What is in the fish? Collaborative trial in suspect and non-target screening of organic micropollutants using LC- and GC-HRMS

嫌疑犯 环境科学 环境化学 渔业 化学 心理学 生物 犯罪学
作者
Wiebke Dürig,Sofia Lindblad,Oksana Golovko,Georgios Gkotsis,Reza Aalizadeh,Maria‐Christina Nika,Νikolaos S. Τhomaidis,‪Nikiforos Alygizakis,Merle Plassmann,Peter Haglund,Qiuguo Fu,Juliane Hollender,Jade Chaker,Arthur David,Uwe Kunkel,André Macherius,Lidia Belova,Giulia Poma,Hugues Preud’homme,Catherine Munschy
出处
期刊:Environment International [Elsevier BV]
卷期号:181: 108288-108288 被引量:9
标识
DOI:10.1016/j.envint.2023.108288
摘要

A collaborative trial involving 16 participants from nine European countries was conducted within the NORMAN network in efforts to harmonise suspect and non-target screening of environmental contaminants in whole fish samples of bream (Abramis brama). Participants were provided with freeze-dried, homogenised fish samples from a contaminated and a reference site, extracts (spiked and non-spiked) and reference sample preparation protocols for liquid chromatography (LC) and gas chromatography (GC) coupled to high resolution mass spectrometry (HRMS). Participants extracted fish samples using their in-house sample preparation method and/or the protocol provided. Participants correctly identified 9–69 % of spiked compounds using LC-HRMS and 20–60 % of spiked compounds using GC-HRMS. From the contaminated site, suspect screening with participants’ own suspect lists led to putative identification of on average ∼145 and ∼20 unique features per participant using LC-HRMS and GC-HRMS, respectively, while non-target screening identified on average ∼42 and ∼56 unique features per participant using LC-HRMS and GC-HRMS, respectively. Within the same sub-group of sample preparation method, only a few features were identified by at least two participants in suspect screening (16 features using LC-HRMS, 0 features using GC-HRMS) and non-target screening (0 features using LC-HRMS, 2 features using GC-HRMS). The compounds identified had log octanol/water partition coefficient (KOW) values from −9.9 to 16 and mass-to-charge ratios (m/z) of 68 to 761 (LC-HRMS and GC-HRMS). A significant linear trend was found between log KOW and m/z for the GC-HRMS data. Overall, these findings indicate that differences in screening results are mainly due to the data analysis workflows used by different participants. Further work is needed to harmonise the results obtained when applying suspect and non-target screening approaches to environmental biota samples.
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