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Photonic crystals in biology

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Poster Session, Tuesday, June 15<br />

Theme A1 - B702<br />

An electrochemical sensor for stripp<strong>in</strong>g voltammetric determ<strong>in</strong>ation of cadmium (II) based on<br />

multiwalled carbon nanotube functionalized with 1-(2-pyridylazo)-2-naphthol<br />

Alireza Mohadesi, 1* Zahra Motallebi 1 and Ashraf Salmanipour 2<br />

1<br />

Department of Chemistry, Payame Noor University (PNU), P.O. Box 76175-559, Kerman, Iran<br />

2<br />

Department of Chemistry, Shahid Bahonar University of Kerman, P.O. Box 76175-133, Kerman, Iran<br />

Abstract— The present work has focused on the modification of multiwalled carbon nanotube with a ligand, 1-(2-pyridylazo)-<br />

2-naphthol (PAN), and its potential application for the development of a new, simple and selective modified glassy carbon<br />

electrode for stripp<strong>in</strong>g voltammetric determ<strong>in</strong>ation of Cd(II). this method demonstrates the powerful application of carbon<br />

nanotubes <strong>in</strong> the field of mercury-free electrodes <strong>in</strong> voltammetric stripp<strong>in</strong>g analysis.<br />

Traditional work<strong>in</strong>g electrodes for voltammetric<br />

determ<strong>in</strong>ation were generally based on a hang<strong>in</strong>g drop<br />

mercury electrode and a mercury film electrode. However, the<br />

toxicity of the Hg and its precursors make these materials<br />

undesirable for disposable <strong>in</strong> situ sens<strong>in</strong>g applications.<br />

Therefore, various chemically modified electrodes as mercuryfree<br />

electrodes are applied for adsorptive stripp<strong>in</strong>g<br />

voltammetry of heavy metal ions [1-3]. Adsorptive stripp<strong>in</strong>g<br />

voltammetry generally applies an accumulation step prior to<br />

the voltammetric scan <strong>in</strong> order to develop analysis methods<br />

with higher levels of sensitivity. In this step, analyte (metal<br />

ion) is adsorbed from sample solution to electrode surface<br />

based on complexation between metal ion and ligand<br />

immobilized on the electrode surface. In this sense, ow<strong>in</strong>g to<br />

the strong sorption properties of carbon nanotubes and their<br />

advantages <strong>in</strong> electrochemical measurements, this<br />

nanostructured material has allowed some novel methods of<br />

stripp<strong>in</strong>g analysis to be developed [1-6].<br />

In this work, the multiwalled carbon nanotube (MWNT)<br />

functionalized with a complex reagent (PAN) was prepared<br />

and coated on a glassy carbon electrode (GCE). This modified<br />

electrode was used successfully for anodic stripp<strong>in</strong>g<br />

determ<strong>in</strong>ation of Cd(II) <strong>in</strong> some real samples.<br />

Before use, the MWNTs were purified and pretreated to<br />

remove graphitic nanoparticles, amorphous carbon, and<br />

catalyst impurities, and then functionalized with carboxylic<br />

acid groups accord<strong>in</strong>g to the literature [7]. After these<br />

procedures, the carboxylic acid groups were <strong>in</strong>troduced onto<br />

the cross sections of the MWNTs. For preparation of PANfunctionalized<br />

MWNT, the PAN dissolved <strong>in</strong> ethanol was<br />

added to 1g of pretreated MWNT, step by step and the<br />

solution was stirred for 12 hour till the solution became<br />

colorless. Then the modified MWNTs were filtered and<br />

washed with doubly distilled water and got dried at room<br />

temperature. Then ultrasonication agitation for 30 m<strong>in</strong> was<br />

applied to disperse 2.0 mg PAN/MWNT <strong>in</strong>to 1 ml of double<br />

distilled water to give 2.0 mg/ml suspension. Before coat<strong>in</strong>g,<br />

the GCE was polished with a nano-Al 2 O 3 powder (Fluka) on a<br />

polish<strong>in</strong>g pad (Metrohm) r<strong>in</strong>sed thoroughly with doubly<br />

distilled water, then sonicated <strong>in</strong> aceton for 2 m<strong>in</strong>. F<strong>in</strong>ally, the<br />

GCE was coated with 5 μL of 2.0 mg/ml PAN/MWNT<br />

suspension and the water allowed evaporat<strong>in</strong>g at room<br />

temperature <strong>in</strong> the air. The bare electrode was prepared by the<br />

same procedure just with unfunctionalized MWNTs.<br />

For differential pulse anodic (DPA) stripp<strong>in</strong>g voltammetric<br />

experiments, the modified GCE was immersed <strong>in</strong> a 25 ml<br />

solution of 0.1 M oxalate buffer pH 3.0 conta<strong>in</strong><strong>in</strong>g a known<br />

amount of Cd(II) and a potential of -1.0 V was then applied<br />

for 100 seconds (while stirrer was on, 600 rpm). F<strong>in</strong>ally the<br />

DPA stripp<strong>in</strong>g voltammogram was recorded (with 20 mV s−1<br />

scan rate, 100 mV pulse amplitude, and 4 ms pulse period).<br />

The scan was term<strong>in</strong>ated at -0.4 V. All measurements were<br />

carried out at room temperature (22 ± 1 °C).<br />

Figure 1a shows typical DPA for the detection of Cd 2+<br />

follow<strong>in</strong>g closed-circuit accumulation onto PAN/MWNT film.<br />

An anodic peak at -0.59 V can be observed, which is related to<br />

the oxidation of accumulated and reduced Cadmium(II). To<br />

prove further the importance of PAN as a chelator reagent <strong>in</strong><br />

the electrode surface, GCE modified with MWNT without<br />

PAN were prepared, and used for the accumulation and<br />

stripp<strong>in</strong>g of Cd 2+ . Figure 1c shows no significant peak, as<br />

expected, <strong>in</strong> the case of unmodified MWNT. These results<br />

show the importance of modification of MWNT with PAN for<br />

the preconcentration of Cd 2+ .<br />

Figure 1: DPA (20 mV/s) voltammograms <strong>in</strong> oxalate buffer pH 3.0 after<br />

closed circuit accumulation (150 s at -0.9 V): (a) PAN/MWNT/GCE, with 50<br />

μg L -1 Cd(II) <strong>in</strong> solution, (b) PAN/MWNT/GCE, no Cd(II) <strong>in</strong> solution, (c)<br />

MWNT/GCE, with 50 μg L -1 Cd(II) <strong>in</strong> solution and (d) MWNT/GCE, no<br />

Cd(II) <strong>in</strong> solution.<br />

*Correspond<strong>in</strong>g author: mohadesi_a@yahoo.com<br />

[1] D. Sun et al, J Appl Electrochem 381223–1227 (2008)<br />

[2] W. Yantasee et al., Environ. Health Perspect. 115 1683-1690 (2007)<br />

[3] G.H. Hwang et al., Talanta 76 301–308 (2008)<br />

[4] K. Wu et al., Anal. Chim. Acta 489 215–221 (2003)<br />

[5] H. Xu et al., Electroanalysis 20 2655 – 2662 (2008)<br />

[6] L. Zhu et al., Electroanalysis 20 527 – 533 (2008)<br />

[7] X. Tan et al., Anal. Biochem. 337 111 (2005)<br />

6th Nanoscience and Nanotechnology Conference, zmir, 2010 366

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