Sensors and Actuators B 125 (2007) 92–99

Novel amperometric carbon monoxide sensor based on multi-wall carbon nanotubes grafted with polydiphenylamine—Fabrication and performance P. Santhosh a , K.M. Manesh a , A. Gopalan a,b,c , Kwang-Pill Lee a,b,∗ a

Advanced Analytical Science and Nanomaterials Lab, Department of Chemistry Education, Kyungpook National University, Daegu 702-701, South Korea b Nano Practical Application Center, Daegu 704-230, South Korea c Department of Industrial Chemistry, Alagappa University, Karaikudi-630 003, India

Received 23 August 2006; received in revised form 24 January 2007; accepted 24 January 2007 Available online 3 February 2007

Abstract A novel amperometric sensor based on multi-wall carbon nanotubes (MWNT) grafted polydiphenylamine (PDPA), MWNT-g-PDPA, has been developed for the determination of carbon monoxide (CO). Cyclic voltammetry is used to fabricate the modified electrode and to demonstrate the electroactivity of MWNT-g-PDPA-ME toward gaseous CO. The MWNT-g-PDPA-ME exhibits high sensitivity for oxidation of CO in a 0.5 M HClO4 solution. Chronoamperometry is carried to determine the working range of CO at MWNT-g-PDPA-ME. The dependence of the response current on CO concentration is explored under optimal conditions and an excellent linear concentration range between 10 and 200 ppm (correlation coefficient r = 0.9941) with a substantially low detection limit of 0.01 ppm is obtained. Further, the response and recovery transients of CO gas at MWNT-g-PDPA-ME are determined. © 2007 Elsevier B.V. All rights reserved. Keywords: CO; Sensor; Multiwall carbon nanotubes; Polydiphenylamine

1. Introduction Carbon monoxide (CO), a major atmospheric pollutant is produced by the incomplete combustion of fossil fuels-gas, oil, coal and wood used in boilers, engines, oil burners, gas fires, water heaters, solid fuel appliances and open fires [1]. CO is a toxic chemical, which is harmful to human health. CO poisons are caused by entering the lungs via the normal breathing mechanism and displacing oxygen from the bloodstream. Interruption of the normal supply of oxygen puts at risk the functions of the heart, brain and other vital functions of the body. Many analytical sensors based on semiconductors [2], catalyst-combustion [3] and electrochemical reactions [4–6] have been developed to measure the CO concentration in air. Low selectivity is one of the major disadvantages with the first two types of CO sensors. On the other hand, amperometric CO

∗ Corresponding author at: Advanced Analytical Science and Nanomaterials Lab, Department of Chemistry Education, Kyungpook National University, Daegu 702-701, South Korea. Tel.: +82 539505901; fax: +82 539528104. E-mail address: [email protected] (K.-P. Lee).

0925-4005/$ – see front matter © 2007 Elsevier B.V. All rights reserved. doi:10.1016/j.snb.2007.01.044

sensors offer high sensitivity and better resolution [7]. Also, various room-temperature CO sensors have been developed for commercial application based on semiconductors such as SnO2 , ZnO, TiO2 , MoO3 and Fe2 O3 [8–10]. The main concern is that metal oxide sensors tend to suffer from baseline drifts upon interaction with poisoning species. Carbon nanotubes (CNTs) have been attracting considerable attentions over the last decade due to their remarkable mechanical and electronic properties [11,12]. CNTs have been proved to be suitable material as electrodes or electrocatalyst supports due to their many advantages such as high electronic conductivity for the promotion of electron transfer reactions and better electrochemical and chemical stabilities in aqueous and non-aqueous solutions. At the same time, conducting polymers are extensively studied for their electrocatalytic activity [13]. Composite materials based on the combination of CNT and conducting polymers have shown properties of the individual components with a synergistic effect [14–16]. The aim of the present study is to develop an amperometric sensor for CO gas. Multiwall carbon nanotubes (MWNT) are suitably functionalized and used to form grafted chains of polydiphenylamine (PDPA), MWNT-g-PDPA, on a glassy carbon

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Scheme 1.

(GC) electrode through electrochemical polymerization. The modified electrode has augmented superior performance for CO detection from the combined influence of MWNT and PDPA. The results are presented here. 2. Experimental 2.1. Reagents Diphenylamine (DPA, Aldrich) was distilled and used. Poly(ethylene glycol) bis(3-aminopropyl) terminated (PEG-AT) and cetyltrimethyl ammonium bromide (CTAB) were of analytical grades from Aldrich and used as received. MWNTs (10–50 nm in diameter) obtained from CNT Co. Ltd. Incheon, Korea were purified by adopting the following procedure and used. The MWNTs were subjected to air oxidation at 150 ◦ C for a period of 12 h, followed by annealing in argon atmosphere at 800 ◦ C for 1 h. Finally, MWNTs were sonicated in concentrated HCl (10 mg in 20 mL), filtered, washed thoroughly with water and 2-propanol, and dried under vacuum. The residual iron content in the MWNTs was found to be less than 0.3% after the purification process. 2.2. Fabrication of MWNT-g-PDPA modified electrode and sensor studies 2.2.1. Fabrication of MWNT-g-PDPA modified electrode MWNT-g-PDPA-ME was fabricated by modifying a GC electrode through electrochemical polymerization of a solution

consisting of amine functionalized MWNT (MWNT–NH2 ) and DPA. Prior to the fabrication of modified electrode, a GC electrode was mechanically polished to a mirror polish using polishing microcloth containing 0.05 ␮M Al2 O3 slurry and carefully cleaned with 1:1 HNO3 –H2 O (1:1), ethanol and water by ultrasonication. Fabrication of MWNT-g-PDPA-ME involved two steps. In the first step, MWNT was amine functionalized (MWNT–NH2 ) with PEG-AT. In the second step, cyclic voltammetry was used to deposit MWNT-g-PDPA as a film on the surface of working electrode (GC) to obtain MWNT-g-PDPA-ME (Scheme 1). MWNT–NH2 was prepared by adopting the procedure detailed in our previous report [17]. One hundred and fifty milligram of MWNT–NH2 was homogeneously dispersed in 40 mL of 0.5 M CTAB using ultrasonication (BRANSON Digital Sonifier) for 3 h. Ten millilitre of 50 mM of DPA (in 4 M H2 SO4 ) was added to the above solution. Ten millitre of the solution containing MWNT–NH2 (0.1%) and DPA (10 mM) was subjected to electrochemical polymerization by continuous potential cycling in the potential range of 0–800 mV using a three electrode cell assembly consisting of GC as a working electrode, saturated calomel electrode (SCE) and platinum wire as reference and counter electrodes, respectively. Green coloured MWNT-g-PDPA was found to be deposited on the surface of GC electrode. The MWNT-gPDPA-ME was washed with water and stored in a nitrogen atmosphere.

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2.2.2. Sensor studies Measurement of CO gas sensing properties was performed in an electrochemical cell assembly as described in literature [18]. The GC electrode modified with MWNT-g-PDPA was used as a working electrode, and SCE and a platinum wire were used as reference and counter electrodes, respectively. The standard CO gas (99.999% purity) used in this study contained impurities of less than 10 ppm (mol/mol), which includes nitrogen (<3 ppm), oxygen (<2 ppm), CO2 (<2 ppm) and sulfur (<1 ppm). The CO gas was used without further purification. Various concentrations of sample gases were prepared by diluting CO gas with air. The total flow rate of the CO gas was adjusted at 500 mL/min. Cyclic voltammetry, chronoamperometry and impedance spectroscopy were used to characterize the sensor electrode. Cyclic voltammetry was performed in the potential range between 0 and 1000 mV versus SCE at a scan rate of 50 mV s−1 . The impedance measurement was performed with the induced ac amplitude of 10 mV and a frequency of 5 MHz-100 mHz. Chronoamperometry was carried out at an applied potential of +550 mV versus SCE under magnetic stirring (150 rpm). After the background current decayed to a steady value, an aliquot amount of CO gas was introduced into the electrolyte solution and the steady state current was measured. The dependence of the amperometric current upon the CO concentration was measured as a sensing signal. All the electrochemical measurements were carried out using EG & G PAR 283 Electrochemical Analyzer with Frequency Response Analyzer 1025. 3. Results and discussion 3.1. Fabrication of MWNT-g-PDPA-ME Cyclic voltammetry was used for the fabrication of MWNTg-PDPA-ME through the electro-polymerization of DPA in the presence of MWNT–NH2 . Fig. 1 displays the cyclic voltammograms (CVs) recorded during the electrochemical polymerization of the solution consisting of MWNT–NH2 and

DPA. CV patterns of the polymer film deposited from the mixture of MWNT–NH2 and DPA showed a single oxidation wave around 600 mV with a cathodic wave at 300 mV in the reverse scan. In the case of electrochemical polymerization of diphenylamine (in the absence of MWNT–NH2 ), two anodic processes were noticed at 650 mV and 740 mV with cathodic counter parts at 570 mV and 690 mV, respectively [15,19]. These two anodic peaks were assigned for the generation of N,N -diphenyl benzidine type radical (DPB•+ , polaronic form of PDPA structure) and N,N -diphenyl benzidine dication (DPB2+ , bipolaronic form of PDPA structure), respectively. In the case of the polymer film deposited with the mixture of MWNT–NH2 and DPA, polaron formation in PDPA structure was augmented by the presence of MWNT–NH2 . The formation of MWNT-g-PDPA was witnessed from the differences in the electrochemical characteristics between polymerization of DPA in the presence and absence of MWNT–NH2 . In the first instance, a continuous anodic current was noticed for the initial anodic scan of potential for the solution of DPA containing MWNT–NH2 . This is in contrast to an oxidation peak noticed around 700 mV for the solution containing only DPA. The continuous increase in peak in the case of the mixture of DPA and MWNT–NH2 is attributed to the simultaneous oxidation of amine sites present in MWNT–NH2 and DPA. As a result, a cross-reaction occurs between the amine cation radicals formed from MWNT–NH2 and DPA. The cation radical sites thus generated in MWNT–NH2 and DPA interact to result in grafting of PDPA onto MWNT. This is the nucleation step for grafting of PDPA onto MWNT. The gradual increase in current value with the number of cycles (Fig. 1) confirms the continuous building up of the MWNT-g-PDPA film over the surface of GC electrode. The grafting of the conducting polymer with amine functionalized MWNT is well documented in our previous reports [14–17]. The field emission transmission electron microscopy (FETEM) image of MWNT-g-PDPA (Fig. 2) reveals the morphology of MWNT-g-PDPA. The surface of MWNT was covered by a layer of PDPA to a thickness of 10–15 nm. This type of morphology is entirely different from the previous reports on the preparation of a polyaniline (PANI) modified MWNT electrode. In the previous report, a partial masking of CNT with PANI has been reported [20]. Hence, electropolymerization of a mixture of DPA and MWNT–NH2 generates MWNT-g-PDPA-ME. This MWNT-gPDPA-ME was used as a sensor electrode for carbon monoxide gas. The MWNT-g-PDPA-ME showed good sensor characteristics for CO. 3.2. Sensor characteristics of MWNT-g-PDPA-ME

Fig. 1. Cyclic voltammograms recorded during the electrochemical polymerization of the solution containing 10 mM diphenylamine and 30 mg poly(ethyleneglycol) bis (3-aminopropyl) functionalized MWNT.

Cyclic voltammetry was performed to understand the electrocatalytic behavior of MWNT-g-PDPA-ME towards the oxidation of CO in a 0.5 M HClO4 solution and compared with MWNT–NH2 –ME and PDPA-ME. Fig. 3A shows the CVs recorded at MWNT-g-PDPA-ME in the presence (400 ppm) and absence of CO in a 0.5 M HClO4 solution, respectively. MWNT-g-PDPA-ME shows pronounced electrocatalytic activ-

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Fig. 2. FESEM image of MWNT-g-PDPA-ME; scale bar 20 nm.

ity for oxidation of CO in comparison to MWNT–NH2 –ME and PDPA-ME (Fig. 3B and C, respectively). This can be clearly witnessed from the enhanced peak current for CO oxidation (515 ␮A/cm2 ) with a far less oxidation potential (Eox : 570 mV) at MWNT-g-PDPA-ME in comparison with MWNT–NH2 –ME (Eox : 725 mV) and PDPA-ME (Eox : 732 mV). Interestingly, the MWNT-g-PDPA-ME exhibits enhanced sensitivity for oxidation of CO over the nano-Au modified Pt electrode [18] and Sn modified Pt/Nafion assembly [21]. The enhanced peak current and the negative shift in the oxidation overpotential for CO oxidation indicate the enhanced electrocatalytic activity of MWNT-g-PDPA-ME. The shift in the overpotential of CO may be due to the kinetic and transport effect of CO at a MWNT-

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g-PDPA-ME interface that may probably cause a substantial increase in the electron transfer rate for the oxidation of CO. Further, experiments were performed and the diffusion coefficient D for the charge transfer reaction was evaluated. The mean value of D determined as 2.18 × 10−5 cm2 s−1 at MWNT-g-PDPA-ME which was far higher than that observed at MWNT–NH2 –ME (7.46 × 10−5 cm2 s−1 ) and PDPA-ME (1.93 × 10−12 cm2 s−1 ). The higher D value at MWNT-g-PDPA-ME substantiates the enhanced electrocatalytic of the modified electrode. The combined presence of MWNT and PDPA in MWNTg-PDPA-ME is the reason for the pronounced sensitivity for oxidation of CO. A three-dimensional electron-conductive network extending throughout the MWNT matrix is expected to be formed and result in the improvement of its electronic and ionic transport capacity. The excellent sensitivity for the oxidation of CO at MWNT-g-PDPA-ME arises from the additional surface area provided by PDPA for the oxidation process. Besides, at the MWNT-g-PDPA-ME, CO was oxidized with a lesser overpotential (>150 mV). This is an indication of more efficient electron transfer at MWNT-g-PDPA-ME than at MWNT–NH2 –ME. The effect of scan rate on the voltammetric response of CO at MWNT-g-PDPA-ME was investigated by cyclic voltammetry. The peak currents for CO oxidation increased linearly with the square root of scan rate in the range of 10–300 mV s−1 with a correlation coefficient of 0.9956. This suggests that the process of electrode reaction is controlled by the diffusion process. Fig. 4 shows the CV curves obtained with MWNT-g-PDPA-ME in the presence of different concentrations of CO in 0.5 M HClO4 . Increasing the concentration of CO resulted in an increased current response toward CO oxidation. There was a good linear correlation between CO oxidation current and CO concentration. The effect of electrolyte solution, amount of MWNT–NH2 loading and film thickness were determined and optimized to have better CO sensitivity.

Fig. 3. Cyclic voltammograms of (A) GC/MWNT-g-PDPA; (B) GC/MWNT–NH2 ; and (C) GC/PDPA modified electrodes in the (i) presence (400 ppm) and (ii) absence of CO in 0.5 M HClO4 ; scan rate: 50 mV s−1 .

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Fig. 4. Cyclic voltammograms toward CO with MWNT-g-PDPA-ME in the presence of different concentrations of CO: (i) 100; (ii) 200; (iii) 300; (iv) 400 and (v) 500 ppm in 0.5 M HClO4 . Scan rate: 50 mV s−1 .

3.3. Factors influencing the oxidation of CO 3.3.1. Effect of electrolyte solution The effect of electrolyte solution on the oxidation of CO was determined at MWNT-g-PDPA-ME in different acid solutions such as HClO4 , H2 SO4 , HCl and H3 PO4 through cyclic voltammetry measurements. Among the electrolyte investigated, MWNT-g-PDPA-ME showed a lower onset potential and higher current response for CO oxidation in 0.5 M HClO4 . The enhanced catalytic activity for the oxidation of CO at MWNTg-PDPA-ME in 0.5 M HClO4 is due to the following fact. It is reported [22] that there is a competition between anions and surface intermediates of an electrochemical process for sites on the electrode surface. The anions inhibit the electrochemical processes by occupying the active sites. The amount an anion inhibits a process increases with its adsorption strength. The following shows the order of the anions in their adsorption strength: ClO4 − < HSO4 − < H2 PO4 − < Cl− The properties of the electrolyte improve as the anion adsorption strength decreases, i.e. the lower the anion strength, the better the electrolyte. Chlorate anions have one of the lowest adsorption strengths and hence showed enhanced electrochemical properties when used as a medium for the oxidation of CO at MWNT-g-PDPA-ME. 3.3.2. Effect of MWNT concentration MWNT-g-PDPA films were deposited on a GC electrode from solutions of DPA (10 mM) having different amounts of MWNT–NH2 . The loading of MWNT–NH2 increases with increasing the amount of MWNT in the electrolyte solution. The voltammograms of CO oxidation on MWNT-g-PDPA-ME at different MWNT–NH2 loadings (with the same film thickness of PDPA) are given in Fig. 5. From this figure, it is clear that the onset oxidation is shifted to a lower potential with increasing the MWNT–NH2 loading up to 30 mg and reaches the minimum at a MWNT loading of 30 mg. Further increasing the MWNT–NH2 loading resulted in the shift of peak potential to more positive potential. Hence, the optimum MWNT–NH2 loading of 30 mg was chosen for CO oxidation at MWNT-g-PDPA-ME.

Fig. 5. Cyclic voltammograms toward CO with MWNT-g-PDPA-ME in 0.5 M HClO4 . Amount of MWNT-NH2 : (i) 10; (ii) 20; (iii) 30; (iv) 40 and (v) 50 mg. Film thickness: 10 ␮m. Scan rate: 50 mV s−1 .

3.3.3. Effect of PDPA thickness In order to study the effect of PDPA film thickness on the electrocatalytic activity for CO oxidation, electrodes with different film thickness were fabricated. The thickness of modified layer (MWNT-g-PDPA) on a GC electrode was controlled by changing the number of potential cycles during electropolymerization. The charge consumed during the electropolymerization process was used to calculate the thickness of the electroactive film over the GC electrode. The cyclic voltammograms (CVs) for electro-oxidation of CO at MWNT-g-PDPA-ME with different thickness of PDPA, but with the same MWNT loadings, are shown in Fig. 6. No apparent shift in the potential was noted, which means that the peak potential is independent of the film thickness of PDPA on MWNT-g-PDPA-ME towards oxidation of CO. The results are in agreement with many other authors [23,24]. On the other hand, the peak current at the MWNT-gPDPA-ME increases with an increase in thickness of PDPA up to 10 ␮m. After a thickness of 10 ␮m, only a slight increase in peak current was observed. This may be due to the slow diffusion of CO into the thin film and therefore a thickness of 10 ␮m was found as optimum and used in further experiments. 3.4. Impedance spectroscopy In order to have an insight into the interfacial behavior of MWNT-g-PDPA-ME, impedance spectroscopic measurements were performed at the MWNT-g-PDPA-ME in the presence and absence of CO. Fig. 7 shows the Nyquist plots obtained from the MWNT-g-PDPA-ME in the absence and presence of 500 ppm CO. The interfacial impedance is dependent on the material com-

Fig. 6. Cyclic voltammograms toward CO with MWNT-g-PDPA-ME in 0.5 M HClO4 . Film thickness: (i) 3; (ii) 7; (iii) 10; (iv) 13 and (v) 15 ␮m. Amount of MWNT-NH2 : 30 mg. Scan rate: 50 mV s−1 .

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Fig. 8. Effect of the dc bias on the impedance response of MWNT-g-PDPA-ME in CO gas; (i) 10; (ii) 30; (iii) 50; (iv) 70 and (v) 100 mV.

Fig. 7. Nyquist plots for the MWNT-g-PDPA-ME showing the effect of the presence of CO; (A) impedance plot in the full-range; (B) the details in the circled zone in (A).

bination of electrolyte and electrode [25]. Any change in either electrolyte or sensing electrode could lead to variation of the interface impedance. In both cases (in the presence and absence of CO), two semicircles were observed within the frequency range studied. It can be seen from the figure that the large semicircle in the low frequency region was shifted down toward the real Z -axis in the presence of CO. However, the small semicircle in the high frequency region was not affected by the presence of CO gas [26]. The Nyquist plot obtained at MWNT-g-PDPA-ME can be interpreted by an equivalent circuit;

The small semicircle in the high frequency region represented by RC elements, where Rb and Cb correspond to the bulk resistance and bulk capacity, respectively. The frequency fs (at maximum Z ) was about 98 kHz. Rb and Cb were determined as 0.9 k and 2.7 × 10−8 F, respectively, for MWNT-g-PDPA-ME in the absence of CO. It is interesting to note that the semicircle in the high frequency region was insensitive to the presence of CO gas. The large semicircle in the low frequency region was attributed to the interfacial contribution comprising of a constant phase element (CPE) and Ri . CPE was used to account for the non-ideal behavior of the double layer at the interface of the sensor electrode. Ri represents the charge transfer resistance at the

interface. Based upon the equivalent circuit modeling results, Ri was found to be 16.2 k in the absence of CO. Ri was reduced from 16.2 to 12.4 k by the introduction of 500 ppm CO. It is clear from the Fig. 7 that only the interfacial impedance was significantly affected by the presence of CO. Hence, it can be concluded that the oxidation of CO to CO2 occurred at the triplephase boundary between the electrolyte, MWNT-g-PDPA-ME and CO gas. The application of small AC amplitude (10 mV) induces the oxidation of CO at the triple-phase boundary. The electrochemical oxidation introduced the charge carriers to the electrolyte/electrode interface, leading to change in the kinetics of charge transfer at the electrolyte/electrode interface. This is responsible for the decrease in the interface impedance on introduction of CO gas. Further, the effect of the dc bias on the impedance behavior of CO at MWNT-g-PDPA-ME was studied. Nyquist plots were obtained by the application of different dc and are shown in Fig. 8. It can be seen from the figure that the interfacial resistance (Ri ) decreased with an increase in the amplitude of dc bias, implying the effect of the applied bias on the rate-limiting step of the electrode reaction. The results suggest that an electrochemical reaction rather than a surface-catalyzed chemical reaction was occurred for the oxidation of CO at the triple-phase boundary, which resulted in a decrease in Ri with an increase of dc bias at the MWNT-g-PDPA-ME/electrolyte interface [27]. 3.5. Amperometric CO sensor behavior In order to examine the sensing character of MWNT-g-PDPAME to CO, amperometry measurements were performed in a 0.5 M HClO4 solution. Fig. 9A shows amperograms recorded during the successive addition of 10 ppm CO under stirred conditions, where the potential of the MWNT-g-PDPA-ME was kept at +550 mV. The amperogram shows an increase in current with subsequent CO injections. A linear relationship between peak currents and CO concentrations was obtained in a range of 10–200 ppm with a correlation coefficient of r = 0.9941 (Fig. 9B). The detection limit has been estimated to be 0.01 ppm. The response and recovery transients of 100 ppm CO gas at MWNT-g-PDPA-ME were determined. The response to each concentration of CO was rather quick; the 96% response and the 98% recovery times to 100 ppm CO were about 2 and 3 s,

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current was observed. These results demonstrate the stability of the MWNT-g-PDPA-ME against these gases. 4. Conclusions A new kind of electrode for electrochemical sensing of CO was developed by grafting PDPA on the surface of MWNT. The modified electrode has augmented superior performance for CO detection from the combined influence of functionalized MWNT and PDPA. MWNT-g-PDPA-ME is anticipated to provide a basis for practical approach to CO monitoring. Acknowledgments This work was supported by Korean Research Foundation Grant (KRF-2006-J02402). The authors acknowledge Kyungpook National University Center for Scientific Instrument References

Fig. 9. (A) Amperometric current response of the MWNT-g-PDPA-ME toward successive addition of 10 ppm of CO in 0.5 M HClO4 at 550 mV; (B) calibration curve.

respectively. The response rate to CO was confirmed to be also rather high, as in the case of CO detection. 3.6. Selectivity and stability The selectivity of MWNT-g-PDPA-ME towards CO gas was assessed. Significant interference from NH3 , CH4 , C3 H8 and N2 O (500 ppm) were observed at MWNT-g-PDPA-ME. However, when the MWNT-g-PDPA-ME was coated with 0.5% Nafion, such interference from the gases was not detected at MWNT-g-PDPA-ME. The insignificant or no interference from the gases is attributed to the solubility and dielectric properties of the gases at a fluorinated polymer [28], Nafion coated on the MWNT-g-PDPA-ME. The dielectric constants of the gases are less than that of CO and hence do not show interfering signals at the Nafion film/gas interface. The fluorinated polymer membrane effectively prevented these and makes the MWNT-g-PDPA-ME selective towards CO gas. Long-term stability of the MWNT-g-PDPA-ME was checked for 10 days and CO gas sensing characteristics of the sensors were evaluated continuously. The MWNT-g-PDPA-ME did not show any significant change in the sensing current in comparison to the freshly prepared sensor. Sample gases containing CH4 , C3 H8 , NOx , SO2 and C2 H5 OH were mixed with CO and the stability of the sensor was also checked. No change in the sensing

[1] K. Wark, C.F. Warner, Air Pollution-Its Origin and Control, second ed., Harper & Row Publishers, New York, 1981. [2] V.A. Chaudhary, I.S. Mulla, S.R. Sainkar, A.A. Belhekar, K. Vijayamohanan, Surface-ruthenated tin oxide as a novel hydrocarbon sensor, Sens. Actuators A 65 (1998) 197–202. [3] K. Marcinkowska, M.P. McGauley, E.A. Symons, A new carbon monoxide sensor based on a hydrophobic CO oxidation catalyst, Sens. Actuators B 5 (1991) 91–96. [4] R. Sorita, T. Kawano, A highly selective CO sensor: screening of electrode materials, Sens. Actuators B 36 (1996) 274–277. [5] P. Millet, R. Durand, E. Dartyge, G. Tourillon, A. Fontaine, Precipitation of metallic platinum into Nafion ionomer membranes. I. Experimental results, J. Electrochem. Soc. 140 (1993) 1373–1380. [6] H. Yan, C.C. Liu, A solid polymer electrolyte-bases electrochemical carbon monoxide sensor, Sens. Actuators B 17 (1994) 165–168. [7] M.E. Tess, J.A. Cox, Humidity-independent solid-state amperometric sensor for carbon monoxide based on an electrolyte prepared by sol–gel chemistry, Anal. Chem. 70 (1998) 187–190. [8] N. Yamazoe, N. Miura, Development of gas sensors for environmentalprotection, IEEE Trans. Comp. Pack Manuf. Tech. A 18 (1995) 252–256. [9] S. Seal, S. Shukla, Nanocrystalline SnO gas sensors in view of surface reactions and modifications, JOM 54 (2002) 35. [10] F. Menil, V. Coillard, C. Lucat, Critical review of nitrogen monoxide sensors for exhaust gases of lean burn engines, Sens. Actuators B 67 (2000) 1–23. [11] S.B. Sinnott, Chemical functionalization of carbon nanotubes, J. Nanosci. Nanotech. 2 (2002) 113–123. [12] R.H. Baughman, A.A. Zakhidov, W.A. de Heer, Carbon nanotubes—the route toward applications, Science 297 (2002) 787–792. [13] A. Malinauskas, Electrocatalysis at conducting polymers, Synth. Met. 107 (1999) 75–83. [14] K.M. Manesh, P. Santhosh, A.I. Gopalan, K.-P. Lee, Electrocatalytic dioxygen reduction at glassy carbon electrode modified with polyaniline grafted multi-wall nanotube film, Electroanalysis 18 (2006) 1564–1571. [15] P. Santhosh, K.M. Manesh, A.I. Gopalan, K.-P. Lee, Enhanced electrocatalysis for the reduction of hydrogen peroxide at new multiwall carbon nanotube grafted polydiphenylamine modified electrode, Electroanalysis 18 (2006) 894–903. [16] P. Santhosh, K.M. Manesh, A. Gopalan, K.-P. Lee, Fabrication of a new polyaniline grafted multi-wall carbon nanotube modified electrode and its application for electrochemical detection of hydrogen peroxide, Anal. Chim. Acta 575 (2006) 32–38. [17] P. Santhosh, A. Gopalan, K.P. Lee, Gold nanoparticles dispersed polyaniline grafted multiwall carbon nanotubes as newer electrocatalysts:

P. Santhosh et al. / Sensors and Actuators B 125 (2007) 92–99

[18]

[19]

[20]

[21] [22]

[23]

[24]

[25]

[26]

[27]

[28]

preparation and performances for methanol oxidation, J. Catal. 238 (2006) 177–185. C. Chen, J. He, D. Xu, X. Tan, X. Zhou, X. Wang, Study of nano-Auassembled amperometric CO gas sensor, Sens. Actuators B 107 (2005) 866–871. M.T. Nguyen, R. Paynter, L.H. Dao, Polymerization and properties of poly(3-chlorodiphenylamine): a soluble electrochromic conducting polymer, Polymer 33 (1992) 214–216. M. Guo, J. Chen, J. Li, B. Tao, S. Yao, Fabrication of polyaniline/carbon nanotube composite modified electrode and its electrocatalytic property to the reduction of nitrite, Anal. Chim. Acta 532 (2005) 71–77. K.I. Tsceng, M.C. Yang, Platinum electrodes modified by tin for electrochemical CO sensors, J. Electrochem. Soc. 150 (2003) H156–H160. B.E.K. Swamy, M. Schell, An experimental and theoretical study of interactions between unlike surface anions and increases in the rate of electrochemical reactions, J. Phys. Chem. B 110 (2006) 5139– 5146. S.M. Golabi, A. Nozad, Electrocatalytic oxidation of methanol on electrodes modified by platinum microparticles dispersed into poly(ophenylenediamine) film, J. Electroanal. Chem. 521 (2002) 161–167. K.H. Xue, C.X. Cai, H. Yang, Y.M. Zhou, S.G. Sun, S.P. Chen, G. Xu, Electrocatalysis and related factors of platinum microparticles dispersed on/in polypyrrole film in methanol oxidation, J. Power Sources 75 (1998) 207–213. M. Liu, Z. Wu, Significance of interfaces in solid-state cells with porous electrodes of mixed ionic-electronic conductors, Solid State Ionics 107 (1998) 105–110. Z. Lukacs, M. Sinz, G. Staikov, W.J. Lorenz, G. Baier, A. Vogel, Electrochemical investigations of a carbon monoxide-oxygen sensor, Solid State Ionics 68 (1994) 105–110. N.L. Robertson, J.N. Michaels, Double layer capacitance of porous platinum electrodes in zirconia electrochemical cells, J. Electrochem. Soc. 138 (1991) 1494–1499. P.L. Kebabian, A. Freedman, Fluoropolymer-based capacitive carbon dioxide sensor, Meas. Sci. Technol. 17 (2006) 703–710.

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Biographies Padmanabhan Santhosh graduated in 1999 from the National College, Trichy, India with MSc in chemistry. He completed his PhD degree at the Department of Industrial Chemistry, Alagappa University, Karaikudi, India in 2005. Currently, he is a postdoctoral fellow at Department of Chemistry Education, Kyungpook National University, Daegu, South Korea. His research interests include the chemical and electrochemical modification of carbon nanotubes and development of the modified carbon nanotubes for sensor applications. Kalayil Manian Manesh received his master degree in industrial chemistry specialized in electrochemistry from Alagappa University (India) in 2004. He is currently working for his Doctoral degree in Kyungpook National University, South Korea. His research field includes development of nanomaterials for device applications. Prof. Anantha Iyengar Gopalan has been working at Department of Industrial chemistry, Alagappa University, Karaikudi (India) since 1986. He received his Master degree in 1979 with specialization in Physical Chemistry and PhD from Madurai Kamaraj University, Madurai (India). He did postdoctoral work at National Cheng Kung University, Taiwan and was visiting researcher at Kyungpook National University, South Korea, Laurence Berkeley National Laboratory, USA, etc. He is recently focusing his research attention on interdisciplinary topics covering synthesis of conducting polymers, nanostructuring of materials, electrochemistry and device applications. Prof. Kwang-Pill Lee received his master degree in applied chemistry from Nagoya University in 1985, and doctoral degree in 1988 from Nagoya University, Japan. He started his career as associate professor in 1994 and currently a professor at Department of Chemistry Education, Kyungpook National University, South Korea. He did postdoctoral work at Japan Atomic Energy Research Institute and was principal researcher at Korea Research Institute of Standards and Science, South Korea, and was visiting researcher at Laurence Berkeley National Laboratory, USA, etc. His current research activities involve synthesis of nanomaterials and composites, nanofibers and applications of nanomaterials as sensor, battery, separation science, etc.

Novel amperometric carbon monoxide sensor based on ...

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