Priming of soil organic carbon decomposition induced by corn compared to soybean crops

The rate of soil organic carbon [CS] loss via microbial respiration [decomposition rate k, y-1], and the rate of stabilization of vegetation inputs [CV] into CS [humification rate h, y-1] are usually considered independent of CV. However, short-term laboratory studies suggest that the quality and quantity of CV controls k, which is often referred to as a priming effect. We investigated how the chemical composition of different residues, [corn and soybean] controls k and h under field conditions in a no-till ecosystem. Using CV-driven shifts in ?13C, we estimated changes in carbon [C] stocks, k and h of both the labile particulate organic matter fraction [CPOM] and the stabilized mineral associated organic matter fraction [CMAOM]. After two years of high C inputs [corn: 4.4Mgha-1y-1 aboveground and C:N=78; soybean: 3.5Mgha-1y-1, C:N=17], we found no changes in CPOM and CMAOM stocks in the top 5-cm of soil or in deeper layers. However, CMAOM in corn had higher k [0.06y-1] and C output fluxes [0.67Mgha-1y-1] than in soybean [0.03y-1 and 0.32Mgha-1y-1], but similar rates and fluxes in CPOM in the top 5-cm of soil. In addition, while C inputs to CPOM were also similar for both crops, C inputs from CV to CMAOM were higher in corn [0.51Mgha-1y-1] than in soybean [0.19Mgha-1y-1]. Overall, corn plots had higher k and C inputs into CMAOM and therefore higher C cycling in this fraction. Our data suggests that the type of crop residue strongly influences C cycling in the topsoil of no-till cropping systems by affecting both the stabilization and the decomposition of soil organic matter.

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Bibliographic Details
Main Authors: Mazzilli, Sebastián R., Kemanian, Armen R., Ernst, Oswaldo, Jackson, Robert B., Piñeiro, Gervasio
Format: Texto biblioteca
Language:spa
Subjects:AGRICULTURAL WASTES, BIODEGRADATION, BIOGEOCHEMISTRY, BIOLOGICAL MATERIALS, CARBON FLUX, CHEMICAL COMPOSITION, COMPARATIVE STUDY, CORN, CROP RESIDUE, CROPS, DECOMPOSITION, HUMIFICATION, HUMIFICATION RATE, IN-FIELD, MAIZE, MICROBIAL ACTIVITY, ORGANIC COMPOUNDS, PARTICULATE ORGANIC MATTER, PRIMING EFFECT IN FIELD CONDITIONS, QUALITY CONTROL, SOIL CARBON, SOIL ORGANIC CARBON, SOIL ORGANIC CARBON DECOMPOSITION, SOIL ORGANIC MATTER, SOIL RESPIRATION, SOILS, SOYBEAN, STABILIZATION, TOPSOIL, ZERO TILLAGE, ,
Online Access:http://ceiba.agro.uba.ar/cgi-bin/koha/opac-detail.pl?biblionumber=47075
http://ceiba.agro.uba.ar/cgi-bin/koha/opac-detail.pl?biblionumber=
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Summary:The rate of soil organic carbon [CS] loss via microbial respiration [decomposition rate k, y-1], and the rate of stabilization of vegetation inputs [CV] into CS [humification rate h, y-1] are usually considered independent of CV. However, short-term laboratory studies suggest that the quality and quantity of CV controls k, which is often referred to as a priming effect. We investigated how the chemical composition of different residues, [corn and soybean] controls k and h under field conditions in a no-till ecosystem. Using CV-driven shifts in ?13C, we estimated changes in carbon [C] stocks, k and h of both the labile particulate organic matter fraction [CPOM] and the stabilized mineral associated organic matter fraction [CMAOM]. After two years of high C inputs [corn: 4.4Mgha-1y-1 aboveground and C:N=78; soybean: 3.5Mgha-1y-1, C:N=17], we found no changes in CPOM and CMAOM stocks in the top 5-cm of soil or in deeper layers. However, CMAOM in corn had higher k [0.06y-1] and C output fluxes [0.67Mgha-1y-1] than in soybean [0.03y-1 and 0.32Mgha-1y-1], but similar rates and fluxes in CPOM in the top 5-cm of soil. In addition, while C inputs to CPOM were also similar for both crops, C inputs from CV to CMAOM were higher in corn [0.51Mgha-1y-1] than in soybean [0.19Mgha-1y-1]. Overall, corn plots had higher k and C inputs into CMAOM and therefore higher C cycling in this fraction. Our data suggests that the type of crop residue strongly influences C cycling in the topsoil of no-till cropping systems by affecting both the stabilization and the decomposition of soil organic matter.