Abstract

Multiple co-occurring environmental changes are affecting soil nitrogen cycling processes, which are mainly mediated by microbes. While it is likely that various nitrogen-cycling functional groups will respond differently to such environmental changes, very little is known about their relative responsiveness. Here we conducted four long-term experiments in a steppe ecosystem by removing plant functional groups, mowing, adding nitrogen, adding phosphorus, watering, warming, and manipulating some of their combinations. We quantified the abundance of seven nitrogen-cycling genes, including those for fixation (nifH), mineralization (chiA), nitrification (amoA of ammonia-oxidizing bacteria (AOB) or archaea (AOA)), and denitrification (nirS, nirK and nosZ). First, for each gene, we compared its sensitivities to different environmental changes and found that the abundances of various genes were sensitive to distinct and different factors. Overall, the abundances of nearly all genes were sensitive to nitrogen enrichment. In addition, the abundances of the chiA and nosZ genes were sensitive to plant functional group removal, the AOB-amoA gene abundance to phosphorus enrichment when nitrogen was added simultaneously, and the nirS and nirK gene abundances responded to watering. Second, for each single- or multi-factorial environmental change, we compared the sensitivities of the abundances of different genes and found that different environmental changes primarily affected different gene abundances. Overall, AOB-amoA gene abundance was most responsive, followed by the two denitrifying genes nosZ and nirS, while the other genes were less sensitive. These results provide, for the first time, systematic insights into how the abundance of each type of nitrogen-cycling gene and the equilibrium state of all these nitrogen-cycling gene abundances would shift under each single- or multi-factorial global change.

Highlights

  • Nitrogen (N) cycling is one of the most important ecosystem functions and most soil N-cycling processes are driven by microbes [1,2,3,4]

  • Three-way analysis of variance (ANOVA) revealed that the effect of plant functional groups (PFG) composition on the abundance of each N-cycling gene was non-significant (P.0.05)

  • One-way ANOVA showed that only the chiA and nosZ gene abundances were significantly different among the four PFG gradients (P,0.05; Fig. 2b1, g1)

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Summary

Introduction

Nitrogen (N) cycling is one of the most important ecosystem functions and most soil N-cycling processes are driven by microbes [1,2,3,4]. N fertilization/ deposition stimulates the production of excess NO3- by nitrifying microbes. This excess NO3- can be lost from soil by leaching, resulting in pollution of groundwater and eutrophication of lakes, estuaries, and coastal oceans [12,14]. It was found that the abundance of AOB decreased under elevated CO2 but increased under elevated precipitation, and that the decrease under elevated CO2 was even more pronounced when elevated precipitation concurred with elevated CO2 [8] Such studies suggest that for each type of Ncycling functional group, we should compare its sensitivity to different environmental changes. To detect or predict possible shifts of a given N-cycling process under multiple environmental changes in the future, our effort should be focused on the environmental change to which the particular microbial process of interest is more sensitive

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