Xianghu Laboratory, Hangzhou 311231, China; College of Agricultural, Nanjing Agricultural University, Nanjing 210095, China.
School of Geographical Sciences, Fujian Normal University, Fuzhou 350007, China.
J Hazard Mater. 2024 Dec 5;480:136068. doi: 10.1016/j.jhazmat.2024.136068. Epub 2024 Oct 5.
Microplastics (MPs) potentially alter physicochemical and transformation of heavy metals (HMs) in soils, which may depend on the specific characteristics of soil types. However, the dynamical and long-term mechanisms remain to be elucidated. A five-year incubation experiment was conducted to evaluate the influence of MPs on the chemical speciation of Pb, Ni, Cu, Cr, Cd, and As in the meadow, tidal, cinnamon, saline-alkali, and brown soils. From the first year to the fifth year, the clay value of the meadow, tidal, cinnamon, and saline-alkali soils was increased by 31.35 %, 9.63 %, 30.12 %, and 33.12 %, respectively; the pH values of the cinnamon and saline-alkali soils were increased by 15.02 % and 15.86 %, respectively. Besides, speciation distribution results suggested that the application of MPs reduced the liable available (LB) form (F2-dissolved and F3-ion exchangeable) of HMs and increased the potentially available (PB) form (F5-minerals and F6-organic-bound fraction) of HMs in all soils. Compared with other forms, F2 HMs fraction was the most responsive to MPs. Furthermore, the average bioconcentration factor (BCF) of Cr and Pb decreased by 73.75 % and 70.41 % in soils, respectively. Interestingly, soil type showed more impact on the form of HMs, which was associated with the different physicochemical parameters of soils, while application time displayed more impact on the bioavailability of HMs. Moreover, our results suggested that soils with higher clay content and pH values (such as cinnamon and saline-alkali soils) may mitigate the bioavailability of HMs more effectively in the presence of MPs, while soils with lower clay content may be more vulnerable to HMs contamination over time. This work highlights the importance of long-term monitoring of the impact of MPs on HMs dynamics for effective mitigation of soil contamination risks. Our study provides valuable guidance for soil remediation strategies and environmental quality management across different soil types.
微塑料(MPs)可能会改变土壤中重金属(HMs)的理化性质和转化,这可能取决于土壤类型的具体特征。然而,其动态和长期机制仍有待阐明。本研究进行了为期五年的孵化实验,以评估 MPs 对草甸、潮汐、肉桂、盐碱和棕壤中 Pb、Ni、Cu、Cr、Cd 和 As 化学形态的影响。从第 1 年到第 5 年,草甸、潮汐、肉桂和盐碱土壤的粘粒含量分别增加了 31.35%、9.63%、30.12%和 33.12%;肉桂和盐碱土壤的 pH 值分别增加了 15.02%和 15.86%。此外,形态分布结果表明,MPs 的应用降低了 HMs 的可利用(LB)形态(F2-溶解态和 F3-离子交换态),增加了 HMs 的潜在可利用(PB)形态(F5-矿物态和 F6-有机结合态)在所有土壤中。与其他形态相比,F2 中的 HMs 形态对 MPs 最敏感。此外,Cr 和 Pb 的平均生物浓缩因子(BCF)分别降低了 73.75%和 70.41%。有趣的是,土壤类型对 HMs 的形态有更大的影响,这与土壤的不同理化参数有关,而应用时间对 HMs 的生物可利用性有更大的影响。此外,我们的研究结果表明,在 MPs 存在的情况下,粘土含量和 pH 值较高的土壤(如肉桂土和盐碱土)可能更有效地降低 HMs 的生物可利用性,而粘土含量较低的土壤随着时间的推移可能更容易受到 HMs 污染。这项工作强调了长期监测 MPs 对 HMs 动态影响的重要性,以便有效减轻土壤污染风险。本研究为不同土壤类型的土壤修复策略和环境质量管理提供了有价值的指导。