Global patterns of soil gross immobilization of ammonium and nitrate in terrestrial ecosystems.

Microbial nitrogen (N) immobilization, which typically results in soil N retention but based on the balance of gross N immobilization over gross N production, affects the fate of the anthropogenic reactive N. However, global patterns and drivers of soil gross immobilization of ammonium (I ) and nitrate (I ) are still only tentatively known. Here, we provide a comprehensive analysis considering gross N production rates, soil properties, and climate and their interactions for a deeper understanding of the patterns and drivers of I and I . By compiling and analyzing 1966 observations from 274 N-labelled studies, we found a global average of I and I of 7.41 ± 0.72 and 2.03 ± 0.30 mg N kg  day with a ratio of I to I (I :I ) of 0.79 ± 0.11. Soil I and I increased with increasing soil gross N mineralization (GNM) and nitrification (GN), microbial biomass, organic carbon, and total N and decreasing soil bulk density. Our analysis revealed that GNM and GN were the main stimulators for I and I , respectively. The structural equation modeling showed that higher soil microbial biomass, total N, pH, and precipitation stimulate I and I through enhancing GNM and GN. However, higher temperature and soil bulk density suppress I and I by reducing microbial biomass and total N. Soil I varied with terrestrial ecosystems, being greater in grasslands and forests, which have higher rates of GNM, than in croplands. The highest I :I was observed in croplands, which had higher rates of GN. The global average of GN to I was 2.86 ± 0.31, manifesting a high potential risk of N loss. We highlight that anthropogenic activities that influence soil properties and gross N production rates likely interact with future climate changes and land uses to affect soil N immobilization and, eventually, the fate of the anthropogenic reactive N.