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生物固体抑制三氯生和三氯卡班的生物利用度和植物摄取。

Biosolids inhibit bioavailability and plant uptake of triclosan and triclocarban.

机构信息

Department of Environmental Sciences, University of California, Riverside, CA 92521, USA; Institute of Nuclear Agricultural Sciences, Zhejiang University, Hangzhou 310029, China.

Department of Environmental Sciences, University of California, Riverside, CA 92521, USA.

出版信息

Water Res. 2016 Oct 1;102:117-124. doi: 10.1016/j.watres.2016.06.026. Epub 2016 Jun 14.

Abstract

Biosolids from wastewater treatment are primarily disposed of via land applications, where numerous pharmaceuticals and personal care products (PPCPs) may contaminate food crops and pose a human exposure risk. Biosolids are rich in organic carbon and addition of biosolids can increase the sorption of certain PPCPs in soil, decreasing their bioavailability. This study tested the hypothesis that the relative plant uptake of PPCPs decreases with increasing biosolids amendment. Accumulation of triclosan and triclocarban was measured in roots of radish and carrot grown in soils with or without biosolids. Addition of biosolids significantly prolonged the persistence of triclosan in soil. When expressed in bioaccumulation factor (BCF), accumulation of triclosan drastically decreased in biosolids-amended soils, while the effect was limited for triclocarban. Compared to the unamended soil, amending biosolids at 2% (w/w) decreased BCF of triclosan in the edible tissues of radish and carrot by 85.4 and 89.3%, respectively. Measurement using a thin-film passive sampler provided direct evidence showing that the availability of triclosan greatly decreased in biosolids-amended soils. Partial correlation analysis using data from this and published studies validated that biosolids decreased plant uptake primarily by increasing soil organic carbon content and subsequently sorption. Therefore, contamination of food crops by biosolids-borne contaminants does not linearly depend on biosolids use rates. This finding bears significant implications in the overall risk evaluation of biosolids-borne contaminants.

摘要

污水生物固体主要通过土地应用进行处置,其中许多药品和个人护理产品(PPCPs)可能会污染食用作物并对人类暴露构成风险。生物固体富含有机碳,添加生物固体可以增加土壤中某些 PPCPs 的吸附,从而降低其生物利用度。本研究检验了这样一个假设,即 PPCPs 的相对植物吸收随着生物固体添加剂的增加而降低。在有或没有生物固体的土壤中种植的萝卜和胡萝卜的根部测量了三氯生和三氯卡班的积累。添加生物固体显著延长了三氯生在土壤中的持久性。当以生物累积因子(BCF)表示时,三氯生在生物固体添加土壤中的积累急剧减少,而三氯卡班的影响有限。与未添加土壤相比,将生物固体以 2%(w/w)的比例添加到土壤中,分别降低了萝卜和胡萝卜可食用组织中三氯生的 BCF 达 85.4%和 89.3%。使用薄膜被动采样器进行的测量提供了直接证据,表明三氯生在生物固体添加土壤中的可用性大大降低。使用本研究和已发表研究的数据进行的偏相关分析验证了生物固体主要通过增加土壤有机碳含量和随后的吸附来降低植物吸收。因此,受生物固体携带污染物污染的食用作物的污染程度并不取决于生物固体的使用量呈线性关系。这一发现对生物固体携带污染物的总体风险评估具有重要意义。

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