Nitrogen (N) deposition and climate warming are the two most important factors driving soil N2O emissions in terrestrial ecosystems. Both biotic and abiotic factors impact N cycling processes and functional gene abundances, but their global responses and patterns to mineral N addition and warming and the regulatory factors affecting N2O emissions remain unclear.
Global.
1986–2022.
Soil N2O emission, N functional gene abundances and edaphic factors.
We synthesised 5299 observations of soil N cycling processes, functional gene abundances and edaphic factors under mineral N addition and warming from 357 peer-reviewed publications worldwide.
We showed that mineral N addition and warming increased soil N2O emissions by 199.9% and 32.4%, respectively. N functional gene abundances, potential nitrification and denitrification rates were less sensitive to warming, and the responses of N2O emissions and N functional gene abundances were independent of biome, N form and warming method. Changes in N cycling processes and functional gene abundances are related to climates, edaphic factors and experimental manipulations, and spatial heterogeneity in the response of N2O emissions and N functional gene abundances to N addition and warming has been observed across the world. There was no clear relationship between changes in soil N2O emissions and N functional gene abundances despite the positive correlation between N functional gene abundances and potential nitrification and denitrification rates, but soil N2O emissions increased with increasing soil available N under both N addition and warming. Our results suggest that abiotic factors are the key reason for N-induced changes in N2O emissions.
Our findings indicate that N addition and warming substantially affect soil N2O emissions and highlight the urgent need to incorporate key abiotic factors and temperature-driven microbial kinetics of soil N2O emissions into theoretical and modelling research for predicting global N2O emissions.