Microdroplet anodic stripping voltammetry at the in situ preparing antimony-modified rotating disk electrode for determination of Cd(II) and Pb(II)

被引:3
作者
Huo, Ranran [1 ]
Liu, Lin [1 ]
Chanthasa, Chanika [1 ,2 ]
Okazaki, Takuya [1 ,3 ]
Sazawa, Kazuto [1 ]
Sugawara, Kazuharu [4 ]
Kuramitz, Hideki [1 ,5 ]
机构
[1] Univ Toyama, Grad Sch Sci & Engn Res, Dept Environm Biol & Chem, Toyama, Japan
[2] Silpakorn Univ, Fac Anim Sci & Agr Technol, Phetchaburi, Thailand
[3] Meiji Univ, Sch Sci & Technol, Dept Appl Chem, Kawasaki, Kanagawa, Japan
[4] Maebashi Inst Technol, Maebashi, Gunma, Japan
[5] Univ Toyama, Grad Sch Sci & Engn Res, Dept Environm Biol & Chem, Gofuku 3190, Toyama 9308555, Japan
基金
日本学术振兴会;
关键词
1-(2-pyridylazo)-2-naphthol; antimony-modified rotating disk electrode (Sb-RDE); microdroplet anodic stripping voltammetry; preconcentration using membrane filter; BISMUTH-FILM ELECTRODES; SOLUBLE MEMBRANE-FILTER; TRACE-METALS; SPECTROPHOTOMETRIC DETERMINATION; SPECTROMETRIC DETERMINATION; HEAVY-METALS; PRECONCENTRATION; WATER; SOLUBILIZATION; IONS;
D O I
10.1002/elan.202200528
中图分类号
O65 [分析化学];
学科分类号
070302 ; 081704 ;
摘要
A simple electroanalytical method for Cd(II) and Pb(II) detection based on differential pulse anodic stripping voltammetry (DPSV) with in situ prepared antimony-modified glassy carbon rotating disk electrode (in situ Sb-GC-RDE) was developed. The electrochemical detection was performed in a microdroplet (50 mu L) of 0.01 M hydrochloric acid that is placed between the electrode surface (top) and a Parafilm (R)-covered glass slide to maintain a hydrophobic surface (bottom). This method includes a preconcentration process using a membrane filter (MF). The target metal ions were complexed with 1-(2-pyridylazo)-2-naphthol (PAN) as a chelating agent, which was accumulated on the MF via filtration. The RDE microdroplet anodic stripping voltammetry was suitable for the elution and determination of metal ions accumulated on the MF. The in situ preparation of antimony-modified electrode allows the use of common GC electrode with high performance. The detection limits for Cd(II) and Pb(II) were 1.4 and 1.1 mu g/L, respectively. The proposed method was successfully used in natural water samples for the simultaneous determination of Cd(II) and Pb(II).
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页数:7
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