Soil water content was determined by oven-drying the samples at 105°C, and soil texture was analyzed using the pipette method (Gee and Bauder,1986) . Soil pH was measured using a fresh soil to water ratio of 1: 2.5 with a Delta pH-meter, and soil organic carbon (SOC) was determined using the K2CrO7 oxidation titration method (Walkley & Black 1934) . Total carbon (TC) and total nitrogen (TN) were measured on a
LECO macro-CN analyzer (LECO, St. Joseph, MI, USA). Inorganic N and labile carbon in the soils were extracted with 0.5 M K2SO4 in a ratio of 1:5 by shaking at 200 rpm for 1 h and filtered through 0.45-μm Millipore filter paper. Total C and N concentrations in the extracts were analyzed by TOC analyzer with total nitrogen unit (
TOC-L Analyzer, Shimadzu, Japan). In parallel, the carbon in microbial biomass (MBC) was determined using the fumigation-extraction method (Vance et al., 1987) . For each measurement of respiration rate, approximately 10 g of fresh soil (within 48 h after sampling) was incubated in a 120 ml container at 25 °C for 24 h. At the end of this period, CO2 concentrations in headspace were measured using an
Agilent-7890a gas chromatograph equipped with a flame ionization detector (FID) and an electron capture detector (ECD) (Agilent Technologies, Wilmington, DE, USA). Soil respiration rates were calculated from the net accumulation of CO2 over time.
Liu Y.R., Delgado-Baquerizo M., Wang J.T., Hu H.W., Yang Z, & He J.Z. (2018). New insights into the role of microbial community composition in driving soil respiration rates. Soil biology & biochemistry, 118.