College of Environmental Science Engineering, Key Laboratory of Environmental Biology Pollution Control, Ministry of Education, Hunan University, Changsha, 410082, China.
South China Institute of Environmental Sciences, Ministry of Environmental Protection of PRC, Guangzhou, 510655, China.
Mikrochim Acta. 2018 Mar 3;185(3):207. doi: 10.1007/s00604-018-2689-6.
The authors describe a fluorometric assay for the determination of Hg(II). A naphthalimide derivative is used as a label for a thymine (T) rich ssDNA, and graphene oxide magnetized with FeO nanoparticles acts as a quencher and preconcentrators. In the absence of Hg(II), the labeled ssDNA does not separate from the magnetized graphene oxide. As a result, fluorescence is fully quenched. In the presence of Hg(II), a T-Hg(II)-T link is formed dues to the highly affinity between T and Hg(II). Hence, fluorescence is restored. The assay has a linear response in the 1.0 to 10.0 nM Hg(II) concentration range, and a 0.65 nM detection limit. The method is selective and sensitive. It was applied to the analysis of spiked environmental water samples, and data agreed well with those obtained by atomic fluorescence spectrometry. Graphical abstract Strategy of a fluorescent probe for detecting Hg(II). The method has a 0.65 nM detection limit and is selective. MGO: magnetized graphene oxide, AHN: a fluorescent derivative of naphthalimide.
作者描述了一种用于测定 Hg(II) 的荧光测定法。萘酰亚胺衍生物被用作富含胸腺嘧啶 (T) 的 ssDNA 的标记物,而用 FeO 纳米粒子磁化的氧化石墨烯则作为猝灭剂和预浓缩剂。在没有 Hg(II) 的情况下,标记的 ssDNA 不会与磁化的氧化石墨烯分离。结果,荧光被完全猝灭。在存在 Hg(II) 的情况下,由于 T 与 Hg(II) 之间的高亲和力,形成了 T-Hg(II)-T 键。因此,荧光恢复。该测定法在 1.0 至 10.0 nM Hg(II)浓度范围内具有线性响应,检测限为 0.65 nM。该方法具有选择性和灵敏度。它被应用于加标环境水样的分析,所得数据与原子荧光光谱法获得的数据吻合良好。