The diversity and co-occurrence network of soil bacterial and fungal communities and their implications for a new indicator of grassland degradation

Grassland degradation is a retrogressive succession of grassland vegetation, which leads to the loss of biodiversity and the degradation of ecosystem functions. Soil microbiomes play critical roles in the functioning and services of grassland ecosystems, yet little is known about how their diversity...

Full description

Bibliographic Details
Main Authors: Liu, L. (Author), Naeem, I. (Author), Ruan, H. (Author), Wang, D. (Author), Wang, L. (Author), Wang, S. (Author), Wu, X. (Author), Yang, J. (Author), Yang, Y. (Author)
Format: Article
Language:English
Published: Elsevier B.V. 2021
Subjects:
Online Access:View Fulltext in Publisher
LEADER 04525nam a2200817Ia 4500
001 10.1016-j.ecolind.2021.107989
008 220427s2021 CNT 000 0 und d
020 |a 1470160X (ISSN) 
245 1 0 |a The diversity and co-occurrence network of soil bacterial and fungal communities and their implications for a new indicator of grassland degradation 
260 0 |b Elsevier B.V.  |c 2021 
856 |z View Fulltext in Publisher  |u https://doi.org/10.1016/j.ecolind.2021.107989 
520 3 |a Grassland degradation is a retrogressive succession of grassland vegetation, which leads to the loss of biodiversity and the degradation of ecosystem functions. Soil microbiomes play critical roles in the functioning and services of grassland ecosystems, yet little is known about how their diversity, structure and co-occurrence network characteristics respond to grassland degradation. Here, we used lllumina Miseq technique to evaluate soil bacterial and fungal communities in a meadow steppe with different degrees of degradation in Northeastern China. Our results showed that Actinobacteria, Proteobacteria, and Chloroflexi and Acidobacteria were the dominant bacterial phyla, while Ascomycota, Basidiomycota, and Zygomycota were the predominant fungal phyla. The relative abundance of taxa assigned to Actinobacteria, Gemmatimonadetes, Firmicutes, and Deinococcus-Thermus increased with increasing degradation degrees, whereas those affiliated with Acidobacteria and Nitrospirae showed a decreasing pattern. Compared to bacteria, the relative abundance of most fungal phyla decreased gradually along the degradation gradient. Bacterial Shannon diversity index possessed a similar hump pattern, while fungal diversity decreased with increasing degree of grassland degradation. Bacterial and fungal communities have different responses to grassland degradation, indicating that fungi are more sensitive to grassland degradation than bacteria. Both bacterial and fungal community structures were significantly different among the three sites. Changes in soil bacterial and fungal community structures were best explained by soil salinity and pH. Plant diversity and nitrogen concentration in aboveground plant tissues were also important factors for regulating fungal communities. Co-occurrence network analysis revealed that microbial taxa increased positive interactions and average degree to strengthen the adaptability of microorganisms to grassland degradation. These findings could enhance our understanding of the formation and maintenance of microbial community diversity in degraded grasslands and the development of a new indicator for grassland ecosystem management. © 2021 
650 0 4 |a Acidobacteria 
650 0 4 |a Actinobacteria 
650 0 4 |a Ascomycota 
650 0 4 |a Bacteria 
650 0 4 |a Bacteria (microorganisms) 
650 0 4 |a bacterium 
650 0 4 |a Basidiomycota 
650 0 4 |a biodegradation 
650 0 4 |a Biodegradation 
650 0 4 |a biodiversity 
650 0 4 |a Biodiversity 
650 0 4 |a China 
650 0 4 |a Chloroflexi 
650 0 4 |a community structure 
650 0 4 |a Community structure 
650 0 4 |a Community structures 
650 0 4 |a Co-occurrence network 
650 0 4 |a Co-occurrence networks 
650 0 4 |a Deinococcus-Thermus 
650 0 4 |a dominance 
650 0 4 |a Ecosystems 
650 0 4 |a environmental degradation 
650 0 4 |a Firmicutes 
650 0 4 |a Fungal community 
650 0 4 |a Fungi 
650 0 4 |a fungus 
650 0 4 |a Gemmatimonadetes 
650 0 4 |a grassland 
650 0 4 |a Grassland degradation 
650 0 4 |a Grassland degradation 
650 0 4 |a Grassland ecosystems 
650 0 4 |a Indicator indicator 
650 0 4 |a meadow 
650 0 4 |a microbial community 
650 0 4 |a Microbial diversity 
650 0 4 |a Microbial diversity 
650 0 4 |a Nitrospirae 
650 0 4 |a Proteobacteria 
650 0 4 |a relative abundance 
650 0 4 |a Soil bacteria 
650 0 4 |a Soil bacterial community 
650 0 4 |a Soil bacterium 
650 0 4 |a Soil fungal communities 
650 0 4 |a Soil fungi 
650 0 4 |a Soil fungi 
650 0 4 |a soil microorganism 
650 0 4 |a Soils 
650 0 4 |a succession 
650 0 4 |a Zygomycota 
700 1 |a Liu, L.  |e author 
700 1 |a Naeem, I.  |e author 
700 1 |a Ruan, H.  |e author 
700 1 |a Wang, D.  |e author 
700 1 |a Wang, L.  |e author 
700 1 |a Wang, S.  |e author 
700 1 |a Wu, X.  |e author 
700 1 |a Yang, J.  |e author 
700 1 |a Yang, Y.  |e author 
773 |t Ecological Indicators