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四溴双酚 A(TBBPA)在潜水土壤和土壤-植物系统中的降解和代谢。

Degradation and metabolism of tetrabromobisphenol A (TBBPA) in submerged soil and soil-plant systems.

机构信息

State Key Laboratory of Pollution Control and Resource Reuse, School of the Environment, Nanjing University , 163 Xianlin Avenue, 210023 Nanjing, People's Republic of China.

出版信息

Environ Sci Technol. 2014 Dec 16;48(24):14291-9. doi: 10.1021/es503383h. Epub 2014 Dec 5.

Abstract

Contamination by tetrabromobisphenol A (TBBPA), the most widely used brominated flame retardant, is a matter of environmental concern. Here, we investigated the fate and metabolites of (14)C-TBBPA in a submerged soil with an anoxic-oxic interface and planted or not with rice (Oryza sativa) and reed (Phragmites australis) seedlings. In unplanted soil, TBBPA dissipation (half-life 20.8 days) was accompanied by mineralization (11.5% of initial TBBPA) and the substantial formation (60.8%) of bound residues. Twelve metabolites (10 in unplanted soil and 7 in planted soil) were formed via four interconnected pathways: oxidative skeletal cleavage, O-methylation, type II ipso-substitution, and reductive debromination. The presence of the seedlings strongly reduced (14)C-TBBPA mineralization and bound-residue formation and stimulated debromination and O-methylation. Considerable radioactivity accumulated in rice (21.3%) and reed (33.1%) seedlings, mainly on or in the roots. While TBBPA dissipation was hardly affected by the rice seedlings, it was strongly enhanced by the reed seedlings, greatly reducing the half-life (11.4 days) and increasing monomethyl TBBPA formation (11.3%). The impact of the interconnected aerobic and anaerobic transformation of TBBPA and wetland plants on the profile and dynamics of the metabolites should be considered in phytoremediation strategies and environmental risk assessments of TBBPA in submerged soils.

摘要

四溴双酚 A(TBBPA)是最广泛使用的溴系阻燃剂,其污染问题引起了人们的广泛关注。在这里,我们研究了(14)C-TBBPA 在具有缺氧-好氧界面的淹没土壤中的归宿和代谢物,同时研究了是否种植水稻(Oryza sativa)和芦苇(Phragmites australis)幼苗。在未种植的土壤中,TBBPA 的消解(半衰期为 20.8 天)伴随着矿化(初始 TBBPA 的 11.5%)和大量结合残留的形成(60.8%)。通过四个相互关联的途径形成了 12 种代谢物(未种植土壤中有 10 种,种植土壤中有 7 种):氧化骨架裂解、O-甲基化、II 型对位取代和还原脱溴。幼苗的存在强烈降低了(14)C-TBBPA 的矿化和结合残留的形成,并刺激了脱溴和 O-甲基化。相当多的放射性物质积累在水稻(21.3%)和芦苇(33.1%)幼苗中,主要在根上或根内。虽然 TBBPA 的消解几乎不受水稻幼苗的影响,但它受到芦苇幼苗的强烈促进,大大缩短了半衰期(11.4 天),并增加了单甲基 TBBPA 的形成(11.3%)。在淹没土壤中,TBBPA 和湿地植物的相互有氧和厌氧转化对代谢物的特征和动态的影响应在植物修复策略和 TBBPA 的环境风险评估中加以考虑。

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