phenol and chlorophenols was developed. The constructed modified electrode was optimized for the amperometric determination of phenolic compounds in flow injection mode. The results demonstrate that the amperometric sensor exhibits a good analytical performance for the detection of phenolic compounds in flowing systems. The developed sensor is simple and efficient and possesses a good operational stability and reproducibility. In general it is advantageous compared with other enzymztic and nonenzymatic sensors used in flow injection systems. The analytical performance makes possible the estimation of phenolic compound in tap water. The detector has good selectivity towards the determination of phenols and chlorophenols in terms of other interfering substances. However the analysis of mixtures of phenols and chlorophenols requires separation prior to analysis.

Conflict of Interests

The authors declare that there is no conflict of interests regarding the publication of this paper.

Acknowledgments

One of the authors, Negussie Negash, is grateful to the Graduate School of Addis Ababa University for financial support and to the National University of Lesotho for giving him the chance to use the resources and facilities of their research laboratory.

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