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使用加速溶剂萃取-同位素稀释-高分辨率气相色谱-高分辨率质谱法测定生物样品中的82种多氯联苯

[Determination of 82 polychlorinated biphenyls in biological samples using accelerated solvent extraction-isotope dilution-high resolution gas chromatography-high resolution mass spectrometry].

作者信息

Wu Yinju, Qu Bailu, Hou Yulan, Yu Haibin, Xu Renji, Zheng Xiaoyan

机构信息

China National Environmental Monitoring Centre, Beijing 100012, China;Hunan Changsha Eco-Environment Monitoring Center, Changsha 410000, China.

Hunan Changsha Eco-Environment Monitoring Center, Changsha 410000, China.

出版信息

Se Pu. 2022 May 8;40(5):452-460. doi: 10.3724/SP.J.1123.2021.10018.

Abstract

In China, the detection methods for polychlorinated biphenyls (PCBs) in aquatic products are mainly effective for 6 indicative PCBs and 12 coplanar dioxin-like PCBs, which only account for a limited proportion of PCBs in organisms. In this study, to obtain the detailed concentration levels of PCBs in organisms, elucidate the metabolism and enrichment characteristics of PCBs in organisms, and accurately evaluate the exposure level and risks of PCBs to humans, an improved method for the simultaneous determination of 82 PCBs in fish and shellfish samples was developed using isotope dilution-high resolution gas chromatography-high resolution mass spectrometry (ID-HRGC-HRMS). The recovery and reproducibility of two extraction methods, i. e., oscillatory extraction and accelerated solvent extraction (ASE), were compared. Finally, ASE was chosen for subsequent experiments. Specifically, after adding 1 ngC-labeled extraction internal standards, the samples were extracted under pressure by ASE using a mixture of -hexane-dichloromethane (1∶1, v/v). The experimental conditions employed for this were a pressure of 10.3 MPa, heating temperature of 100 ℃, heating time of 5 min, static time of 8 min, flush volume of 60%, purging time of 120 s, and 34 mL cells. Subsequently, the extracts were loaded on an 8 g acid silica gel (44%) column (inner diameter: 15 mm) and eluted with 90 mL of -hexane. After purification and concentration, the analytes were determined by HRGC-HRMS with a fused-silica capillary column (DB-5MS, 60 m×0.25 mm×0.25 μm). The temperature program was optimized to separate the most target compounds at the baseline. Specifically, the initial oven temperature was 120 ℃, which was held for 1 min, following by heating to 180 ℃ at 30 ℃/min, heating to 210 ℃ at 2 ℃/min and holding for 1 min, and further heating to 310 ℃ at 2.5 ℃/min and holding for 1 min. The injector and ion source temperatures were 270 ℃ and 280 ℃, respectively. With a static resolution of 10000, the HRMS instrument was operated in the selected-ion monitoring mode at an electron energy of 35 eV. The 82 PCBs were qualified by their retention time and two characteristic ions, and thereafter quantified using the mean relative corresponding factor (RRF). The results showed that the relative standard deviation (RSD) of the RRF obtained from six-point calibration standard solutions was less than 20%. The linearity ranges were from 0.1 to 200 μg/L, and the correlation coefficients () were greater than 0.99. Under optimum conditions, the method detection limits (MDLs) for the PCBs of biological samples were in the range of 0.02-3 pg/g. To validate the method, the fish and shellfish samples were spiked with a low level (0.4 ng) and high level (3.6 ng) of native PCB standards. The spiked recoveries using low-concentration native PCBs were 71.3%-139% in fish and 76.9%-143% in shellfish, and the RSDs (=7) were 2.1%-14% and 4.5%-14%, respectively. The spiked recoveries using high-concentration native PCBs were 77.6%-141% and 82.2%-131%, respectively, and the RSDs (=7) were 1.4%-9.4% and 1.7%-11%, respectively. An analysis of fresh fish and shellfish samples showed that the contents of a single PCB ranged from "not detected" to 54.1 pg/g, where 12 coplanar dioxin-like PCBs were detected in the range of 12.6 pg/g to 74.5 pg/g, six indicative PCBs in the range of 30.9 pg/g to 62.1 pg/g, and 82 PCBs in the range of 174 pg/g to 672 pg/g. It was concluded that this method could be successfully applied for the determination of PCBs in biological samples with good accuracy and precision. This comprehensive analytical method of PCBs in aquatic products provides effective technical support for biological monitoring; it will also aid in ecological and environmental management and the implementation of the Stockholm Convention policies.

摘要

在中国,水产品中多氯联苯(PCBs)的检测方法主要针对6种指示性PCBs和12种共面二噁英类PCBs,而这些仅占生物体中PCBs的有限比例。在本研究中,为了获取生物体中PCBs的详细浓度水平,阐明PCBs在生物体中的代谢和富集特征,并准确评估PCBs对人类的暴露水平和风险,采用同位素稀释-高分辨率气相色谱-高分辨率质谱法(ID-HRGC-HRMS)建立了一种同时测定鱼和贝类样品中82种PCBs的改进方法。比较了振荡萃取和加速溶剂萃取(ASE)这两种萃取方法的回收率和重现性。最终选择ASE用于后续实验。具体而言,加入1 ng C标记的萃取内标后,样品用正己烷-二氯甲烷(1∶1,v/v)混合溶剂通过ASE在压力下萃取。实验条件为压力10.3 MPa、加热温度100℃、加热时间5 min、静态时间8 min、冲洗体积60%、吹扫时间120 s以及34 mL萃取池。随后,将萃取液加载到8 g酸性硅胶(44%)柱(内径:15 mm)上,并用90 mL正己烷洗脱。经过净化和浓缩后,采用带有熔融石英毛细管柱(DB-5MS,60 m×0.25 mm×0.25μm)的HRGC-HRMS对分析物进行测定。优化了温度程序以在基线水平分离大多数目标化合物。具体来说,初始柱温箱温度为120℃,保持1 min,随后以30℃/min升温至180℃,再以2℃/min升温至210℃并保持1 min,进一步以2.5℃/min升温至310℃并保持1 min。进样口和离子源温度分别为270℃和280℃。HRMS仪器在静态分辨率为10000的条件下,以35 eV电子能量在选择离子监测模式下运行。通过保留时间和两个特征离子对82种PCBs进行定性,然后使用平均相对响应因子(RRF)进行定量。结果表明,六点校准标准溶液得到的RRF的相对标准偏差(RSD)小于20%。线性范围为0.1至200μg/L,相关系数()大于0.99。在最佳条件下,生物样品中PCBs的方法检出限(MDLs)在0.02 - 3 pg/g范围内。为验证该方法,向鱼和贝类样品中添加低水平(0.4 ng)和高水平(3.6 ng)的天然PCB标准品。低浓度天然PCBs加标回收率在鱼中为71.3% - 139%,在贝类中为76.9% - 143%,RSD(=7)分别为2.1% - 14%和4.5% - 14%。高浓度天然PCBs加标回收率分别为77.6% - 141%和82.2% - 131%,RSD(=7)分别为1.4% - 9.4%和1.7% - 11%。对新鲜鱼和贝类样品的分析表明,单一PCB的含量范围为“未检出”至54.1 pg/g,其中12种共面二噁英类PCBs的检出范围为12.6 pg/g至74.5 pg/g,6种指示性PCBs的检出范围为30.9 pg/g至62.1 pg/g,82种PCBs的检出范围为174 pg/g至672 pg/g。得出结论,该方法可成功应用于生物样品中PCBs的测定,具有良好的准确性和精密度。这种水产品中PCBs的综合分析方法为生物监测提供了有效的技术支持;也将有助于生态和环境管理以及《斯德哥尔摩公约》政策的实施。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a42b/9404184/59066a59113f/cjc-40-05-452-img_1.jpg

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