BSEF aisbl, Av. E. Van Nieuwenhuyse 4, 1160, Brussels, Belgium.
Department of Environmental Health, College of Medicine, University of Cincinnati, 160 Panceza Way, Cincinnati, OH, 45267-0056, USA.
Environ Sci Pollut Res Int. 2018 Jun;25(18):17268-17277. doi: 10.1007/s11356-018-2255-0. Epub 2018 May 17.
This article summarizes historical and recent research on the terrestrial toxicology of tetrabromobisphenol A (TBBPA). Despite its ubiquitous use and presence in the environment, little published data is available to evaluate the terrestrial ecotoxicity of TBBPA. The purposes of this paper are to enable broad access to a series of TBBPA ecotoxicity tests (nitrogen transformation, earthworm survival/reproduction, and seedling emergence/growth) that were conducted in support of regulatory risk assessments, and to summarize available research in the terrestrial toxicity of TBBPA. In these studies, no significant effect of TBBPA on nitrogen transformation was observed up to the highest concentration [1000 mg/kg dry weight (d.w.) soil]. The no-observed-effect concentrations (NOECs) for seedling emergence ranged from 20 to 5000 mg/kg d.w. Sensitivities were soybeans < corn ≈ onion ≈ tomato < ryegrass < cucumber; the most sensitive endpoints being seedling dry weight and height. The 28-day earthworm mortality NOEC was > 4840 mg/kg d.w. The most sensitive terrestrial endpoint was earthworm reproduction with a half maximal effective concentration (EC) of 0.12 mg/kg d.w. soil. Based on this sensitive terrestrial endpoint, the EU derived a predicted no-effect concentration (PNEC) for soil of 0.012 mg/kg wet weight soil (EU 2008). We did not identify a more sensitive/lower point of departure for terrestrial toxicity endpoints in the published literature. On the basis of this PNEC, the EU concluded there was potential risk for environmental effects near TBBPA manufacturing sites, but no additional risk provided that no sewage sludge was applied to agricultural land (EU 2008).
本文总结了四溴双酚 A(TBBPA)在陆地毒理学方面的历史和近期研究。尽管 TBBPA 广泛使用且存在于环境中,但可用于评估其陆地生态毒性的已发表数据很少。本文旨在广泛提供一系列 TBBPA 生态毒性测试(氮转化、蚯蚓存活/繁殖和幼苗出土/生长)的数据,这些测试是为支持监管风险评估而进行的,并总结 TBBPA 在陆地毒性方面的现有研究。在这些研究中,TBBPA 对氮转化的影响在最高浓度[1000mg/kg 干重(dw)土壤]下没有显著作用。幼苗出土的无观察效应浓度(NOEC)范围为 20 至 5000mg/kg dw。敏感性依次为大豆<玉米≈洋葱≈番茄<黑麦草<黄瓜;最敏感的终点是幼苗干重和高度。28 天蚯蚓死亡率的无观察效应浓度(NOEC)大于 4840mg/kg dw。最敏感的陆地终点是蚯蚓繁殖,半数最大有效浓度(EC)为 0.12mg/kg dw 土壤。基于这一敏感的陆地终点,欧盟得出土壤的预测无效应浓度(PNEC)为 0.012mg/kg 湿重土壤(欧盟,2008 年)。我们在已发表的文献中没有发现更敏感/更低的陆地毒性终点起点。基于这一 PNEC,欧盟得出结论,在 TBBPA 制造场所附近存在潜在的环境影响风险,但如果不将污水污泥施用于农业用地,则不会有额外风险(欧盟,2008 年)。