College of Environmental Science and Engineering, Ministry of Education Key Laboratory of Pollution Processes and Environmental Criteria, Tianjin Key Laboratory of Environmental Remediation and Pollution Control, Nankai University, Tianjin 300350, China.
College of Environmental Science and Engineering, Ministry of Education Key Laboratory of Pollution Processes and Environmental Criteria, Tianjin Key Laboratory of Environmental Remediation and Pollution Control, Nankai University, Tianjin 300350, China.
J Environ Sci (China). 2025 Apr;150:309-317. doi: 10.1016/j.jes.2024.03.008. Epub 2024 Mar 22.
Modeling the fate and transport of organic pollutants at contaminated sites is critical for risk assessment and management practices, such as establishing realistic cleanup standards or remediation endpoints. Against the conventional wisdom that highly hydrophobic persistent organic pollutants (POPs) (e.g., polybrominated diphenyl ethers and polycyclic aromatic hydrocarbons) in surface soils are essentially immobile, mounting evidence has demonstrated the potential of these contaminants leaching into the groundwater, due to enhanced transport by soil colloids. Here, we develop a Colloids-Enhanced Transport (CET) model, which can be used as a simple screening tool to predict the leaching potential of POPs into groundwater, as mediated by soil colloids. The CET model incorporates several processes, including the release of POPs-bearing colloids into the porewater, the vertical transport of colloids and associated POPs in the vadose zone, the mixing of POPs-containing soil leachate with groundwater, and the migration of POPs-bearing colloids in saturated zone. Thus, using parameters that can be easily obtained (e.g., annual rainfall, soil type, and common hydrogeological properties of the subsurface porous media), the CET model can estimate the concentrations of POPs in the saturated zone from the observed POPs concentrations in surface or shallow subsurface zones. The CET model can also be used to derive soil quality standards or cleanup endpoints by back-calculating soil concentrations based on groundwater protection limits.
在污染场地中对有机污染物的归宿和迁移进行建模对于风险评估和管理实践至关重要,例如制定现实的清理标准或修复终点。传统观点认为,表层土壤中高度疏水的持久性有机污染物(POPs)(例如多溴二苯醚和多环芳烃)基本上是不可移动的,但越来越多的证据表明,由于土壤胶体的增强传输作用,这些污染物有可能浸出到地下水中。在这里,我们开发了一种胶体增强传输(CET)模型,可作为一种简单的筛选工具,用于预测由于土壤胶体介导而将 POPs 浸出到地下水中的潜力。CET 模型结合了几个过程,包括将含有 POPs 的胶体释放到孔隙水中、胶体和相关 POPs 在包气带中的垂直传输、含 POPs 的土壤浸出液与地下水的混合以及含有胶体的 POPs 在饱和带中的迁移。因此,使用可以轻松获得的参数(例如,年降雨量、土壤类型和地下多孔介质的常见水文地质特性),CET 模型可以根据表层或浅层地下区域中观察到的 POPs 浓度估算饱和区中 POPs 的浓度。CET 模型还可以通过基于地下水保护限值反算土壤浓度来推导土壤质量标准或清理终点。