Georgin Jordana, S P Franco Dison, de Oliveira Jivago Schummacher, Dehmani Younes, El Messaoudi Noureddine, Miyah Youssef, Alruwaili Amani, Knani Salah, Hwang Yuhoon
Department of Civil and Environmental Engineering, Universidad de la Costa, CUC, Barranquilla, Atlántico, Colombia.
Research Group on Nanobiotechnology and Biosystems Simulation, Universidade Franciscana (UFN), Santa Maria, RS, Brazil.
Int J Phytoremediation. 2025 Oct 27:1-27. doi: 10.1080/15226514.2025.2575792.
Phytoremediation is a technique that uses plants to decontaminate polluted environments, such as soil, water and even air. Plants employ several mechanisms to remove, stabilize or degrade contaminants, depending on the nature of the pollutant and the environmental conditions. The main mechanisms include: phytoextraction, phytodegradation, phytovolatilization, phytostabilization and rhizofiltration. The uptake of heavy metals by plants is influenced by several key factors. Soil characteristics such as soil properties such as pH, organic matter content, cation exchange capacity (CEC), and texture significantly affect the mobility and bioavailability of heavy metals. For example, soil pH influences metal solubility, and acidic conditions generally increase the availability of metals. Conversely, higher organic matter and CEC can bind heavy metals, reducing their bioavailability. Different plant species and even varieties within a species exhibit varying capacities to take up and accumulate heavy metals. Some plants, known as hyperaccumulators, can tolerate and concentrate high levels of heavy metals in their tissues, making them useful for phytoremediation. In contrast, other plants may restrict the uptake or translocation of metals to aerial parts. And environmental conditions such as factors such as temperature, humidity, and the presence of other contaminants can influence the uptake of heavy metals. For example, waterlogging conditions can alter the redox state of metals, affecting their solubility and availability to plants. Furthermore, interactions with other pollutants, such as microplastics, can modify the adsorption and mobility of heavy metals in the soil-plant system. The main soil contaminants that can be treated include heavy metals (such as lead, cadmium and mercury), pesticides, solvents, hydrocarbons and explosives. In water, phytoremediation is applied to remove heavy metals, excess nutrients (such as nitrogen and phosphorus), pesticides and organic compounds. Although less common, phytoremediation can also be used to treat air pollutants, such as volatile organic compounds (VOCs) and certain gases. These can be of anthropogenic or natural origin, the former being more evident due to industrial activities, agricultural practices and low removal efficiency of conventional treatments present in water treatment plants. This study aims to analyze the potential of using phytoremediation as a way of recovering ecosystems and ensuring a healthy environment. While nanomaterials and similar compounds can enhance phytoremediation, high doses may harm plants. Further research is needed to improve phytoremediation's efficiency and feasibility for restoring contaminated soil, water, and air.
植物修复是一种利用植物对受污染环境(如土壤、水甚至空气)进行净化的技术。植物根据污染物的性质和环境条件,采用多种机制来去除、稳定或降解污染物。主要机制包括:植物提取、植物降解、植物挥发、植物稳定和根际过滤。植物对重金属的吸收受几个关键因素影响。土壤特性,如土壤pH值、有机质含量、阳离子交换容量(CEC)和质地等,显著影响重金属的迁移性和生物有效性。例如,土壤pH值影响金属的溶解度,酸性条件通常会增加金属的有效性。相反,较高的有机质和CEC可以结合重金属,降低其生物有效性。不同的植物物种甚至同一物种内的不同品种吸收和积累重金属的能力各不相同。一些植物,即超富集植物,能够耐受并在其组织中浓缩高水平的重金属,这使得它们在植物修复中很有用。相比之下,其他植物可能会限制金属向地上部分的吸收或转运。环境条件,如温度、湿度以及其他污染物的存在等因素,会影响重金属的吸收。例如,涝渍条件会改变金属的氧化还原状态,影响其溶解度和对植物的有效性。此外,与其他污染物(如微塑料)的相互作用,会改变土壤-植物系统中重金属的吸附和迁移性。可处理的主要土壤污染物包括重金属(如铅、镉和汞)、农药、溶剂、碳氢化合物和爆炸物。在水中,植物修复用于去除重金属、过量营养物(如氮和磷)、农药和有机化合物。虽然不太常见,但植物修复也可用于处理空气污染物,如挥发性有机化合物(VOCs)和某些气体。这些污染物可能来自人为或自然源,由于工业活动、农业实践以及水处理厂中传统处理方法的去除效率较低,前者更为明显。本研究旨在分析利用植物修复来恢复生态系统和确保健康环境的潜力。虽然纳米材料和类似化合物可以增强植物修复,但高剂量可能会损害植物。需要进一步研究以提高植物修复在修复受污染土壤、水和空气方面的效率和可行性。