Soil microbial adaptation to carbon deprivation: shifts in lignocellulolytic gene profiles following long-term plant exclusion
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Background
Lignocellulose represents a primary input of organic carbon (C) into soils, yet the identity of specific microorganisms and genes which drive lignocellulose turnover in soils remains poorly understood. To address this knowledge gap, we used a 10-year grassland plant-exclusion experiment to investigate how reduced plant C inputs affect microbial communities and their lignocellulolytic potential using a combination of metagenomic sequencing and untargeted metabolomics. We specifically tested the hypothesis that microbial community function in bare fallow plots would transition towards microbiota with genes for recalcitrant biomass degradation (i.e., lignocellulose), when compared to grassland plots with high labile C inputs.
Results
Long-term plant exclusion lowered soil C and nitrogen (N) and reduced cellulose content, whilst hemicellulose and lignin were unchanged. Similarly soil microbiomes were highly distinct in long-term bare soils, along with soil extracellular enzyme profiles, though short-term plant-removal effects were less apparent. Plant exclusion resulted in a general enrichment of Firmicutes, Thaumarchaeota, Acidobacteria, Fusobacteria, and Ascomycota, with a general reduction in Actinobacteria. However, changes in bare soil lignocellulose degradation genes were more associated with discrete taxa from diverse lineages, particularly the Proteobacteria. Grouping of lignocellulose-degrading genes into broad substrate classes (cellulases, hemicellulases and lignases) revealed a possible increase in lignin degradation genes under plant exclusion confirming our hypothesis, although all other changes were at the level of the carbohydrate-active enzyme (CAZy) family. Intriguingly, untargeted metabolome profiles were highly responsive to plant exclusion, even after only one year. Bare soils were depleted in oligosaccharides and enriched in monosaccharides, fatty and carboxylic acids, supporting emerging evidence of long-term persistent C being within simple compounds.
Conclusions
Together our data show that extracellular lignin degrading enzymes increase under long-term plant exclusion. There is now a need for increased focus on the microbial metabolic mechanisms which regulate the processing and persistence of enzymatically released compounds, particularly in energy limited soils.
