Chu Yixuan, Zhang Xin, Tang Xudong, Jiang Lanhui, He Ruo
School of Civil Engineering and Architecture, Zhejiang University of Science and Technology, Hangzhou, 310023, China; Zhejiang- Singapore Joint Laboratory for Urban Renewal and Future City, Hangzhou, 310023, China.
Zhejiang Provincial Key Laboratory of Solid Waste Treatment and Recycling, School of Environmental Science and Engineering, Zhejiang Gongshang University, Hangzhou, 310012, China.
Environ Res. 2025 Apr 15;271:121139. doi: 10.1016/j.envres.2025.121139. Epub 2025 Feb 15.
Anaerobic oxidation of methane (AOM) coupled electron acceptor reduction has been shown to regulate methane (CH) emissions from the habitats. Landfill is one of the most important anthropogenic CH emission sources. However, the effect of electron acceptors on the AOM process and its microbial mechanism in landfills is poorly characterized. Herein, electron acceptors including nitrate, nitrite, sulfate and ferric iron were used to regulate the AOM process in landfill microcosms by using stable isotope probing analysis. The addition of electron acceptors could promote AOM in the landfilled waste. Among them, nitrate and nitrite had the strongest promoting effect on AOM in the waste with the maximum activities of 5.60-5.76 μg g d, which increased by 1070.9%-1103.6% compared with the control without electron acceptor amendation. Candidatus Methylomirabilis was only detected in assimilating CH in the ferric iron-amended treatment. The proteobacterial methanotrophs and Methylacidiphilum were mainly observed in the ferric iron C-DNA, likely due to O released from the conversion of nitric oxide. Methanomassiliicoccus were the most abundant archaea in the treatments with nitrate, nitrite and sulfate, while Methanosarcina dominated in the ferric iron-amended treatment. Nitrate, nitrite, sulfate and ferric iron all could prompt the growth of sulfur, iron, nitrate and nitrite metabolizing microorganisms. Partial least squares path modeling indicated that AOM in the landfilled waste could be driven by electron acceptors via the changes of environmental variables, while the direct effect of electron acceptors on the AOM activity was weak with an intensity of 0.06. Taken together, this study demonstrated that the AOM process in landfills can be regulated by electron acceptors, especially nitrate and nitrite, to mitigate CH emissions from landfills.
甲烷厌氧氧化(AOM)耦合电子受体还原已被证明可调节栖息地的甲烷(CH)排放。垃圾填埋场是最重要的人为CH排放源之一。然而,电子受体对垃圾填埋场AOM过程及其微生物机制的影响尚不清楚。在此,通过稳定同位素探测分析,使用包括硝酸盐、亚硝酸盐、硫酸盐和铁离子在内的电子受体来调节垃圾填埋场微观世界中的AOM过程。电子受体的添加可促进填埋废物中的AOM。其中,硝酸盐和亚硝酸盐对废物中AOM的促进作用最强,最大活性为5.60 - 5.76 μg g d,与未添加电子受体的对照相比增加了1070.9% - 1103.6%。仅在添加铁离子的处理中检测到厌氧甲烷氧化菌在同化CH。变形菌门甲烷营养菌和嗜酸甲基菌主要在铁离子C-DNA中观察到,可能是由于一氧化氮转化释放的O。甲烷微球菌是硝酸盐、亚硝酸盐和硫酸盐处理中最丰富的古菌,而甲烷八叠球菌在添加铁离子的处理中占主导地位。硝酸盐、亚硝酸盐、硫酸盐和铁离子均可促进硫、铁、硝酸盐和亚硝酸盐代谢微生物的生长。偏最小二乘路径模型表明,填埋废物中的AOM可通过环境变量的变化由电子受体驱动,而电子受体对AOM活性的直接影响较弱,强度为0.06。综上所述,本研究表明垃圾填埋场中的AOM过程可通过电子受体,特别是硝酸盐和亚硝酸盐来调节,以减少垃圾填埋场的CH排放。