Toxicological Centre, University of Antwerp, Universiteitsplein 1, 2610, Wilrijk, Belgium.
Toxicological Centre, University of Antwerp, Universiteitsplein 1, 2610, Wilrijk, Belgium; Daiichi University of Pharmacy, 22-1 Tamagawa-cho, Minami-ku, Fukuoka, 815-8511, Japan.
Food Chem Toxicol. 2021 Aug;154:112311. doi: 10.1016/j.fct.2021.112311. Epub 2021 Jun 1.
Due to the growth of the world's population, edible insects have been considered a valuable alternative food source for humans. Japan has a long-lasting traditional culture of eating wild insects, a practice that has recently evolved towards farming and selling reared edible insects. In this study, we investigated the contamination loads, profiles, and possible sources of organophosphorus flame retardants (PFRs), plasticizers, and selected persistent organic pollutants (POPs) in insect foods available on the Japanese market. Medians of selected POPs in the dataset were up to 1.3 ng/g lw, while medians of PFRs and plasticizers were 12 and 486 ng/g ww, respectively. CB-153, p,p'-DDE, BDE-47, tris(1-chloro-2-propyl)-phosphate (TCIPP), and bis(2-ethylhexyl)-phthalate (DEHP) were the dominant compounds in the analyzed samples, a pattern comparable to previous investigations on organic chemicals in edible insects. Our overall results suggest that POPs were likely accumulated by the insects during rearing or from the wild environment, while PFRs and plasticizers derived from post-harvesting industrial handling and seasoning. Differences in pollution patterns and the absence of correlations between PFR and plasticizer loads in insects and in food packaging suggest that the transfer of contaminants from food contact materials is not a main source of contamination.
由于世界人口的增长,食用昆虫已被视为人类有价值的替代食物来源。日本有着悠久的食用野生昆虫的传统文化,这种做法最近已经发展为养殖和销售养殖可食用昆虫。在本研究中,我们调查了日本市场上可获得的昆虫食品中的有机磷阻燃剂(PFRs)、增塑剂和选定的持久性有机污染物(POPs)的污染负荷、分布情况和可能来源。数据集中选定 POPs 的中位数高达 1.3ng/g 干重,而 PFRs 和增塑剂的中位数分别为 12ng/g 和 486ng/g 湿重。CB-153、p,p'-DDE、BDE-47、三(1-氯-2-丙基)磷酸酯(TCIPP)和邻苯二甲酸二(2-乙基己基)酯(DEHP)是分析样品中主要的化合物,这与之前对食用昆虫中有机化学品的研究结果相似。我们的综合结果表明,POPs 可能是在昆虫养殖或从野外环境中积累的,而 PFRs 和增塑剂则来自收获后的工业处理和调味。昆虫和食品包装中 PFR 和增塑剂负荷之间污染模式的差异以及缺乏相关性表明,从食品接触材料转移污染物不是污染的主要来源。