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Poster Session, Tuesday, June 15<br />

Theme A1 - B702<br />

Multiwalled carbon nanotube modified with 5-Br-PADAP for stripp<strong>in</strong>g voltammetric<br />

determ<strong>in</strong>ation of Pb(II)<br />

Ashraf Salmanipour, 1 Mohammad Ali Taher 1 and Alireza Mohadesi 2*<br />

1<br />

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

2<br />

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

Abstract— In this work, we have demonstrated that glassy carbon electrode (GCE) modified with multiwalled carbon<br />

nanotube (MWNT) functionalized with 2-(5-bromo-2-pyridylazo)-5-diethylam<strong>in</strong>ophenol (5-Br-PADAP) as a ligand can be<br />

used for the stripp<strong>in</strong>g voltammetry of lead(II). The ability of the 5-Br-PADAP to extract Pb(II) <strong>in</strong>to the electrode surface leads<br />

to an electrochemical sensor that is precise and accurate for determ<strong>in</strong>ation of lead(II) <strong>in</strong> water samples.<br />

Adsorptive stripp<strong>in</strong>g voltammetry generally applies an<br />

accumulation step prior to the voltammetric scan <strong>in</strong> order to<br />

develop analysis methods with higher levels of sensitivity. In<br />

this step, analyte (metal ion) is adsorbed from sample solution<br />

to electrode surface based on complexation between metal ion<br />

and ligand immobilized on the electrode surface. In this sense,<br />

ow<strong>in</strong>g to the strong sorption properties of carbon nanotubes<br />

and their 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 [1-4].<br />

In this work, the MWNT functionalized with a complex<br />

reagent (5-Br-PADAP) was prepared and coated on a GCE.<br />

This modified electrode was used successfully for anodic<br />

stripp<strong>in</strong>g determ<strong>in</strong>ation of lead(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 [5]. After these<br />

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

the cross sections of the MWNTs. For preparation of 5-Br-<br />

PADAP-functionalized MWNT, the 5-Br-PADAP dissolved<br />

<strong>in</strong> ethanol was added to 1 g of pretreated MWNT, step by step<br />

and the solution was stirred for 24 hour till the solution<br />

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

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

temperature. Then ultrasonication agitation for 20 m<strong>in</strong> was<br />

applied to disperse 0.5 mg 5-Br-PADAP/MWNT <strong>in</strong>to 1 ml of<br />

double distilled water to give 0.5 mg/ml suspension. Before<br />

coat<strong>in</strong>g, the GCE was polished with a nano-Al 2 O 3 powder on a<br />

polish<strong>in</strong>g pad r<strong>in</strong>sed thoroughly with doubly distilled water,<br />

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

coated with 10 μL of 0.5 mg/ml 5-Br-PADAP/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) or cyclic stripp<strong>in</strong>g<br />

voltammetric experiments, the 5-Br-PADAP/MWNT/GCE<br />

was immersed <strong>in</strong> a 25 ml of sample solution (0.1 M acetate<br />

buffer pH 5.58) conta<strong>in</strong><strong>in</strong>g a known amount of Pb(II) and the<br />

solution was stirred for 15 m<strong>in</strong>. This was followed by medium<br />

exchange to a 0.1 M stripp<strong>in</strong>g solution (0.1 M KNO 3 , 0.1 M<br />

acetate buffer pH 4.23), where the DPA or cyclic<br />

voltammograms were recorded from -1.0 to -0.2 V.<br />

Figure 1a shows typical cyclic voltammogram for the<br />

detection of Pb 2+ follow<strong>in</strong>g open-circuit accumulation onto 5-<br />

Br-PADAP/MWNT film. An anodic peak at -0.55 V can be<br />

observed, which is related to the oxidation of accumulated<br />

lead(II). To prove further the importance of 5-Br-PADAP as a<br />

chelator reagent <strong>in</strong> the electrode surface, GC electrode<br />

modified with MWNT without 5-Br-PADAP were prepared,<br />

and used for the accumulation and stripp<strong>in</strong>g of Pb 2+ . Figure 1c<br />

shows no significant peak, as expected, <strong>in</strong> the case of<br />

unmodified MWNT. These results show the importance of<br />

modification of MWNT with 5-Br-PADAP for the<br />

preconcentration of Pb 2+ .<br />

From the above observations, under the conditions of the<br />

experiments, the possible pathways for the analysis cycle,<br />

from modification of MWNT to stripp<strong>in</strong>g voltammetry, are<br />

postulated below ("sol", or "surf" subscript means compound<br />

is <strong>in</strong> solution or electrode surface):<br />

Modification of pretreated-MWNT with 5-Br-PADAP:<br />

reflux<br />

MWNT + 5 − Br − PADAP( sol )<br />

⎯⎯⎯<br />

→ 5 − Br − PADAP / MWNT<br />

Accumulation of Pb 2+ from acetate buffer solution:<br />

Pb<br />

2+<br />

(<br />

sol<br />

)<br />

+<br />

open circuit 2+<br />

[ 5 − Br − PADAP / MWNT ](<br />

surf )<br />

⎯⎯ ⎯⎯→<br />

[ Pb / 5 − Br − PADAP / MWNT ](<br />

surf<br />

Reduction of accumulated Pb 2+ <strong>in</strong> clean acetate buffer:<br />

2+<br />

<strong>in</strong> more negative than −0.7V<br />

0<br />

[ Pb / 5 − Br − PADAP / MWNT]<br />

( surf )<br />

+ 2e<br />

⎯⎯⎯⎯⎯⎯⎯⎯→<br />

Pb(<br />

surf )<br />

+ [5 − Br − PADAP / MWNT]<br />

( surf<br />

Stripp<strong>in</strong>g of reduced lead <strong>in</strong> clean acetate buffer:<br />

Pb<br />

⎯⎯⎯⎯⎯⎯⎯→Pb<br />

0 Scan from −1.0<br />

to −0.2V<br />

2+<br />

( surf )<br />

( surf )<br />

Figure 1. Cyclic (50 mV/s) voltammograms <strong>in</strong> acetate buffer pH 4.23 after<br />

open circuit accumulation (15 m<strong>in</strong>) <strong>in</strong> acetate buffer pH 5.58: (a) 5-Br-<br />

PADAP/MWNT/GCE, with 100 μg L -1 Pb(II) <strong>in</strong> accumulation medium, (b) 5-<br />

Br-PADAP/MWNT/GCE, no Pb(II) <strong>in</strong> accumulation medium, (c)<br />

MWNT/GCE, with 100 μg L -1 Pb(II) <strong>in</strong> accumulation medium and (d)<br />

MWNT/GCE, no Pb(II) <strong>in</strong> accumulation medium.<br />

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

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

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

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

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

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

)<br />

)<br />

6th Nanoscience and Nanotechnology Conference, zmir, 2010 365

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