Soil Biogeochemistry

Despite strong changes in the microbial community (observed through 16S rRNA gene and ITS amplicon sequencing), the microbial biomass C:N ratio did not change. N addition decreased microbial N acquisition as indicated by reduced leucine-aminopeptidase activity, and increased microbial net N mineralization. In contrast, predicted relative abundances of functional genes involved in degradation of labile C compounds (e.g. cellulose, hemicellulose, and chitin) as well as β-glucosidase and N-acetylglucosaminidase activities increased with elevated N availability. In combination, this pointed to a more intensive investment of microorganisms into C acquisition upon N addition. In contrast, N addition and associated soil acidification decreased microbial biomass and respiration and altered the community composition with prokaryotes being more affected than fungi. Nitrogen addition increased the relative abundance of gram-positive over gram-negative bacteria and favored taxa with low genome-size. Taken together, our findings support the concept that C and N cycling processes can be explained by the property of the soil microbial community to keep the element ratio of its biomass constant and by its reaction to soil acidification. Our findings suggest that predicted elevated N inputs might largely shape soil C and N cycling because the soil microbial community adjusts metabolic processes, which allows it to maintain its biomass stoichiometry constant.