Grass root litter and soil carbon quality contrarily control Q10 of labile and recalcitrant carbon pools in a semi-arid inceptisol
摘要
The temperature sensitivity of labile (Q10L) and recalcitrant (Q10R) pools of soil organic carbon (SOC) decomposition is a critical for predicting soil carbon (C) fluxes.
MethodsSoils under six grass covers, namely, Cenchrus ciliaris, Chrysopogon fulvus, Panicum maximum, Sehima nervosa, Heteropogon contortus, and Vetiveria zizanioides from semi-arid India were evaluated for Q10L and Q10R of bulk soil, macroaggregates, microaggregates, and silt + clay associated SOC. Soil fractions (from 0–20 and 21–40 cm depths) were incubated at 25, 32, and 37 °C for 100 days, and cumulative C mineralization was measured. The Q10L and Q10R were calculated using a two-pool decay model. The quality of root litter C and SOC was assessed through FTIR spectroscopy.
ResultsQ10L and Q10R of microaggregate-C was significantly higher (22–64% and 22–24%, respectively) than macroaggregate-C and silt + clay-C. Among grasses, Q10L and Q10R values under C.ciliaris, H.contortus, and S. nervosa were lower (by 6–35%) than other grasses, indicating their capability to store SOC under global warming scenarios. Q10L at topsoil layer was correlated with root litter C quality (r = -0.641 to 0.633) and at the sub-surface soil layer, it was influenced by labile C concentration (r > 0.637). The Q10R was correlated with the recalcitrant C concentration (r > 0.721) and SOC quality in both soil layers, indicating that quality and availability of recalcitrant SOC had pivotal roles in governing Q10R in restored land.
ConclusionsSoil C and litter C quality should be potentially incorporated into the biogeochemical models to better predict SOC dynamics in managed ecosystems in the context of global warming and land use changes.