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1.延安大学 化学与化工学院, 延安市分析技术与检测重点实验室, 陕西 延安 716000
2.中材地质工程勘查研究院有限公司, 北京 100102
3.延安大学 医学院, 陕西 延安 716000
[ "张越诚(1990-),男,陕西西安人,博士,讲师,硕士生导师,2021年于瑞典Malmö University获得博士学位,主要从事生化分析与分子诊断方面的 研究。 E-mail: YuechengZhang@outlook.com" ]
[ "王清清(1998-),女,陕西西安人,硕士研究生,2019年于宝鸡文理学院获得学士学位,主要从事发光分析的研究。E⁃mail: qqwangcrystal@163.com" ]
[ "马红燕(1966-),女,陕西延安人,硕士,教授,硕士生导师,2004年于陕西师范大学获得硕士学位,主要从事发光分析的研究。 E-mail: Mahy6614@163.com" ]
收稿日期:2022-09-22,
修回日期:2022-10-11,
纸质出版日期:2023-04-05
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张越诚,王清清,马静等.环境水样中S2-的CQDs双发射比率荧光测定[J].发光学报,2023,44(04):729-737.
ZHANG Yuecheng,WANG Qingqing,MA Jing,et al.Determination of S2- in Environmental Water Samples Using Dual-emission CQDs as Ratio Fluorescent Probe[J].Chinese Journal of Luminescence,2023,44(04):729-737.
张越诚,王清清,马静等.环境水样中S2-的CQDs双发射比率荧光测定[J].发光学报,2023,44(04):729-737. DOI: 10.37188/CJL.20220339.
ZHANG Yuecheng,WANG Qingqing,MA Jing,et al.Determination of S2- in Environmental Water Samples Using Dual-emission CQDs as Ratio Fluorescent Probe[J].Chinese Journal of Luminescence,2023,44(04):729-737. DOI: 10.37188/CJL.20220339.
以葡萄糖为碳源、对苯二胺为氮源,一步水热法合成了新型双发射荧光碳量子点(GP⁃CQDs),对该GP⁃CQDs的形貌及光谱特性进行了研究。实验发现,在单一波长
λ
ex
=300 nm激发下,该GP⁃CQDs于348 nm和452 nm处有双发射荧光信号。将MnO
4
-
加入GP⁃CQDs溶液,GP⁃CQDs于452 nm处的荧光信号完全猝灭,而348 nm处的信号基本不变。于上述猝灭体系中继续加入S
2-
,其于425 nm处产生新的荧光发射峰,相较于GP⁃CQDs原452 nm处的荧光信号,发射峰位置发生蓝移,且发射峰强度随S
2-
的浓度增加线性增强,而348 nm处的信号无增敏现象。根据该现象,以425 nm处的荧光峰为响应信号、348 nm荧光峰为参比信号,可直接构建基于S
2-
测定的比率荧光传感探针。实验对该探针的构建条件及分析性能进行了优化,当S
2-
浓度在3.1×10
-8
~ 8.0×10
-6
mol/L范围内时,与348 nm和425 nm两处的荧光强度比值(
I
425
/
I
348
)呈现良好的线性关系,检出限为9.41×10
-9
mol/L(3
σ
/
k
)。对MnO
4
-
及S
2-
与GP⁃CQDs的作用机理进行了探讨。该方法简单、快速、灵敏度高,用于环境水样中S
2-
的测定,结果满意。
Dual-emission fluorescence carbon quantum dots (GP-CQDs) were synthesized by a one-step hydrothermal method using glucose and p-phenylenediamine as carbon sources. The morphology and spectral properties of GP-CQDs were studied. It was found that the GP-CQDs have dual emission fluorescence signals at 348 nm and 452 nm under a single excitation wavelength at 300 nm. When MnO
4
-
was added to the GP-CQDs solution, the fluorescence signal of GP-CQDs at 452 nm was completely quenched; however, the signals at 348 nm kept stable. When S
2-
was added to the quenching system above, a new fluorescence emission peak was generated at 425 nm. Compared with the original fluorescence peak at 452 nm, the peak was blue-shifted, and the fluorescence intensity at 425 nm was linearly enhanced with the S
2-
concentration. With the fluorescence peak at 425 nm as the response signal and the 348 nm fluorescence peak as the reference signal, a ratiometric fluorescence sensing probe for S
2-
determination can be directly constructed. Under the optimal condition, this method showed a good linear relationship in the range of 3.1×10
-8
-8.0×10
-6
mol/L and the detection limit was calculated to be 9.41×10
-9
mol/L(3
σ
/
k
). The basic mechanism of the proposed method was further discussed. Moreover, this method can be applied to detect S
2-
in environmental water samples with satisfactory results.
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