Key Laboratory of Photochemical Biomaterials and Energy Storage Materials, Heilongjiang Province and College of Chemistry and Chemical Engineering, Harbin Normal University, Harbin, 150025, People's Republic of China.
Key Laboratory of Polyoxometalate Science of Ministry of Education Institution, Northeast Normal University, Changchun, 130024, People's Republic of China.
Mikrochim Acta. 2019 Jun 14;186(7):451. doi: 10.1007/s00604-019-3522-6.
The first example of metallic bismuth encapsulated into a mesoporous metal-organic framework of the type MIL-101(Cr) matrix is presented. Bi(III)-impregnated MIL-101(Cr) (Bi(III)/MIL-101(Cr)) was dropped onto a conductive carbon cloth electrode (CCE). Then, bismuth was generated by electrochemical reduction of the Bi(III)/MIL-101(Cr) supported on CCE (Bi/MIL-101(Cr)/CCE). The resulting Bi/MIL-101(Cr)/CCE display impressive performance in terms of peak currents for the ions Cd(II) and Pb(II) when compared to the single-component counterparts. Differential pulse anodic stripping voltammetry (DPASV) enabled sensing of the two ions over linear working range of 0.1 to 30 μg L and 30 to 90 μg L. The parameters are refined before the detection of two metal ions, including the amount of bismuth in MIL-101(Cr), optimum pH (5.0), deposition potential (-1.2 V) and deposition time (600 s). The respective detection limits are 60 and 70 ng L (at S/N = 3). This is strikingly lower than the guideline values of domestic water given by the WHO which are 3 μg L for Cd(II) and 10 μg L for Pb(II). The Bi/MIL-101(Cr) onto CCE is fairly specific for Cd(II) (at around -0.76 V) and Pb(II) (at around -0.54 V), well reproducible and has excellent recovery in real water analysis. Graphical abstract Schematic illustration of the preparation of a Bi(III)/MIL-101(Cr) metal-organic framework, its deposition on a carbon cloth electrode (CCE), and its application for detection of Cd(II) and Pb(II) by differential pulse adsorptive stripping voltammetry (DPASV).
首次将三价铋封装到 MIL-101(Cr) 介孔金属有机骨架基质中。将三价铋浸渍的 MIL-101(Cr)(Bi(III)/MIL-101(Cr))滴加到导电碳纤维布电极(CCE)上。然后,通过电化学还原负载在 CCE 上的 Bi(III)/MIL-101(Cr)(Bi/MIL-101(Cr)/CCE)生成铋。与单一组分相比,所得的 Bi/MIL-101(Cr)/CCE 在 Cd(II)和 Pb(II)离子的峰电流方面表现出令人印象深刻的性能。差分脉冲阳极溶出伏安法(DPASV)使能够在 0.1 至 30μg L 和 30 至 90μg L 的线性工作范围内检测两种离子。在检测两种金属离子之前,对参数进行了优化,包括 MIL-101(Cr)中的铋含量、最佳 pH 值(5.0)、沉积电位(-1.2 V)和沉积时间(600 s)。相应的检测限分别为 60 和 70 ng L(在 S/N = 3 时)。这明显低于世界卫生组织给出的国内饮用水指导值,Cd(II)为 3μg L,Pb(II)为 10μg L。负载在 CCE 上的 Bi/MIL-101(Cr) 对 Cd(II)(约-0.76 V)和 Pb(II)(约-0.54 V)具有相当的特异性,重现性好,在实际水样分析中具有良好的回收率。