Direct Electrocatalytic Oxidation of Hydrogen Peroxide Based on Nafion and Microspheres MnO 2 Modified Glass Carbon Electrode

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Int. J. Electrochem. Sci., 4 (2009) 407-413 www.electrochemsci.org Direct Electrocatalytic Oxidation of Hydrogen Peroxide Based on Nafion and Microspheres MnO 2 Modified Glass Carbon Electrode Li Zhang *, Zhen Fang, Yonghong Ni and Guangchao Zhao Anhui Key Laboratory of Functional Molecular Solids, School of Chemistry and Materials Science, Anhui Normal University, Wuhu 241000, P. R. China * E-mail: lizhang3@mail.ahnu.edu.cn Received: 21 December 2008 / Accepted: 2 February 2009 / Published: 1 March 2009 Film of microspheres MnO 2 and Nafion composite fabricated on glass carbon electrode (GCE) were active for electrocatalytic oxidation of H 2 O 2 in phosphate buffer solution (PBS). The amperometric response to H 2 O 2 obtained at +0.8V (vs. Ag/AgCl) was rapid and highly sensitive. Under the optimized condition, the linear range for the detection of H 2 O 2 was 10.0 10 6 to 15.0 10 5 M with a detection limit of 2.0 10 6 M and a fast response time of within 5s. In addition, good reproducibility and long-term stability of the sensor make it valuable for further application. Keywords: microspheres MnO 2, Nafion, Glass carbon electrode, Electrocatalytic oxidation, H 2 O 2 1. INTRODUCTION The detection of H 2 O 2 is very important in various fields including clinic, food, pharmaceutical and environmental analyses, because H 2 O 2 is a chemical threat to the environment and the production of enzymatic reactions, at the same time, it has been recognized as one of the major factors in the progression of important diseases [1]. Accurate and reliable determination of H 2 O 2 has been widely investigated using chromatography [2], chemiluminscence [3] and electrochemistry [4] technologies. Among these methods, electrochemical detection is a most promising approach to achieve accurate, separate, and rapid H 2 O 2 monitoring [5]. Most of the H 2 O 2 biosensors developed till date are based on enzymes [6-8]. However, the immobilized enzyme on the surface of the electrode is facilitated to denature, which leads to such modified electrodes suffer from a poor enzyme activity, a low reproducibility and stability [9]. To remedy these problems, many efforts have been tried for the electrochemical measurements of H 2 O 2 without using enzyme [10-13]. Although some chemically

Int. J. Electrochem. Sci., Vol. 4, 2009 408 modified electrodes have been proposed to reduce the large overpotential required for the direct oxidation of H 2 O 2, it is interesting to develop new materials with high efficiency and small dimensions for the detection of H 2 O 2. Among various oxide materials, manganese dioxides (MnO 2 ) are a kind of attractive inorganic materials and have great potential as selective heterogeneous catalysts, adsorbents, and battery materials [14, 15]. In recent years, several kinds of MnO 2 nanoparticles were synthesized and used to construct biosensors. Schachl et al. reported the amperometric determination of H 2 O 2 with a carbon paste electrode modified with commercially available MnO 2 using flow injection analysis [16]. Lin et al. reported low potential amperometric determination of H 2 O 2 with a carbon paste electrode modified with nanostructured cryptomelane-type manganese oxides [17]. Hu et al. synthesized MnO 2 nanoparticles by rheological phase reaction and dispersed them in dihexadecyl hydrogen phosphate for amperometric determination of H 2 O 2 [1]. Porous films of MnO 2 nanoparticles and PDDA or myoglobin by layer-by-layer adsorption was fabricated by J. F. Rusling group [18]. They also fabricated films of polyions and octahedral layered manganese oxide nanoparticles on carbon electrode by layer-by-layer adsorption for electrochemically catalyze styrene epoxidation [15]. Beyene et al. reported biosensors based on manganese dioxide-modified carbon substrates [19]. All these researches are based on the excellent catalytic ability of MnO 2 nanoparticles modified electrode. In the present work, we constructed a novel functional hybrid film of nafion and MnO 2 microspheres on a glass carbon electrode as a catalytic layer for H 2 O 2 detection, taking advantage of MnO 2 microspheres as catalysts and microscopic network structure of nafion. MnO 2 microspheres, which have great surface area and excellent catalytic ability to H 2 O 2, were employed to enhance electron transfer. Nafion, due to its exceptional chemical stability and good biocompatibility, has been widely selected as the immobilization matrix for catalysts [20, 21]. Tests show that MnO 2 microspheres exhibit a remarkable electrocatalytic activity for the oxidation of H 2 O 2. The proposed sensor possesses high sensitivity and high stability. So it has the promising future for practical application. 2. EXPERIMENTAL PART 2.1. Reagents and apparatus Microscale manganese dioxide was synthesized according to reference [22]. Analytical grade MnSO 4 H 2 O (0.3380g, 2mmol), (NH 4 ) 2 S 2 O 8 (0.4564g, 2mmol) and 2mL concentrated sulfuric were mixed in 50mL distilled water at room temperature. The 1mL of 10mL AgNO 3 (0.1052g, 0.059mmol) solution was added. After the homogeneous solution was allowed to stand for 1-2 days, the products were filtered off, washed with absolute ethanol and distilled water respectively for several times, and then dried in vacuum. Electrochemical experiments were performed with CHI 440A electrochemical analyzer (ChenHua Instruments Co. Ltd., Shanghai, China) with conventional three-electrode cell. The working electrode was a MnO 2 microspheres modified glass carbon electrode. An Ag/AgCl and a

Int. J. Electrochem. Sci., Vol. 4, 2009 409 platinum electrode were used as the reference and the auxiliary electrode, respectively. Images of scan electron microscopy (SEM) were obtained using a Hitachi X-650 microscope (Japan). Analytical grade MnSO 4 H 2 O, (NH 4 ) 2 S 2 O 8, H 2 O 2 (30%) and concentrated sulfuric acid were purchased from Shanghai Chemical agent Co. Other chemicals were of analytical reagent grade. All the solutions were prepared with double distilled water and were deaerated with high purity nitrogen. Experiments were carried out at room temperature. 2.2. Electrode modification The dispersed MnO 2 microspheres on the electrode were fabricated by the following way: Firstly, the glass carbon electrode (GCE, =3mm) was polished with a 1700# diamond paper and washed successively with double distilled water and ethanol in an ultrasonic bath, then 15 cyclic scans were carried out in the potential of 2.0 to -2.0 V (vs. Ag/AgCl) in the solution of 1.0 mol/l H 2 SO 4. Secondly, Nafion was diluted with ethanol to 0.1%. 3 mg MnO 2 microspheres was dispersed in 2 ml Nafion solution. Next, 20 l of MnO 2 /Nafion solution (1.5 mg/ml) was cast on the surface of GCE and dried in air. Thus microspheres-mno 2 /nafion modified GCE was obtained. 3. RESULTS AND DISCUSSION 3.1. Characterization of the as-prepared MnO 2 microspheres The morphologies of the products were then studied by the field emission scanning electron microscope. Fig. 1 (left) indicated that the product consisted of microsperes with diameters of 1-2.5 µm. There are numerous nanorods on the surface of the MnO 2 microspheres. Fig. 1 (right) showed that nanorods with uniform diameters around 200 nm were fixed on the surface of the spheres, and they were densely parked and spherically aligned. Figure 1. SEM images of as-prepared MnO 2 microspheres with low (left) and high magnification (right).

Int. J. Electrochem. Sci., Vol. 4, 2009 410 3.2. Electrocatalytic oxidation of H 2 O 2 at microspheres MnO 2 /Nafion/GCE Fig. 2 (A) shows the cyclic voltammetric behavior of a Nafion/GCE and the microspheres MnO 2 /Nafion/GCE in the absence of H 2 O 2 in PBS (ph 7.0, 0.1M) at the scan rate of 10 mv/s. At the Nafion/GCE, no obvious oxidation and reduction peak was found in the potential range of 0-1.1 V (curve a). At the microspheres MnO 2 /Nafion/GCE, a couple of small reduction and oxidation peaks are observed (curve c) at around 0.5 V and 0.8 V, which are assignable to the reduction of MnO 2 to Mn (II or III) and the oxidation of Mn (II or III) to MnO 2 [23]. Fig. 2 (B) shows the cyclic voltammetric behavior of a Nafion/GCE and the microspheres MnO 2 /Nafion/GCE in the absence and presence of different concentrations of H 2 O 2 in PBS (ph 7.0, 0.1M) at the scan rate of 10 mv/s. At the Nafion/GCE, a slight oxidation current of 1.5 mm H 2 O 2 (curve b) was obtained at about 1.0 V. At the microspheres MnO 2 /Nafion/GCE, sensitive oxidation peaks at around 0.86 V (curve d and e) were found in the presence of 1.5 mm H 2 O 2 and 3 mm H 2 O 2. According to the experimental results, the oxidation current of Mn (II or III) to MnO 2 was significantly increased when increasing the concentration of H 2 O 2. 3.0 (A) 4 (B) 1.5 0.0-1.5-3.0 c a 0 a b c d.5-8 e -6.0 1.2 1.0 0.8 0.6 0.4 0.2 0.0 E / V vs. Ag / AgCl 1.2 1.0 0.8 0.6 0.4 0.2 0.0 E / V vs. Ag / AgCl Figure 2. (A) CVs recorded in PBS (ph 7.0, 0.1M) at Nafion/GCE (a) and MnO 2 /Nafion/GCE (c). (B) CVs of Nafion/GCE (a, b) and microspheres MnO 2 /Nafion/GC electrode (c, d, e) in the absence (a, c) and presence (b, d) of 1.5 mm H 2 O 2, (e) 3.0 mm H 2 O 2 in PBS (ph 7.0, 0.1M). Scan rate: 10 mv/s. 3.3 Optimization of the H 2 O 2 determination conditions To improve the performance of the sensor, the effect of the determination conditions such as the concentration of MnO 2 in Nafion solution and the ph value on the response of the microspheres MnO 2 /Nafion/GCE to H 2 O 2 has been investigated in detail. The effect of the concentration of MnO 2 in Nafion solution on the response current of the microspheres MnO 2 /Nafion/GCE to H 2 O 2 is illustrated in Fig. 3 (A). When the concentration of MnO 2

Int. J. Electrochem. Sci., Vol. 4, 2009 411 in Nafion solution was changed from 0.1 to 2.0 mg/ml, the maximum response current was observed at 1.5 mg/ml. So the concentration of 1.5 mg/ml was selected as the optimum concentration. The effect of ph value on the response current of the microspheres MnO 2 /Nafion/GCE was also studied between 5.0 and 9.0 in 0.1 M PBS. As shown in fig. 3 (B), the response current increased from 5.0 to 7.0, and a slightly increase from 7.0 to 8.0. In this work, ph 7.0 was selected in the subsequent experiments. -5 (A) -6.0 (B).5-3 -2-3.0-1 -1.5 0 0.0 0.4 0.8 1.2 1.6 2.0 Concentration of MnO 2 in nafion solution (mg/ml) 0.0 5 6 7 8 ph Figure 3. (A) Effect of MnO 2 concentration in Nafion solution on the response current of the microspheres MnO 2 /Nafion/GCE to addition of 1.5 mm H 2 O 2 to PBS (ph 7.0, 0.1M). (B) Effect of ph solution on the response current of the microspheres MnO 2 /Nafion/GCE to addition of 1.5 mm H 2 O 2. Scan rate: 10 mv/s. 0-2 a -6-2 b -6-8 -8 0 50 100 150 200 µ M -10 0 200 400 600 Figure 4. Current-time recording obtained on increasing the H 2 O 2 concention in 10 M steps at (a) Nafion/GCE and (b) microspheres MnO 2 /Nafion/GCE at an operating potential of 0.8 V in PBS (ph 7.0, 0.1M). Inset: calibration curve of the sensor for H 2 O 2 concentration from 10.0 10 6 to 15.0 10 5 M. T / s

Int. J. Electrochem. Sci., Vol. 4, 2009 412 3.4 Amperometric response of H 2 O 2 at microspheres MnO 2 /Nafion/GCE Fig. 4 compares the amperometric response (at +0.80 V) of the (a) Nafion/GCE and (b) microspheres MnO 2 /Nafion/GCE to the successive addition of 10 µm H 2 O 2. As expected from the voltammetric data (Fig. 2(B, b)), the Nafion/GCE is not responsive to the addition of H 2 O 2. In contrast, the microspheres MnO 2 /Nafion/GCE respond rapidly to the changes in H 2 O 2 concentration, producing steady-state signals within 5 s (Fig. 4(b)). Such a fast response implies that microspheres MnO 2 can promote the oxidation of H 2 O 2. The linear relationship between the catalytic current and the concentration is shown in the inset of the fig. 4. As can be seen, the microspheres MnO 2 /Nafion/GCE displays linear response range of 10.0 10 6 to 15.0 10 5 M (correlation coefficient: 0.997), with a detection limit of 2.0 10 6 M at a signal-to-noise ratio of 3. The reproducibility and stability of the sensor were also investigated. Ror 10 replicate measurements of one electrode studied at 50 M H 2 O 2, the relative standard deviation (R. S. D) was 3.2%. We studied the storage stability of the sensor by storing it at room temperature. One week later the response of the sensor still retained 93.5% and the next three weeks the response still retained 89.0% of the initial value. These experiments results confirmed that the modified electrode were highly reproducibility and stability. 3.5 Effect of interferents The influence of possible interfering species on the current response of the sensor was examined and is given in Table 1. The current response obtained with 10 : 1 concentration ratio of interfering species and H 2 O 2 was compared with the results obtained with that of pure H 2 O 2 alone. As shown, Uric acid, dopamine and L-cysteine induced slight effect on the steady-state current to H 2 O 2. The steady-state current to H 2 O 2 was increased to 109% of original response by addition of ascorbic acid. So there was no obvious interference in the measure of the electrode. The modified electrode exhibits great prospects for future biosensor work. Table 1. Possible interferences tested with the modified electrode Possible interferences Uric acid Dopamine L-cysteine ascorbic acid Current ratio a 0.985 0.987 1.002 1.090 a Ratio is the current from a mixture of 1.0 mmol interfering substances and 0.1 mm H 2 O 2 versus the current from 0.1 mm H 2 O 2 alone. Assay solution: 0.1 M PBS.

Int. J. Electrochem. Sci., Vol. 4, 2009 413 4. CONCLUSIONS A novel functional hybrid film of Nafion and MnO 2 microspheres on a glass carbon electrode was constructed as a catalytic layer for H 2 O 2 detection in the present work. Tests show that MnO 2 microspheres exhibit a remarkable electrocatalytic activity for the oxidation of H 2 O 2. The proposed sensor possesses high sensitivity and stability, good reproducibility and selectivity. These advantages make it promising for providing a simple method for practical application. ACKNOWLEDGEMENTS The authors thank the Young Fund of Anhui Normal University (2008xqn61) for fund support. References 1. S. Yao, J. Xu, Y. Wang, X. Chen, Y. Xu, S. Hu, Anal. Chim. Acta 557 (2006) 78. 2. W. M. Weigert, Chem. Ztg. 99 (1975) 106. 3. H. Knorre, Galvanotechnik 66 (1975) 374. 4. X. M. Miao, R. Yuan, Y. Q. Chai, Y. T. Shi, Y. Y. Yuan, J. Electroanal. Chem. 612 (2008) 157. 5. J. Gong, L. Wang, K. Zhao, D. Song, Electrochem. Commun. 10 (2008) 123. 6. C. X. Lei, S. Q. Hu, N. Gao, G. L. Shen, R. Q. Yu, Bioelectrochemistry 65 (2004) 33. 7. H. Y. Wang, R. Guan, C. H. Fan, D. X. Zhu, G. X. Li, Sens. Actuators B: Chem. 84 (2002) 214. 8. Q. L. Wang, G. X. Lu, B. J. Yang, Sens. Actuators B: Chem. 99 (2004) 50. 9. Y. Yang, S. Mu, J. Electroanal. Chem. 432 (1997) 71. 10. I. L. de Mattos, L. Gorton, T. Ruzgas, Biosens. Bioelectron. 18 (2003) 193. 11. T. Y. You, O. Niwa, M. Tomita, S. Hirono, Anal. Chem. 75 (2003) 2080. 12. J. Zhang, L. Gao, Mater. Lett. 61 (2007) 3571. 13. J. D. Qiu, H. Z. Peng, R. P. Liang, J. Li, X. H. Xia, Langmuir 23 (2007) 2133. 14. S. L. Brock, M. Sanabria, J. Nair, S. L. Suib, T. Ressler, J. Phys. Chem. B 105 (2001) 5404. 15. L. Espinal, S. L. Suib, J. F. Rusling, J. Am. Chem. Soc. 126 (2004) 7676. 16. K. Schachl, H. Alemu, K. Kalcher, J. Jezkova, I. Svancara, K. Vytras, Analyst 122 (1997) 985. 17. Y. Lin, X. Cui, L. Li, Electrochem. Commun. 7 (2005) 166. 18. Y. Lvov, B. Munge, O. Giraldo, I. Ichinose, S. L. Suib, J. F. Rusling, Langmuir 16 (2000) 8850. 19. N. W. Beyene, P. Kotzian, K. Schachl, K. Vytas, K. Kalcher, Talanta 64 (2004) 1151. 20. M. Pan, H. L. Tang, S. P. Jiang, Z. Liu, Electrochem. Commun. 7 (2005) 119. 21. M. Pan, H. L. Tang, S. P. Jiang, Z. Liu, Electrochem. Soc. 152 (2005) 1081. 22. Z. Li, Y. Ding, Y. Xiong, Q. Yang, Y. Xie, Chem. Commun. (2005) 918. 23. E. Turkusic, J. Kalcher, E. Kahrovic, N. W. Beyene, J. Kalcher, Talanta 65 (2005) 559. 2009 by ESG (www.electrochemsci.org)