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磁性固相萃取-液相色谱-质谱法测定环境水样中的全氟化合物及相关风险评估

[Determination of perfluorinated compounds in environmental water samples by magnetic solid-phase extraction-liquid chromatography-mass spectrometry and associated risk assessment].

作者信息

Gu Chen-Shu, Liu Zhen-Zhen, Jin Hui-Ling, Liu Xiao-Qi, Wang Mei-Yu, Sun Wei-Jie, Sun Yang-Ying, Qi Pei-Pei

机构信息

State Key Laboratory for Managing Biotic and Chemical Threats to the Quality and Safety of Agro-products,School of Food Science and Engineering,Ningbo University,Ningbo 315211 China.

State Key Laboratory for Managing Biotic and Chemical Threats to the Quality and Safety of Agro-products,Institute of Agro-product Safety and Nutrition,Zhejiang Academy of Agricultural Sciences,Hangzhou 310021,China.

出版信息

Se Pu. 2025 Jun;43(6):650-658. doi: 10.3724/SP.J.1123.2024.08015.

DOI:10.3724/SP.J.1123.2024.08015
PMID:40394744
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC12093205/
Abstract

Perfluorinated compounds (PFCs) are widely used, persistent, and their presence in water is of significant concern. PFCs, particularly short-chain variants, are highly soluble and mobile in water, which enables their transport over long distances via river systems, potentially leading to extensive contamination. These compounds are resistant to degradation, which is challenging for conventional water-treatment methods that often remove PFCs ineffectively, leading to their prolonged presence in water bodies. This paper establishes a magnetic solid-phase extraction method for 11 PFCs in enriched water using magnetic polystyrene pyrrolidone (FeO-PLS) as a magnetic adsorbent. Purified lipophilic PLS magnetic beads were used as the solid-phase extractant, and their surfaces were modified using phenyl and pyrrolidone groups to facilitate the adsorption of PFCs that contain hydrophilic functional groups and hydrophobic alkyl side chains. PFCs in water were determined accurately and sensitively by liquid chromatography-tandem mass spectrometry (LC-MS/MS). The method involved accurately weighing 50 mg (±0.05 mg) of the FeO-PLS into a 500-mL beaker, adding 2 mL of methanol (for activation), placing the beaker on a magnet for 30 s, and discarding the methanol once the methanol and FeO-PLS had been completely separated. A 200-mL aliquot of an aqueous mixed PFC solution was added to the beaker, sonicated for 15 min, and then placed on a strong magnet until the FeO-PLS had completely separated at the bottom of the beaker. The upper liquid was discarded. A 4-mL acetonitrile containing 0.1% formic acid was added as the FeO-PLS eluent, ultrasonicated for 30 s, after which the beaker was placed on the magnet and the eluate collected. The sample was taken to dryness under a stream of nitrogen, the residue was redissolved in 0.5 mL of acetonitrile, ultrasonicated for 10 s, and then membrane-filtered prior to analysis by LC-MS/MS. The 11 PFCs exhibited good linear relationships ranging from 1 to100 μg/L, with correlation coefficients () ranging from 0.997 6 to 0.999 9. Limits of detection and quantification (LODs and LOQs, respectively) were determined to be 0.001-0.620 ng/L and 0.002-2.065 ng/L, respectively, indicative of high sensitivity. The 11 PFCs exhibited recoveries of 60.8%-120.0% at various concentrations (0.05, 1, 10, and 50 μg/L). Relative standard deviations (RSDs) ranged from 1.0% to 20.0%, which meet the requirements for PFC analysis in water. The concentrations of the 11 PFCs at 15 sites in the Dongtiaoxi River, Hangzhou (near factories, reservoirs and residential areas) were analyzed using the developed method. A total of six PFCs, namely perfluorooctanoic acid (PFOA), perfluorononanoic acid (PFNA), perfluorooctane sulfonic acid (PFOS), perfluoroheptanoic acid (PFHpS), perfluorobutanesulfonate (PFBS) and perfluorodecanoic acid (PFDA), were detected at mass concentrations of 11.4-30.7 ng/L. The highest mass concentration of PFOA was determined to be 25.5 ng/L. The PFCs in the Dongtiaoxi River were found to be mainly associated with precursor degradation and industrial wastewater discharge. A sudden rise in the pollution level was observed near the sampling point with the lowest detected concentration, which is possibly ascribable to the strong hydrodynamic difference between the hydraulic transport process near the river wharf and the highly turbulent flowing water. This difference results in the suspended particles in surface water mixing with re-suspended sediment particles such that PFCs are released back into the surface water. Pollution levels were observed to continuously decrease in the directions of the extended river and its estuary and tributaries. Risk assessments revealed that the PFC levels in the surface water of the Dongtiaoxi River basin are much lower than the official health reference value and have not reached levels that are expected to cause ecological harm and risk human health. The data are expected to support monitoring-system improvements by providing an in-depth understanding of occurrence characteristics, and help formulate a management plan for PFCs in the Dongtiaoxi River.

摘要

全氟化合物(PFCs)被广泛使用,具有持久性,其在水中的存在令人高度关注。PFCs,尤其是短链变体,在水中具有高溶解性和流动性,这使得它们能够通过河流系统进行长距离传输,有可能导致广泛污染。这些化合物抗降解,这对常规水处理方法构成挑战,因为常规方法往往无法有效去除PFCs,导致它们在水体中长期存在。本文建立了一种以磁性聚苯乙烯吡咯烷酮(FeO-PLS)作为磁性吸附剂,用于富集水中11种PFCs的磁性固相萃取方法。纯化的亲脂性PLS磁珠用作固相萃取剂,其表面用苯基和吡咯烷酮基团进行修饰,以促进对含有亲水性官能团和疏水性烷基侧链的PFCs的吸附。水中的PFCs通过液相色谱-串联质谱(LC-MS/MS)进行准确灵敏的测定。该方法包括准确称取50 mg(±0.05 mg)的FeO-PLS放入500 mL烧杯中,加入2 mL甲醇(用于活化),将烧杯置于磁铁上30 s,一旦甲醇和FeO-PLS完全分离,就弃去甲醇。向烧杯中加入200 mL混合PFC水溶液等分试样,超声处理15 min,然后置于强磁铁上,直到FeO-PLS在烧杯底部完全分离。弃去上层液体。加入4 mL含0.1%甲酸的乙腈作为FeO-PLS洗脱剂,超声处理30 s,之后将烧杯置于磁铁上并收集洗脱液。样品在氮气流下吹干,残渣用0.5 mL乙腈重新溶解,超声处理10 s,然后在通过LC-MS/MS分析之前进行膜过滤。11种PFCs在1至100 μg/L范围内呈现良好的线性关系,相关系数()在0.997 6至0.999 9之间。检测限和定量限(分别为LOD和LOQ)分别确定为0.001 - 0.620 ng/L和0.002 - 2.065 ng/L,表明具有高灵敏度。11种PFCs在不同浓度(0.05、1、10和50 μg/L)下的回收率为60.8% - 120.0%。相对标准偏差(RSD)范围为1.0%至20.0%,符合水中PFC分析的要求。使用所建立的方法分析了杭州东苕溪15个地点(靠近工厂、水库和居民区)的11种PFCs浓度。总共检测到6种PFCs,即全氟辛酸(PFOA)、全氟壬酸(PFNA)、全氟辛烷磺酸(PFOS)、全氟庚酸(PFHpS)、全氟丁烷磺酸(PFBS)和全氟癸酸(PFDA),质量浓度为11.4 - 30.7 ng/L。PFOA的最高质量浓度确定为25.5 ng/L。发现东苕溪中的PFCs主要与前体降解和工业废水排放有关。在检测浓度最低的采样点附近观察到污染水平突然上升,这可能归因于河码头附近的水力输送过程与高度湍流的流水之间强烈的水动力差异。这种差异导致地表水的悬浮颗粒与再悬浮的沉积物颗粒混合,从而使PFCs释放回地表水。在河流延伸方向及其河口和支流方向观察到污染水平持续下降。风险评估表明,东苕溪流域地表水的PFC水平远低于官方健康参考值,尚未达到预期会造成生态危害和危害人类健康的水平。这些数据有望通过深入了解其存在特征来支持监测系统的改进,并有助于制定东苕溪中PFCs的管理计划。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/08af/12093205/5c57573df245/EEC9103A-3AFC-4bc6-BDD9-499387ACCEFA-F003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/08af/12093205/1e8037115b2b/EEC9103A-3AFC-4bc6-BDD9-499387ACCEFA-F001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/08af/12093205/9e73d2c0f70e/EEC9103A-3AFC-4bc6-BDD9-499387ACCEFA-F002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/08af/12093205/5c57573df245/EEC9103A-3AFC-4bc6-BDD9-499387ACCEFA-F003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/08af/12093205/1e8037115b2b/EEC9103A-3AFC-4bc6-BDD9-499387ACCEFA-F001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/08af/12093205/9e73d2c0f70e/EEC9103A-3AFC-4bc6-BDD9-499387ACCEFA-F002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/08af/12093205/5c57573df245/EEC9103A-3AFC-4bc6-BDD9-499387ACCEFA-F003.jpg

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