Multi-media interaction improves the efficiency and stability of the bioretention system for stormwater runoff treatment

生态调节池 生物炭 浸出(土壤学) 化学 有机质 雨水 硝酸盐 黄铁矿 环境化学 吸附 环境科学 地表径流 环境工程 土壤水分 土壤科学 热解 生态学 有机化学 生物 矿物学
作者
Zheng Kong,Yunqian Song,Mei Xu,Yan Yang,X. Wang,Haiyuan Ma,Yue Zhi,Zhiyu Shao,Lei Chen,Yunsong Yuan,Fujian Liu,Yanhong Xu,Qichang Ni,Shihu Hu,Hongxiang Chai
出处
期刊:Water Research [Elsevier]
卷期号:250: 121017-121017 被引量:6
标识
DOI:10.1016/j.watres.2023.121017
摘要

Bioretention systems are one of the most widely used stormwater control measures for urban runoff treatment. However, stable and effective dissolved nutrient treatment by bioretention systems is often challenged by complicated stormwater conditions. In this study, pyrite-only (PO), pyrite-biochar (PB), pyrite-woodchip (PW), and pyrite-woodchip-biochar mixed (M) bioretention systems were established to study the feasibility of improving both stability and efficiency in bioretention system via multi-media interaction. PB, PW, and M all showed enhanced dissolved nitrogen and/or phosphorus removal compared to PO, with M demonstrating the highest efficiency and stability under different antecedent drying durations (ADD), pollutant levels, and prolonged precipitation depth. The total dissolved nitrogen and dissolved phosphorus removal in M ranged between 64%–86% and 80%–95%, respectively, with limited organic matter and iron leaching. Pore water, microbial community, and material analysis collectively indicate that pyrite, woodchip, and biochar synergistically facilitated multiple nutrient treatment processes and protected each other against by-product leaching. Pyrite-woodchip interaction greatly increased nitrate removal by facilitating mixotrophic denitrification, while biochar further enhanced ammonium adsorption and expanded the denitrification area. The Fe3+ generated by pyrite aerobic oxidation was adsorbed on the biochar surface and potentially formed a Fe-biochar composite layer, which not only reduced Fe3+-induced pyrite excessive oxidation but also potentially increased organic matter adsorption. Fe (oxyhydr)oxides intermediate product formed by pyrite oxidation, in return, controlled the phosphorus and organic matter leaching from biochar and woodchip. Overall, this study demonstrates that multi-media interaction may enable bioretention systems to achieve stable and effective urban runoff treatment.
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