综述了双酚A二缩水甘油酯和新丙基缩水甘油酯的性质、生产、人体暴露、生物监测、毒性和调控

IF 9 Q1 ENVIRONMENTAL SCIENCES
Jingchuan Xue , Yuxian Liu , Danlin Yang , Yanan Zhao , Yanpeng Cai , Tao Zhang , Kurunthachalam Kannan
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引用次数: 1

摘要

尽管有大量研究调查了双酚A (BPA)等双酚类似物的环境发生、人体暴露和毒性作用,但对密切相关的化学类别,即双酚A二缩水甘油酯醚(badge)和新丙基缩水甘油酯醚(NOGEs)知之甚少,它们广泛用于各种工业和消费品。在这篇综述中,我们收集了有关徽章和NOGEs的生产和使用、分析挑战、饮食和非饮食暴露源、在人类和环境基质中的发生、毒性以及法规的现有信息。人体对徽章和NOGEs的暴露是普遍存在的,每天从饮食中摄入的暴露剂量为每公斤体重几百纳克(ng)至几微克(μg),从吸入室内空气和摄入室内灰尘中摄入的暴露剂量为每公斤体重每天10纳克(ng)至每公斤体重每天10纳克(ng)。罐头食品和饮料中所含的徽章和NOGEs的浓度为每克几十至几百纳克,在某些情况下甚至高达每克几千纳克。迄今为止,据报道,徽章的最高浓度是罐头鱼,为12.6毫克/公斤。据报道,室内粉尘样品中BADGE浓度高达63.2 mg/kg。在多项研究分析的5种徽章衍生物中,BADGE·2H2O和BADGE·HCl·H2O在室内粉尘和环境样品中占主导地位。据报道,在人类脂肪组织中,双酚F二缩水甘油醚(BFDGE)的浓度高达4500纳克/克,是NOGE的组成部分。徽章和NOGEs的环氧化物部分赋予这些化学物质高反应性,通过内分泌干扰,生殖效应和遗传毒性表现出毒性。据报道,徽章与DNA和蛋白质的加合物/缀合物和反应产物的形成,尽管对其发生的程度和毒性知之甚少。这些化学品的监管框架主要集中在罐头食品中的迁移限制上。尽管它们产量高,使用广泛,但对它们的环境迁移、毒性和命运的研究仍然有限,进一步的研究应侧重于徽章和NOGEs的加合物/生物转化产物、毒理学机制以及生态和人类健康风险。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
A review of properties, production, human exposure, biomonitoring, toxicity, and regulation of bisphenol A diglycidyl ethers and novolac glycidyl ethers

Although numerous studies have investigated environmental occurrence, human exposure, and toxic effects of bisphenol analogues including bisphenol A (BPA), little is known about closely related chemical classes namely, bisphenol A diglycidyl ethers (BADGEs) and novolac glycidyl ethers (NOGEs), which are widely used in a variety of industrial and consumer products. In this review, we compiled available information on production and usage, analytical challenges, dietary and non-dietary sources of exposure, occurrence in human and environmental matrices, toxicity, and regulations on BADGEs and NOGEs. Human exposure to BADGEs and NOGEs is widespread, with exposure doses in the range of several hundreds of nanograms (ng) to few micrograms (μg) per kilogram (kg) body weight (bw) per day (d) from diet and <10 ng/kg bw/d from inhalation of indoor air and indoor dust ingestion. Canned foods and beverages contain BADGEs and NOGEs at concentrations on the order of several tens to hundreds of nanogram (ng) per g and in some cases up to several thousand ng per g. The highest reported concentration of BADGEs thus far was in canned fish at 12.6 mg/kg. In indoor dust samples, a BADGE concentration of up to 63.2 mg/kg was reported. Among five derivatives of BADGEs analyzed in several studies, BADGE·2H2O and BADGE·HCl·H2O were predominant in indoor dust and environmental samples. In human adipose tissue, a concentration of up to 4500 ng/g bisphenol F diglycidyl ether (BFDGE), a building block of NOGE, was reported. The epoxide moieties of BADGEs and NOGEs impart high reactivity of these chemicals, which exhibit toxicity through endocrine disruption, reproductive effects and genotoxicity. Formation of adducts/conjugates and reaction products of BADGEs with DNA and protein was reported, although little is known about the magnitude of their occurrence and toxicity. Regulatory framework for these chemicals is mainly focused on migration limits in canned foods. Despite their high production and widespread usage, studies on environmental transport, toxicity and fate are still limited and further studies should focus on adducts/biotransformation products, toxicological mechanisms, as well as ecological and human health risks of BADGEs and NOGEs.

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