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基于聚乙烯和聚(己二酸丁二醇酯-对苯二甲酸酯)的可生物降解微塑料调节土壤中 Cd 和 As 的生物可利用性和形态:转化机制的见解。

Polyethylene and poly (butyleneadipate-co-terephthalate)-based biodegradable microplastics modulate the bioavailability and speciation of Cd and As in soil: Insights into transformation mechanisms.

机构信息

School of Environmental Science and Engineering, Shaanxi University of Science & Technology, Xi'an 710021, China.

College of Resources and Environment, Yunnan Agricultural University, Kunming 650201, China.

出版信息

J Hazard Mater. 2023 Mar 5;445:130638. doi: 10.1016/j.jhazmat.2022.130638. Epub 2022 Dec 21.

Abstract

Microplastics (MPs) that enter the soil can alter the physicochemical and biochemical properties of soil and affect speciation of heavy metals (HMs), thereby perturbing the bioavailability of HMs. However, the mechanisms underlying these effects are not understood. Therefore, we investigated the effects of MPs from poly (butyleneadipate-co-terephthalate)-based biodegradable mulch (BM) and polyethylene mulch (PM) in Cd- or As-contaminated soil on soil properties and speciation of HMs. MPs were characterised using Fourier-transform infrared spectroscopy (FTIR) and X-ray photoelectron spectroscopy (XPS). The addition of MPs reduced the bioavailability of HMs in soil and promoted the transformation of HMs into inert fractions. The mechanisms underlying the reduction of the bioavailability of HMs in soils could be as follows: (1) the entry of MPs into the soil changed its properties, which reduced the bioavailability of HMs; (2) FTIR and XPS analyses revealed that the hydroxyl and carboxyl groups and benzene ring present on the surface of aged MPs stabilized complexes (As(V)-O) with As(V) may have directly reduced the bioavailability of As(V) in soil; (3) aged BM exposed more amounts and types of reactive functional groups and was more effective in stabilising soil HMs than PM. Overall, this study provides new insights regarding the complexation mechanisms of soil HMs by MPs from different plastic mulch sources.

摘要

微塑料(MPs)进入土壤会改变土壤的理化和生化性质,并影响重金属(HMs)的形态,从而扰乱 HMs 的生物可利用性。然而,这些影响的机制尚不清楚。因此,我们研究了来自基于聚(丁二酸丁二醇酯-共对苯二甲酸酯)的可生物降解覆盖物(BM)和聚乙烯覆盖物(PM)的 MPs 在 Cd 或 As 污染土壤中对土壤性质和 HMs 形态的影响。使用傅里叶变换红外光谱(FTIR)和 X 射线光电子能谱(XPS)对 MPs 进行了表征。MPs 的添加降低了土壤中 HMs 的生物可利用性,并促进了 HMs 向惰性部分的转化。土壤中 HMs 生物可利用性降低的机制可能如下:(1)MPs 进入土壤改变了其性质,从而降低了 HMs 的生物可利用性;(2)FTIR 和 XPS 分析表明,老化 MPs 表面存在的羟基和羧基以及苯环可能与 As(V)形成稳定的配合物(As(V)-O),从而直接降低了土壤中 As(V)的生物可利用性;(3)暴露于 aged BM 的 MPs 具有更多数量和类型的反应性官能团,并且比 PM 更有效地稳定土壤 HMs。总体而言,这项研究提供了关于不同塑料覆盖物来源的 MPs 与土壤 HMs 络合机制的新见解。

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