Xiang Hua, Hong Yiguo, Wu Jiapeng, Wang Yu, Ye Fei, Ye Jiaqi, Lu Jing, Long Aimin
State Key Laboratory of Tropical Oceanography (LTO), South China Sea Institute of Oceanology, Chinese Academy of Sciences, Guangzhou, China.
Key Laboratory for Water Quality and Conservation of the Pearl River Delta, Institute of Environmental Research at Greater Bay Area, Ministry of Education, Guangzhou University, Guangzhou, China.
Front Microbiol. 2023 Jun 16;14:1218207. doi: 10.3389/fmicb.2023.1218207. eCollection 2023.
Denitrification is vital to nitrogen removal and NO release in ecosystems; in this regard, paddy soils exhibit strong denitrifying ability. However, the underlying mechanism of NO emission from denitrification in paddy soils is yet to be elucidated. In this study, the potential NO emission rate, enzymatic activity for NO production and reduction, gene abundance, and community composition during denitrification were investigated using the N isotope tracer technique combined with slurry incubation, enzymatic activity detection, quantitative polymerase chain reaction (qPCR), and metagenomic sequencing. Results of incubation experiments showed that the average potential NO emission rates were 0.51 ± 0.20 μmol⋅N⋅kg⋅h, which constituted 2.16 ± 0.85% of the denitrification end-products. The enzymatic activity for NO production was 2.77-8.94 times than that for NO reduction, indicating an imbalance between NO production and reduction. The gene abundance ratio of to Z from qPCR results further supported the imbalance. Results of metagenomic analysis showed that, although Proteobacteria was the common phylum for denitrification genes, other dominant community compositions varied for different denitrification genes. Gammaproteobacteria and other phyla containing the B gene without Z genes, including Actinobacteria, Planctomycetes, Desulfobacterota, Cyanobacteria, Acidobacteria, Bacteroidetes, and Myxococcus, may contribute to NO emission from paddy soils. Our results suggest that denitrification is highly modular, with different microbial communities collaborating to complete the denitrification process, thus resulting in an emission estimation of 13.67 ± 5.44 g NO⋅m⋅yr in surface paddy soils.
反硝化作用对于生态系统中的氮去除和一氧化氮(NO)释放至关重要;就此而言,稻田土壤表现出很强的反硝化能力。然而,稻田土壤反硝化作用产生NO排放的潜在机制尚待阐明。在本研究中,结合泥浆培养、酶活性检测、定量聚合酶链反应(qPCR)和宏基因组测序的氮同位素示踪技术,研究了反硝化过程中潜在的NO排放速率、NO产生和还原的酶活性、基因丰度以及群落组成。培养实验结果表明,平均潜在NO排放速率为0.51±0.20μmol⋅N⋅kg⋅h,占反硝化终产物的2.16±0.85%。NO产生的酶活性是NO还原酶活性的2.77 - 8.94倍,表明NO产生和还原之间存在不平衡。qPCR结果中 与Z的基因丰度比进一步支持了这种不平衡。宏基因组分析结果表明,虽然变形菌门是反硝化基因的常见门类,但不同反硝化基因的其他优势群落组成有所不同。γ-变形菌门和其他不含Z基因但含有B基因的门类,包括放线菌门、浮霉菌门、脱硫杆菌门、蓝细菌门、酸杆菌门、拟杆菌门和粘球菌,可能是稻田土壤NO排放的原因。我们的研究结果表明,反硝化作用具有高度模块化,不同的微生物群落协同完成反硝化过程,因此表层稻田土壤的NO排放估计为13.67±5.44 g NO⋅m⋅yr。