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在添加生物炭和沼气残渣的稻草堆肥过程中,氨氧化菌和反硝化真菌对 NO 生成的相对贡献。

Relative contribution of ammonia-oxidizing bacteria and denitrifying fungi to NO production during rice straw composting with biochar and biogas residue amendments.

机构信息

College of Environment and Ecology, Hunan Agricultural University, 410128, China; Yuelu Mountain Laboratory, Hunan Agricultural University Area, Changsha 410000, Hunan, China.

Department of Botany and Microbiology, College of Science, King Saud University, P. O. Box 2455, Riyadh 11451, Saudi Arabia.

出版信息

Bioresour Technol. 2023 Dec;390:129891. doi: 10.1016/j.biortech.2023.129891. Epub 2023 Oct 18.

Abstract

Nitrous oxide (NO) production is associated with ammonia-oxidizing bacteria (amoA-AOB) and denitrifying fungi (nirK-fungi) during the incorporation of biochar and biogas residue composting. This research examined the relative contribution of alterations in the abundance, diversity and structure of amoA-AOB and nirK-fungi communities on NO emission by real-time PCR and sequence processing. Results showed that NO emissions showed an extreme relation with the abundance of amoA-AOB (rs = 0.584) while giving credit to nirK-fungi (rs = 0.500). Nitrosomonas and Nitrosospira emerged as the dominant genera driving ammoxidation process. Biogas residue changed the community structure of AOB by altering Nitrosomonadaceae proportion and physiological capacity. The denitrification process, primarily governed by nirK-fungi, served as a crucial pathway for NO production, unveiling the pivotal mechanism of biochar to suppress NO emissions. C/N and NH-N were identified as significant parameters influencing the distribution of nirK-fungi, especially Micromonospora, Halomonas and Mesorhizobium.

摘要

在生物炭和沼气残渣堆肥过程中,一氧化二氮(NO)的产生与氨氧化细菌(amoA-AOB)和反硝化真菌(nirK-fungi)有关。本研究通过实时 PCR 和序列处理,考察了 amoA-AOB 和 nirK-fungi 群落丰度、多样性和结构变化对 NO 排放的相对贡献。结果表明,NO 排放与 amoA-AOB 的丰度呈极显著相关(rs=0.584),而与 nirK-fungi 呈显著相关(rs=0.500)。亚硝化单胞菌和硝化螺旋菌是推动氨氧化过程的主要属。沼气残渣通过改变硝化单胞菌科的比例和生理能力改变了 AOB 的群落结构。反硝化过程主要由 nirK-fungi 控制,是 NO 产生的关键途径,揭示了生物炭抑制 NO 排放的关键机制。C/N 和 NH-N 被确定为影响 nirK-fungi 分布的重要参数,特别是 Micromonospora、Halomonas 和 Mesorhizobium。

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