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    基于纳米金-罗丹明B荧光猝灭效应的核酸适配体传感方法测定水体中雌二醇的含量

    Determination of Estradiol in Water Body by Aptamer Sensing Method Based on Gold Nanoparticles-Rhodamine B Fluorescence Quenching Effect

    • 摘要: 为实现水体中雌二醇的简单、快速、高灵敏定量检测,以核酸适配体为雌二醇的识别元件,罗丹明B为信号分子,基于纳米金对罗丹明B的荧光猝灭效应构建一种可定量检测水体中雌二醇的核酸适配体传感方法。采用柠檬酸三钠还原四氯金酸法合成纳米金溶液,在50 μL过滤后的湖水样品中加入纳米金溶液250 μL和10 μmol·L−1核酸适配体溶液50 μL,混匀,于25 ℃孵育20 min,然后加入1.00 mol·L−1氯化钠溶液125 μL和40 μmol·L−1罗丹明B溶液25 μL,混合均匀,补加水使溶液总体积达到500 μL,于25 ℃孵育5 min,在激发波长530 nm、发射波长574 nm下测量荧光强度差值∆F(试验组和空白组的荧光强度差值),并利用∆F与雌二醇浓度的线性关系进行定量检测。结果显示,该方法的线性范围为20~200 nmol·L−1,检出限(3s/k)为10 nmol·L−1。在湖水样品中添加20,50,100 nmol·L−1的雌二醇,回收率为87.0%~102%,测定值的相对标准偏差(n=5)为2.8%~4.9%。在荧光体系中加入干扰物质雌三醇、百菌清、4-羟基百菌清,体系的荧光强度变化不大。

       

      Abstract: To achieve simple, rapid, and highly sensitive quantitative detection of estradiol in water body, using aptamer as the recognition element for estradiol and Rhodamine B as the signal molecule, an aptamer sensing method for quantitative detection of estradiol in water body was developed based on the fluorescence quenching effect of gold nanoparticles on Rhodamine B. Gold nanoparticle solution was synthesized by the trisodium citrate reduction method using chloroauric acid. The 250 μL of gold nanoparticle solution and 50 μL of 10 μmol · L-1 aptamer solution were added into 50 μL of filtered lake water sample. After mixing well, the mixed solution was incubated at 25 ℃ for 20 min. Then, 125 μL of 1.00 mol · L-1 sodium chloride solution and 25 μL of 40 μmol · L-1 Rhodamine B solution were added. The mixed solution was mixed thoroughly, the volume of which was supplemented to 500 μL with water. After incubating for 5 min at 25 ℃, the fluorescence intensity difference ΔF(the difference between the test group and the blank group) was measured at an emission wavelength of 574 nm under an excitation wavelength of 530 nm. Quantitative detection was performed using the linear relationship between ΔF and estradiol concentration. It was shown that the linear range of this method was 20-200 nmol · L-1, with detection limit (3s/k) of 10 nmol · L-1. For lake water samples spiked with 20, 50, 100 nmol · L-1 of estradiol, the recoveries were found in the range of 87.0%-102%, giving RSDs (n=5) of the determined values in the range of 2.8%-4.9%. In the fluorescence system, the addition of interfering substances (estriol, chlorothalonil, and 4-hydroxychlorothalonil) resulted in minimal changes in fluorescence intensity.

       

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