Soil microbial biomass size and soil carbon influence the priming effect from carbon inputs depending on nitrogen availability. (April 2018)

• Record Type: Journal Article
• Authors: Li, Lu-Jun; Zhu-Barker, Xia; Ye, Rongzhong; Doane, Timothy A.; Horwath, William R.
• Is Part Of: Soil biology and biochemistry. Volume 119(2018)
• Page Start: 41
• Page End: 49
• Publication Date: 2018-04
• Subjects: Microbial biomass -- Microbial N mining -- Priming effect -- Ryegrass -- Soil organic carbon; Soil biochemistry -- Periodicals; Soil biology -- Periodicals; Sols -- Biochimie -- Périodiques; Sols -- Biologie -- Périodiques; Sols -- Microbiologie -- Périodiques; Bodembiologie; Biochemie; 631.46
• DOI: 10.1016/j.soilbio.2018.01.003
• Languages: English
• ISSNs: 0038-0717

Abstract

Abstract: Microbial biomass plays a critical role in soil organic carbon (SOC) mineralization. However, the effects of microbial biomass size on SOC mineralization are poorly understood. We investigated how the priming effect (PE) of plant residue inputs on native SOC mineralization responds to changes in microbial biomass size and nitrogen (N) availability in the same soil with a 23 y history of crops and grass cover with contrasting SOC contents. The size of the soil microbial biomass was changed by pre-incubating soils with glucose. The pre-incubated soils were then treated with 13 C-labeled ryegrass residue combined with or without N to determine the PE. In all soils, the addition of ryegrass residue significantly increased cumulative carbon dioxide (CO2 ) production, whereas the addition of N decreased it compared to the control (no ryegrass or N addition). After a 42-day incubation, only 9–16% of the ryegrass carbon (C) was mineralized to CO2, which contributed approximately 55 and 34% to the total CO2 production in crop and grass soils, respectively. The addition of N decreased CO2 production during the ryegrass decomposition by 9–45%, while the change in soil microbial biomass size had no impact. In addition, a positive PE was generally found in the soils amended with ryegrass alone, while the application of ryegrass residue combined with N decreased the PE. Moreover, the priming effect was independent of the size of the microbial biomass in crop soil. However, we observed a significant interaction of microbial biomass size and N availability on the priming effect in a grass soil but not in a crop soil. Our results indicate that soil microbial biomass size and soil C influence the magnitude and direction of the priming effect from C inputs depending on N availability. Highlights: N decreased CO2 production during ryegrass decomposition, while MB size had no impact. Ryegrass residue generally resulted in a positive soil C priming effect. N addition decreased priming effect of ryegrass residues on soil C. Microbial biomass size and soil C influence priming effect depending on N availability.