甲壳类动物体内双酚A及相关的烷基酚污染物及其潜在生物效应

Y. Zuo, Zhuo Zhu, Mohammed Alshanqiti, Joseph P. Michael, Yiwei Deng
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引用次数: 8

摘要

双酚A广泛用于塑料和其他工业消费品。双酚A及其类似物在生产、使用和处置过程中释放到水生环境中,由于其毒性和对水生野生动物甚至人类内分泌的干扰作用,一直是科学界和公众关注的问题。最近的研究表明,这些烷基酚可能会影响美国龙虾、螃蟹和虾等甲壳类动物的蜕皮过程和生存。本研究建立了气相色谱-火焰离子化检测法(GC-FID)和气相色谱-质谱联用法(GC-MS)测定罗氏沼虾(Macrobrachium rosenbergii)、蓝蟹(Callinectes sapidus)和美洲龙虾(Homarus americanus)样品中双酚A及其类似物的方法。虾中双酚A、2,4-双-(二甲基苄基)酚和4-cumylphenol的浓度范围分别为0.67 ~ 5.51、0.36 ~ 1.61和< LOD(检出限)~ 1.96 ng/g(湿重),蟹中浓度范围分别为0.10 ~ 0.44、0.13 ~ 0.62和0.26 ~ 0.58 ng/g(湿重)。在龙虾组织样品中,双酚A、2-t-丁基-4-(二甲基苄基)苯酚、2,6-二-(t-丁基)-4-(二甲基苄基)苯酚、2,4-二-(二甲基苄基)苯酚、2,4-二-(二甲基苄基)苯酚、2,4-二-(二甲基苄基)-6-t-丁基苯酚和4-cumylphenol的浓度范围分别为4.48 ~ 7.01、1.23 ~ 2.63、2.71 ~ 9.10、0.35 ~ 0.91、0.64 ~ 3.25和0.44 ~ 1.00 ng/g(湿重)。在这些浓度水平下,BPA及其类似物可能会干扰甲壳类动物的繁殖和发育,如幼虫存活、换壳、变态和壳硬化。
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Bisphenol A and the related alkylphenol contaminants in crustaceans and their potential bioeffects
Bisphenol A is widely used in plastic and other industrial consumer products. Release of bisphenol A and its analogues into the aquatic environment during manufacture, use and disposal has been a great scientific and public concern due to their toxicity and endocrine disrupting effects on aquatic wildlife and even human beings. More recent studies have shown that these alkylphenols may affect the molting processes and survival of crustacean species such as American lobster, crab and shrimp. In this study, we have developed gas chromatography with flame ionization detection (GC-FID) and gas chromatography- mass spectrometric (GC-MS) methods for the determination of bisphenol A and its analogues in shrimp Macrobrachium rosenbergii, blue crab Callinectes sapidus and American lobster Homarus americanus samples. Bisphenol A, 2,4-bis-(dimethylbenzyl)phenol and 4-cumylphenol were found in shrimp in the concentration ranges of 0.67-5.51, 0.36-1.61, and < LOD (the limit of detection)-1.96 ng/g (wet weight), and in crab of 0.10-0.44, 0.13-0.62, and 0.26-0.58 ng/g (wet weight), respectively. In lobster tissue samples, bisphenol A, 2-t-butyl-4-(dimethylbenzyl)phenol, 2,6-bis-(t-butyl)-4-(dimethylbenzyl)phenol, 2,4-bis- (dimethybenzyl)phenol, 2,4-bis-(dimethylbenzyl)-6-t-butylphenol and 4-cumylphenol were determined at the concentration ranges of 4.48-7.01, 1.23-2.63, 2.71-9.10, 0.35-0.91, 0.64-3.25, and 0.44-1.00 ng/g (wet weight), respectively. At these concentration levels, BPA and its analogs may interfere the reproduction and development of crustaceans, such as larval survival, molting, metamorphosis and shell hardening.
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