Abstract

Wetlands are the largest natural source of terrestrial CH4 emissions. Afforestation can enhance soil CH4 oxidation and decrease methanogenesis, yet the driving mechanisms leading to these effects remain unclear. We analyzed the structures of communities of methanogenic and methanotrophic microbes, quantification of mcrA and pmoA genes, the soil microbial metagenome, soil properties and CH4 fluxes in afforested and non-afforested areas in the marshland of the Yangtze River. Compared to the non-afforested land use types, net CH4 emission decreased from bare land, natural vegetation and 5-year forest plantation and transitioned to net CH4 sinks in the 10- and 20-year forest plantations. Both abundances of mcrA and pmoA genes decreased significantly with increasing plantation age. By combining random forest analysis and structural equation modeling, our results provide evidence for an important role of the abundance of functional genes related to methane production in explaining the net CH4 flux in this ecosystem. The structures of methanogenic and methanotrophic microbial communities were of lower importance as explanatory factors than functional genes in terms of in situ CH4 flux. We also found a substantial interaction between functional genes and soil properties in the control of CH4 flux, particularly soil particle size. Our study provides empirical evidence that microbial community function has more explanatory power than taxonomic microbial community structure with respect to in situ CH4 fluxes. This suggests that focusing on gene abundances obtained, e.g., through metagenomics or quantitative/digital PCR could be more effective than community profiling in predicting CH4 fluxes, and such data should be considered for ecosystem modeling.

Highlights

  • Natural wetlands are the largest source of CH4 emissions, accounting for ∼62% of the CH4 budget (Nazaries et al, 2013a)

  • These studies did not include an analysis of the methanogenic community, which may have been altered by afforestation and could affect the net flux of CH4 flux independent of the methanotrophic community

  • Methanotrophs are divided into type-I and type-II, and we found that most of the Operational taxonomic units (OTUs) belonged to type-I methanotrophs, including Crenothrix, Methylobacter, Methylomicrobium, Methylomonas and Methylosarcina

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Summary

Introduction

Natural wetlands are the largest source of CH4 emissions, accounting for ∼62% of the (natural) CH4 budget (Nazaries et al, 2013a). Studies have shown that increased CH4 sink strength following afforestation is associated with increased dominance of members of the USC α clade-type-II-related methanotrophs (Nazaries et al, 2011, 2013b; Täumer et al, 2021). These studies did not include an analysis of the methanogenic community, which may have been altered by afforestation and could affect the net flux of CH4 flux independent of the methanotrophic community. The lack of studies that include analyses of both methanogenic and methanotrophic communities strongly limits our understanding of the mechanisms by which CH4 emissions are mitigated by afforestation

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