Sustainability Cluster, School of Advanced Engineering, UPES, Dehradun 248007, Uttarakhand, India.
Sustainability Cluster, School of Advanced Engineering, UPES, Dehradun 248007, Uttarakhand, India; Escuela de Ingeniería y Ciencias, Tecnológico de Monterrey, Campus Monterey, Monterrey 64849, Nuevo León, Mexico.
J Contam Hydrol. 2024 Sep;266:104398. doi: 10.1016/j.jconhyd.2024.104398. Epub 2024 Jul 14.
The ubiquity of plastics in modern life has made them a significant environmental concern and a marker of the Anthropocene era. The degradation of plastics results in the formation of microplastics (MPs), which measure 5 mm or less. The coexistence of MPs with other pollutants found in sludge, water treatment plant effluents, surface water, and groundwater, shapes the environmental landscape together. Despite extensive investigation, the long-term implications of MPs in soils remain uncertain, underscoring the importance of delving into their transportation and interactions with soil biota and other contaminants. The present article provides a comprehensive overview of MPs contamination in soil, encompassing its sources, prevalence, features, and interactions with soil flora and fauna, heavy metals, and organic compounds. The sources of MPs in soil agroecosystems are mulching, composting, littering, sewage sludge, irrigation water, and fertilizer application. The concentration of MPs reported in plastic mulch, littering, and sewage sludge is 503 ± 2760 items per kg, 4483 ± 2315 MPs/kg, and 11,100 ± 570 per/kg. The transport of MPs in soil agroecosystems is due to their horizontal and vertical migration including biotic and abiotic mobility. The article also highlighted the analytical process, which includes sampling planning, collection, purification, extraction, and identification techniques of MPs in soil agroecosystems. The mechanism in the interaction of MPs and organic pollutants includes surface adsorption or adhesion cation bridging, hydrogen bonding, charge transfer, ligand exchange, van der Waals interactions, and ion exchange.
塑料在现代生活中的普遍存在使其成为一个重大的环境问题,并成为人类世时代的标志。塑料的降解会导致微塑料(MPs)的形成,其尺寸为 5 毫米或以下。MPs 与污泥、污水处理厂废水、地表水和地下水等其他污染物共存,共同构成了环境景观。尽管已经进行了广泛的研究,但 MPs 在土壤中的长期影响仍不确定,这凸显了深入研究 MPs 在土壤中的迁移及其与土壤生物区系和其他污染物的相互作用的重要性。本文全面概述了土壤中 MPs 的污染,包括其来源、普遍性、特征以及与土壤动植物、重金属和有机化合物的相互作用。土壤农业生态系统中 MPs 的来源包括覆盖物、堆肥、垃圾、污水污泥、灌溉水和肥料应用。塑料覆盖物、垃圾和污水污泥中 MPs 的浓度分别为 503±2760 个/千克、4483±2315 个/千克和 11100±570 个/千克。土壤农业生态系统中 MPs 的迁移是由于其包括生物和非生物移动性的水平和垂直迁移。本文还强调了 MPs 在土壤农业生态系统中的分析过程,包括采样规划、收集、净化、提取和识别技术。 MPs 与有机污染物相互作用的机制包括表面吸附或粘附、阳离子桥接、氢键、电荷转移、配体交换、范德华相互作用和离子交换。