提高人工湿地的脱氮能力:综合垂直流系统中进水基质浓度的作用

IF 14 1区 环境科学与生态学 Q1 ENVIRONMENTAL SCIENCES Environmental Science and Ecotechnology Pub Date : 2024-03-20 DOI:10.1016/j.ese.2024.100411
Tongtong Liu , Da Li , Yan Tian , Jiajie Zhou , Ye Qiu , Dongyi Li , Guohong Liu , Yujie Feng
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引用次数: 0

摘要

近年来,人工湿地(CWs)的发展突显了提高氮(N)去除效率的必要性。然而,由于进水基质浓度的变化会对脱氮效率和机制产生影响,因此给脱氮策略的优化带来了挑战。在此,我们利用富含 NO3-N 和 NH4+-N 的废水,以不同的碳氮比(1、3 和 6),展示了一体化垂直流建造湿地(IVFCWs)中进水底物浓度与脱氮过程之间的相互作用。在富含 NO3-N 的系统中,碳氮比与总氮(TN)去除率之间呈正相关,随着碳氮比从 1 升至 6,总氮去除率从 13.46 ± 2.23% 显著升至 87.00 ± 2.37%。相反,在富含 NH4+-N 的系统中,A-6 设置的 TN 去除效率(33.69 ± 4.83%)略高于 A-3 和 A-1 系统的 1.25 至 1.29 倍,这归因于溶解氧(DO)水平和碱度的限制。微生物群落分析和代谢途径评估表明,在 C/N 比(C/N ≥ 3)较高的 NO3-N 系统中,厌氧反硝化、微生物氮同化和硝酸盐还原成铵(DNRA)占主导地位。相反,在 NH4+-N 系统和低 C/N NO3-N 系统中,好氧反硝化和微生物氮同化作用是主要途径。质量平衡法表明,在NO3--N系统中,反硝化作用和微生物氮同化作用对TN去除的贡献率分别为4.12-47.12%和8.51-38.96%;在NH4+-N系统中,反硝化作用和微生物氮同化作用对TN去除的贡献率分别为0.55-17.35%和7.83-33.55%。为了提高N的去除率,NO3--N为主的系统应解决碳源限制以及反硝化和DNRA过程之间的电子竞争问题,而NH4+-N为主的系统则需要优化碳利用途径,并确保充足的溶解氧和碱度供应。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

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Enhancing nitrogen removal in constructed wetlands: The role of influent substrate concentrations in integrated vertical-flow systems

Recent advancements in constructed wetlands (CWs) have highlighted the imperative of enhancing nitrogen (N) removal efficiency. However, the variability in influent substrate concentrations presents a challenge in optimizing N removal strategies due to its impact on removal efficiency and mechanisms. Here we show the interplay between influent substrate concentration and N removal processes within integrated vertical-flow constructed wetlands (IVFCWs), using wastewaters enriched with NO3-N and NH4+-N at varying carbon to nitrogen (C/N) ratios (1, 3, and 6). In the NO3-N enriched systems, a positive correlation was observed between the C/N ratio and total nitrogen (TN) removal efficiency, which markedly increased from 13.46 ± 2.23% to 87.00 ± 2.37% as the C/N ratio escalated from 1 to 6. Conversely, in NH4+-N enriched systems, TN removal efficiencies in the A-6 setup (33.69 ± 4.83%) were marginally 1.25 to 1.29 times higher than those in A-3 and A-1 systems, attributed to constraints in dissolved oxygen (DO) levels and alkalinity. Microbial community analysis and metabolic pathway assessment revealed that anaerobic denitrification, microbial N assimilation, and dissimilatory nitrate reduction to ammonium (DNRA) predominated in NO3-N systems with higher C/N ratios (C/N ≥ 3). In contrast, aerobic denitrification and microbial N assimilation were the primary pathways in NH4+-N systems and low C/N NO3-N systems. A mass balance approach indicated denitrification and microbial N assimilation contributed 4.12–47.12% and 8.51–38.96% in NO3-N systems, respectively, and 0.55–17.35% and 7.83–33.55% in NH4+-N systems to TN removal. To enhance N removal, strategies for NO3-N dominated systems should address carbon source limitations and electron competition between denitrification and DNRA processes, while NH4+-N dominated systems require optimization of carbon utilization pathways, and ensuring adequate DO and alkalinity supply.

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来源期刊
CiteScore
20.40
自引率
6.30%
发文量
11
审稿时长
18 days
期刊介绍: Environmental Science & Ecotechnology (ESE) is an international, open-access journal publishing original research in environmental science, engineering, ecotechnology, and related fields. Authors publishing in ESE can immediately, permanently, and freely share their work. They have license options and retain copyright. Published by Elsevier, ESE is co-organized by the Chinese Society for Environmental Sciences, Harbin Institute of Technology, and the Chinese Research Academy of Environmental Sciences, under the supervision of the China Association for Science and Technology.
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