食品接触材料中全氟和多氟烷基物质(PFAS)的综合筛选:利用燃烧离子色谱法进行总有机氟(TOF)分析。

Jingli Hu, Richard E Cochran, Cynthia M Grim, Neil G Rumachik
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引用次数: 0

摘要

背景:全氟和多氟烷基物质(PFAS)由数千种氟化化学品组成。它们越来越受到关注,因为许多PFAS化合物具有持久性和毒性。含有PFAS的食品接触材料(FCM)给人类带来了多种暴露途径,促使12个州颁布法律,禁止PFAS含量超过100 ppm的FCM。目的:虽然LC-MS通常用于测量目标PFAS化合物,但样品中大部分PFAS总含量可能会被遗漏。为了更全面地了解样品中的有机氟含量,我们建立了一种燃烧离子色谱法(CIC)测量FCM中TOF和可萃取有机氟(EOF)的方法。方法:该技术利用氧气和氩气气氛下的燃烧。所有气态、酸性燃烧产物被收集在水中,离子在离子交换柱上分离,并通过电导率检测。燃烧10 ~ 50 mg氟cm测定总氟(TF)。总无机氟(TIF)的测定方法是用水提取冷磨FCM,然后直接注入IC系统。然后用TF减去TIF计算TOF。用80%甲醇/20%乙腈从地面FCM中提取分析物,用CIC法测定EOF。结果:方法对TOF的检出限(MDL)为0.51 ppm,超出了国家现行规定的灵敏度要求。EOF与TOF的比较表明,在FCM样品中,EOF占TOF的比例不到15%。结论:TOF是评估FCM中PFAS污染的关键指标,因为靶向LC-MS方法可能会遗漏样品中的大部分PFAS。重点:我们开发了一种灵敏、自动化的方法来测定FCM中的TOF和EOF。该方法可用于FCM中PFAS的筛选,确保符合PFAS污染的现行法规。
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Comprehensive Screening of per- and Polyfluoroalkyl Substances (PFAS) in Food Contact Materials: Utilizing Combustion Ion Chromatography for Total Organic Fluorine (TOF) Analysis.

Background: Per- and polyfluoroalkyl substances (PFAS) comprise thousands of fluorinated chemicals. They are of growing concern because many PFAS compounds are persistent and toxic. Food contact materials (FCM) containing PFAS pose multiple exposure pathways to humans, prompting twelve states to enact laws banning FCM with PFAS levels exceeding 100 ppm of TOF.

Objective: While LC-MS is often used to measure targeted PFAS compounds, much of the total PFAS content in the sample may be missed. To understand organic fluorine content in samples more comprehensively, we developed a method using combustion ion chromatography (CIC) to measure TOF and extractable organic fluorine (EOF) in FCM.

Method: This technology utilizes combustion under an oxygen and argon atmosphere. All gaseous, acidic combustion products are collected in water, with ions separated on an ion exchange column and detected by conductivity. Total fluorine (TF) was measured by combusting 10-50 mg of FCM. Total inorganic fluorine (TIF) was measured by extracting cryo-ground FCM with water followed by direct injection to the IC system. TOF was then calculated by subtracting TIF from TF. EOF was determined by CIC after extracting analytes from the ground FCM using 80% methanol/20% acetonitrile.

Results: The Method detection limit (MDL) for TOF is 0.51 ppm, exceeding the sensitivity requirements of current state regulations. A comparison of EOF to TOF revealed that EOF constitutes less than 15% of the TOF in the FCM samples.

Conclusions: TOF is a critical metric for assessing PFAS contamination in FCM, as targeted LC-MS approaches may miss much of the PFAS in the samples.

Highlights: We developed a sensitive and automated method to determine TOF and EOF in FCM. The method can be used to screen for PFAS in FCM, ensuring compliance with current regulations on PFAS contamination.

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