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Published September 2021 | Accepted Version + Supplemental Material
Journal Article Open

Altered microbial CAZyme families indicated dead biomass decomposition following afforestation

Abstract

Afforestation can modify terrestrial carbon (C) pools, some of which are primarily fixed in the plant dead biomass and then incorporated into the microbial dead biomass. Soil microorganisms exert a critical role in C flow and potentially influence C balance through the degradation of plant and microbial dead biomass. Here, we compared sites along a 45-year Robinia pseudoacacia (RP) afforestation chronosequence on the Loess Plateau of China. Subsequently, the trends of microbial carbohydrate-active enzymes (CAZyme) and their responses to the decomposition of dead biomass of different origins were studied using metagenomics. The results show that soil microbial CAZyme families, which degrade the plant- and microbial-derived components, significantly increased after afforestation, with a significant peak at the 20-year site. The dominant bacterial phyla (i.e., Actinobacteria, Proteobacteria, and Acidobacteria) mineralized C sources from plant and microbial biomass components through their corresponding CAZyme families. Moreover, the increased abundance of CAZymes involved in the decomposition of plant-derived components (e.g., cellulose, hemicellulose, and lignin) contributed to the formation of C pools. In the case of microbial-derived components, the abundance of CAZymes encoding the bacterial-derived components (peptidoglycan) was larger than that encoding fungal-derived components (chitin and glucans) and was more associated with microbial metabolic activity (qCO2 and Cmic: Corg ratio), indicating a higher investment of bacterial-derived components for microbial carbon turnover following afforestation. Overall, our study compares plant- and microbial-derived biomass to illustrate the differential contributions of dead biomass to C accumulation and confirms the importance of the bacterial community and derived biomass for C turnover following afforestation.

Additional Information

© 2021 Elsevier Ltd. Received 21 February 2021, Revised 15 July 2021, Accepted 16 July 2021, Available online 27 July 2021. This work were financially supported by the National Natural Science Foundation of China (No. 41907031), Shaanxi Innovation Capability Support Program (2019PT-13), the Natural Science Basic Research Plan in Shaanxi Province of China (No. 2020JQ-272; 2019JM-211), the 2021 first funds for central government to guide local science and technology development in Qinghai Province (2021ZY002), the Young Talents Support Program of the Science and Technology Association of Shaanxi Provincial Universities (No. 20200701), the Chinese Academy of Sciences "Light of West China" Program for Introduced Talent in the West (No. 31570440) and the China Postdoctoral Science Foundation (No. 2019M650276). The authors are also grateful to anonymous reviewers whose comments and suggestions helped us to enhance the quality of this paper. The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper. The authors declare no competing financial interest.

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Accepted Version - 1-s2.0-S0038071721002352-main.pdf

Supplemental Material - 1-s2.0-S0038071721002352-mmc1.docx

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Additional details

Created:
August 22, 2023
Modified:
October 23, 2023