College of Environment, Hohai University, 210098, PR China.
College of Environment, Hohai University, 210098, PR China; Ministry of Education Key Laboratory of Integrated Regulation and Resource Development on Shallow Lakes, Hohai University, Nanjing, 210098, PR China.
J Environ Manage. 2021 Aug 15;292:112654. doi: 10.1016/j.jenvman.2021.112654. Epub 2021 May 8.
Bioretention has been increasingly used recently to treat heavy metals contaminated stormwater. However, less is known about how metal accumulation influences microbial performance and organics removal mechanisms in different layers of the bioretention system. Two lab-scale bioretention columns (i.e., control and Cu treatment) were designed and filled with soil and fillers (zeolite and ceramsite). The results obtained from the time-series experiment of 121 days showed that the removal of organics markedly affected by Cu accumulation and microbial activities, varied between soil and filler layers of bioretention system. The overall organics removal rate was higher in filler than soil. However, at the individual level, the chemical oxygen demand (COD) removal rate was higher than total organic carbon (TOC) in the soil, while the opposite trend was observed in fillers. Mixed media (soil + fillers) significantly reduced the bio-available and labile fractions of Cu from 33.5 to 8% and 67.5 to 33.4%, respectively. The bioretention column treated with Cu lost 14% more microbial biomass in soil than filler over the 121 days study period. Therefore mixed media in bioretention system can offset the substantial negative impacts of long-term metal accumulation on pollutant removal and microbial degradation function in the bioretention. The present study advanced our understanding to resolve the complex metals-impacted microbial pollutant biodegradation mechanisms and highlight importance of mixed media in the long-term maintenance of the bioretention system, which is imperative for developing effective and stormwater-specific remediation strategies.
生物滞留技术最近越来越多地被用于处理重金属污染的雨水。然而,对于金属积累如何影响生物滞留系统不同层中的微生物性能和有机物去除机制,人们知之甚少。设计并填充了两个实验室规模的生物滞留柱(即对照和 Cu 处理),分别用土壤和填充料(沸石和陶粒)填充。在 121 天的时间序列实验中获得的结果表明,有机物的去除受 Cu 积累和微生物活性的显著影响,在生物滞留系统的土壤和填充层之间存在差异。总体有机物去除率在填充料中高于土壤。然而,在个体水平上,土壤中的化学需氧量(COD)去除率高于总有机碳(TOC),而在填充料中则相反。混合介质(土壤+填充料)将可生物利用的和不稳定的 Cu 分数分别从 33.5%和 67.5%降低到 8%和 33.4%。在 121 天的研究期间,用 Cu 处理的生物滞留柱在土壤中的微生物生物量比填充料中损失了 14%。因此,在生物滞留系统中使用混合介质可以抵消长期金属积累对污染物去除和微生物降解功能的负面影响。本研究加深了我们对解决复杂的金属影响微生物污染物生物降解机制的理解,并强调了混合介质在长期维持生物滞留系统方面的重要性,这对于开发有效的、针对雨水的修复策略至关重要。