College of Water Sciences, Beijing Normal University, Beijing, 100875, China; Engineering Research Center of Groundwater Pollution Control and Remediation, Ministry of Education, Beijing, 100875, China.
College of Water Sciences, Beijing Normal University, Beijing, 100875, China; Engineering Research Center of Groundwater Pollution Control and Remediation, Ministry of Education, Beijing, 100875, China.
J Environ Manage. 2022 Sep 1;317:115366. doi: 10.1016/j.jenvman.2022.115366. Epub 2022 May 26.
Due to the leaching of capillary water, the petroleum pollutants initially trapped in vadose zone may migrate to lower aquifer, thus increasing the risk of groundwater pollution. In order to explore the effect of capillary leaching on toluene-contaminated soil and the relationship between toluene concentration (TC) and environmental factors (EFs) during the leaching process, the sterilized and non-sterilized soil column experiments were designed. The EFs were used to estimate TC. The results showed that the difference between leaching and volatilization rates directly determined the changing trend of toluene concentration in capillary water. The toluene concentration in the medium always showed decreasing trend due to leaching. The indigenous microbial community structure of the non-sterilized soil column was analyzed by 16S rRNA sequencing. It was found that indigenous microorganisms could degrade toluene after 33.0 days of acclimatation. The microbial population was dominated by bacteria, among them the Ellin6055 strain and Pseudomonas, Pseudoxanthomonas, Cupriavidus, Bdellovibrio, Sphingobium, Phenylobacterium, Ramlibacter, Bradyrhizobium, Shinella genera. The Pseudomonas was the most crucial bacterial genus that degraded toluene. Indigenous microbial degradation was the fundamental reason for strong response relationship. Furthermore, we suggested a relationship of function between environmental factors (pH, DO, ORP) and time (t) for toluene attenuation: C+ln(eαγ)=C, (α, β, γ represent the pH, DO, and ORP in leaching capillary water, respectively; A, B, and C represent undetermined coefficients), and the fitting coefficient R > 0.950. This relationship can only characterize the attenuation process of capillary zone leaching on toluene. However, it may still be utilized to give a theoretical foundation for understanding the dynamic of pollutant concentration change processes under specific environmental factors.
由于毛细水的淋滤作用,最初被捕获在包气带中的石油污染物可能会迁移到较低的含水层,从而增加地下水污染的风险。为了探索毛细淋滤对甲苯污染土壤的影响以及淋滤过程中甲苯浓度(TC)与环境因子(EFs)之间的关系,设计了灭菌和非灭菌土柱实验。使用 EFs 来估算 TC。结果表明,淋滤和挥发速率的差异直接决定了毛细水相中甲苯浓度的变化趋势。由于淋滤,介质中的甲苯浓度始终呈下降趋势。通过 16S rRNA 测序分析了非灭菌土柱的土著微生物群落结构。发现土著微生物在适应 33.0 天后可以降解甲苯。微生物种群主要由细菌组成,其中包括 Ellin6055 菌株和假单胞菌、假单胞菌、铜绿假单胞菌、贪噬菌、鞘氨醇单胞菌、苯基杆菌、拉姆利伯克菌、根瘤菌、希内拉属。假单胞菌是降解甲苯的最关键的细菌属。土著微生物降解是强响应关系的根本原因。此外,我们建议了环境因子(pH、DO、ORP)与时间(t)之间的甲苯衰减功能关系:C+ln(eαγ)=C,(α、β、γ 分别代表毛细水淋滤中的 pH、DO 和 ORP;A、B 和 C 代表未确定系数),拟合系数 R>0.950。这种关系只能描述毛细带淋滤对甲苯的衰减过程。然而,它仍然可以用来为理解特定环境因子下污染物浓度变化过程的动态提供理论基础。