Research Progress on the Effects of Bisphenol Compounds on Human Beings and Animals
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摘要: 双酚类化合物(Bisphenol compounds,BPs)是合成高分子材料的重要原材料之一。目前,常见的双酚类化合物主要包括双酚A、双酚B、双酚F以及双酚AF等。现如今,双酚类化合物主要应用于塑料制品、食品包装、饮用水添加剂、海鲜等方面。大量的研究发现,双酚类化合物通过物理迁移、化学迁移、生物迁移途径侵入人类和动物体内,甚至在深海哺乳动物体内也检测到了该物质,从而影响了机体的生殖系统、神经系统、消化系统、心血管系统、行为、发育和代谢性疾病的发生发展。因此,双酚类化合物引起了更多的关注。因此,本文主要从BPs的分类、侵入机体的途径以及对机体的影响方面进行了综述,以期对BPs的进一步研究以及安全性和毒理学评价提供参考依据。Abstract: Bisphenol compounds (BPs) are one of the most significant raw materials, used in synthesizing high polymer materials. At present, common BPs mainly include bisphenol A, bisphenol B, bisphenol F, bisphenol AF and so on. Nowadays, BPs are principally applied in plastic products, the food packaging, drinking water additives, seafood and other fields. A large number of studies have found that BPs penetrate into human beings and animals by physical migration, chemical migration, biological migration and it even have been detected in deep-sea mammals, affecting the mechanisms of the reproductive system, central nervous system, digestive system, cardiovascular system, behavior, development, and metabolic diseases. Therefore, BPs have been attracting more attention. In the review, the classification, invasive pathway to foods of BPs, and its implication on human beings and animals are systematically reviewed, hoping to provide reference for the safety and toxicological evaluation of BPs.
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表 1 双酚类化合物的结构与侵入方式
Table 1. Structure and invasion pathways of BPs
名称 分子式 分子结构 侵入方式 侵入途径 参考文献 双酚A(BPA)
Bisphenol AC15H16O2 物理迁移
化学迁移
生物迁移皮肤和粘膜
消化道
呼吸道[13] 双酚B(BPB)
Bisphenol BC16H18O2 [16−17] 双酚C(BPC)
Bisphenol CC17H20O2 [25] 双酚E(BPE)
Bisphenol EC14H14O2 [26] 双酚F(BPF)
Bisphenol FC13H12O2 [27] 双酚P(BPP)
Bisphenol PC24H26O2 [26] 双酚S(BPS)
Bisphenol SC12H10O4S [28] 双酚Z(BPZ)
Bisphenol ZC18H20O2 [29] 双酚AF(BPAF)
Bisphenol AFC15H10F6O2 [23] 双酚AP(BPAP)
Bisphenol APC20H18O2 [30] 四溴双酚A(TBBPA)
Tetrabromo bisphenol AC15H12Br4O2 [31] 四氯双酚A(TCBPA)
Tetrachloro bisphenol AC15H12Cl4O2 [32] 表 2 BPs对生殖系统的影响
Table 2. Effects of BPs on the reproductive system
研究类型(模型) BPs 浓度 影响 参考文献 体外 牛卵母细胞和精子 BPA,BPS,BPF 0.05 mg/mL BPA处理:活性氧升高,重组人线粒体超氧化物歧化酶-2、
谷胱甘肽过氧化物酶1、谷胱甘肽过氧化物酶4基因及
蛋白表达降低;BPF、BPS处理:精子产量减少[41] 体外 人类精子 BPA 0,10−3,10−2,10−1,10,103 nmol/L 精子活力、进行性运动和黄体酮诱导的顶体反应显着下降 [42] 体内 雄性大鼠 BPS 0.5,5,50 μg/L 精子活力、产量、附睾中精子数量减少;血浆睾酮、
黄体生成素、卵泡刺激素浓度降低,雌二醇水平升高;
睾丸中氧化应激水平升高[43] 体内 成年雄性小鼠 BPA 5,50 mg/kg bw/day 生殖细胞比例异常、睾丸形态改变、精元干细胞功能特性丧失 [44] 体外 小鼠卵母细胞 BPA,BPF 5,25,50 μg/mL 纺锤体缩短,微管附着减少 [45] 体内 成年雄性大鼠 BPF 1,5,25,50 mg/kg/d 精子减少,睾丸激素分泌物水平降低 [46] 体内 雌性和雄性斑马鱼 BPB 0.001,0.01,0.1,1 mg/L 鱼卵数量减少,孵化率及存活率降低,生殖功能受损 [47] 体内 雌性和雄性斑马鱼 BPAF 0.05,0.25,1 mg/L 雄性斑马睾酮水平降低,鱼E2水平升高;雌性斑马鱼睾酮分泌增加 [48] 表 3 BPs对胚胎发育的影响
Table 3. Effects of BPs on embryonic development
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