[固相萃取-气相色谱-静电场轨道阱高分辨质谱法测定海水中4类34种氯代持久性有机污染物]。

Meng-Hao Gao, Xiao-Ying Li, Yuan Gao, Hai-Jun Zhang, Ji-Ping Chen
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引用次数: 0

摘要

海洋是自然环境中污染物的“汇”。因此,以陆源海洋污染为重点的问题日益引起人们的注意。包括有机氯农药(OCPs)、多氯联苯(PCBs)、短链氯化石蜡(SCCPs)和脱氯烷+异构体(DPs)在内的持久性有机污染物(POPs)对环境和人类都有严重的危害。这些持久性有机污染物已在海洋环境中广泛检测到,并且通常以微量水平存在;然而,分离和确定单个污染物需要大量的采样和时间。建立一种确定典型持久性有机污染物的准确分析方法对于研究其环境行为及其对海洋环境的相关生态风险至关重要。本研究建立了固相萃取(SPE)联合气相色谱-静电场轨道阱-高分辨率质谱(GC-Orbitrap-HRMS)测定海水中34种氯化POPs的方法,包括25种OCPs、6种PCB同系物、SCCPs和2种DPs。对色谱条件和质谱参数进行了优化,并对提取溶剂和纯化方法的影响进行了系统研究。二氯甲烷在海水样品的液-液萃取(LLE)中表现出满意的萃取效率,OCPs的回收率为73.1% ~ 120.5%,PCBs的回收率为87.2% ~ 101.7%,sccp的回收率为105.5%,DPs的回收率为74.9% ~ 78.6%。采用500 mg Florisil固相萃取柱进行纯化,洗脱液为9∶1 (v/v)正己烷/丙酮,34种氯化POPs的回收率在68.2% ~ 122.8%之间。采用DB-5MS (15 m×0.25 mm×0.10 μm)毛细管色谱柱分离目标化合物,电子电离(EI)源检测OCPs和pcb,负化学电离(NCI)源检测SCCPs和DPs。所有目标化合物在全扫描模式下分析。OCPs和SCCPs采用内标法定量,PCBs和DPs采用同位素稀释法定量。在共萃取物质混合物中检测氯化持久性有机污染物时观察到的严重干扰在纯化后完全消除。34种目标氯代持久性有机污染物在相应范围内呈良好的线性关系,相关系数(R2)均超过0.9。优化条件下,25种OCPs的检出限为0.009 ~ 0.061 ng/L, 6种pcb的检出限为0.006 ~ 0.016 ng/L, sccp的检出限为2.78 ng/L, 2种DPs的检出限为0.021 ~ 0.023 ng/L,检出限分别为0.06 ~ 0.24、0.02 ~ 0.06、11.12和0.08 ~ 0.09 ng/L。在低、中、高水平加标样品的加标回收率范围为70.6% ~ 128.9%,验证了该方法的准确性和精密度。相对标准偏差(n=6)测定为0.2% ~ 19.2%。这些结果突出了所开发的分析海水中痕量氯化持久性有机污染物的方法的适用性。该方法具有样品前处理简单、灵敏度高、分析通量快、成本效益好、痕量检测稳定性好等特点;因此,它适用于海水中典型氯化持久性有机污染物的快速、准确分析。该方法有望在海洋环境监测和海水污染应急监测中发挥重要作用。将该方法应用于渤海海域的海水样品中,结果表明,SCCPs的检出率最高(90%),而α-六氯环己烷(α-HCH)的检出率仅为30%。其余ocp均低于检出限。PCB-52是海水样品中唯一检测到的PCB同系物。SCCPs的检测浓度远高于其他持久性有机污染物,最高值为130.6 ng/L。因此,必须特别注意sccp。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

[Determination of four classes of 34 chlorinated persistent organic pollutants in seawater by solid-phase extraction and gas chromatography-electrostatic field orbitrap high resolution mass spectrometry].

[Determination of four classes of 34 chlorinated persistent organic pollutants in seawater by solid-phase extraction and gas chromatography-electrostatic field orbitrap high resolution mass spectrometry].

[Determination of four classes of 34 chlorinated persistent organic pollutants in seawater by solid-phase extraction and gas chromatography-electrostatic field orbitrap high resolution mass spectrometry].

Ocean acts as a "sink" for pollutants in the natural environment. Consequently, issues focused on marine pollution from terrestrial origin is attracting increasing attention. Persistent organic pollutants (POPs), including organochlorine pesticides (OCPs), polychlorinated biphenyls (PCBs), short-chain chlorinated paraffins (SCCPs), and dechlorane plus isomers (DPs), are serious hazards for both the environment and humans. These POPs have been widely detected in the marine environment and are typically present at trace levels; however, separating and determining individual contaminants require large amounts of sampling and time. Establishing an accurate analytical method for determining typical POPs is critical for studying their environmental behavior and associated ecological risks to the marine environment. In this study, we developed a method based on solid-phase extraction (SPE) combined with gas chromatography-electrostatic field orbitrap high resolution mass spectrometry (GC-Orbitrap-HRMS) for determining 34 chlorinated POPs in seawater, including 25 OCPs, six PCB congeners, SCCPs and two DPs. The chromatographic conditions and MS parameters were optimized, and the effects of the extraction solvent and purification method were systematically studied. Dichloromethane exhibited satisfactory extraction efficiencies during the liquid-liquid extraction (LLE) of seawater samples, with recoveries of 73.1%-120.5% for OCPs, 87.2%-101.7% for PCBs, 105.5% for SCCPs, and 74.9%-78.6% for DPs, respectively. Purification using a SPE column with 500 mg of Florisil was adopted, and 9∶1 (v/v) n-hexane/acetone was confirmed as the eluent with recoveries between 68.2% and 122.8% for all the 34 chlorinated POPs. A DB-5MS (15 m×0.25 mm×0.10 μm) capillary chromatographic column was used to separate the target compounds, with an electron ionization (EI) source used to detect OCPs and PCBs, whereas SCCPs and DPs were determined in negative chemical ionization (NCI) source. All target compounds were analyzed in full-scan mode. An internal standard quantification method was used for OCPs and SCCPs while isotope dilution quantification was used for PCBs and DPs. The severe interference observed during the detection of chlorinated POPs in the mixture of co-extracted substances was completely eliminated following the purification. The 34 target chlorinated POPs exhibited good linearities in their corresponding ranges, with correlation coefficients (R2) exceeding 0.9. The method demonstrated low detection limits under the optimized conditions, with values of 0.009-0.061 ng/L for the 25 OCPs, 0.006-0.016 ng/L for the six PCBs, 2.78 ng/L for the SCCPs, and 0.021-0.023 ng/L for the two DPs, with lower limits of determination of 0.06-0.24, 0.02-0.06, 11.12, and 0.08-0.09 ng/L, respectively. Accuracy and precision were validated by the recoveries of samples spiked at low, medium, and high levels, which ranged between 70.6% and 128.9%. Relative standard deviations (n=6) were determined to be 0.2%-19.2%. These results highlight the suitability of the developed method for analyzing trace amounts of chlorinated POPs in seawater. The method is characterized by simple sample pretreatment, high sensitivity, fast analytical throughput, cost-effectiveness, and good stability for trace-level detection; hence, it is suitable for the rapid and accurate analysis of typical chlorinated POPs in seawater. This method is expected to play a significant role in marine environmental monitoring and the emergency surveillance of seawater pollution. The developed method was applied to seawater samples collected from Bohai, which revealed that the highest detection frequency (90%) was recorded for the SCCPs, while α-hexachlorocyclohexane (α-HCH) was only detected in 30% of the samples. All other OCPs were below the detection limit. PCB-52 was the only PCB congener detected in the seawater samples. The SCCPs were detected in much higher concentrations than the other POPs, with the highest value of 130.6 ng/L recorded. Consequently, particular attention must be paid to SCCPs.

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