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Soil Carbon Saturation: Linking Concept and Measurable Carbon Pools
Author(s) -
Stewart Catherine E.,
Plante Alain F.,
Paustian Keith,
Conant Richard T.,
Six Johan
Publication year - 2008
Publication title -
soil science society of america journal
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 0.836
H-Index - 168
eISSN - 1435-0661
pISSN - 0361-5995
DOI - 10.2136/sssaj2007.0104
Subject(s) - saturation (graph theory) , silt , chemistry , soil water , environmental chemistry , soil carbon , soil science , agroecosystem , environmental science , mineralogy , ecology , geology , biology , geomorphology , mathematics , combinatorics , agriculture
The soil C saturation concept suggests a limit to whole soil organic carbon (SOC) accumulation determined by inherent physicochemical characteristics of four soil C pools: unprotected, physically protected, chemically protected, and biochemically protected. Previous attempts to quantify soil C sequestration capacity have focused primarily on silt and clay protection and largely ignored the effects of soil structural protection and biochemical protection. We assessed two contrasting models of SOC accumulation, one with no saturation limit (i.e., linear first‐order model) and one with an explicit soil C saturation limit (i.e., C saturation model). We isolated soil fractions corresponding to the C pools (i.e., free particulate organic matter [POM], microaggregate‐associated C, silt‐ and clay‐associated C, and nonhydrolyzable C) from eight long‐term agroecosystem experiments across the United States and Canada. Due to the composite nature of the physically protected C pool, we fractioned it into mineral‐ vs. POM‐associated C. Within each site, the number of fractions fitting the C saturation model was directly related to maximum SOC content, suggesting that a broad range in SOC content is necessary to evaluate fraction C saturation. The two sites with the greatest SOC range showed C saturation behavior in the chemically, biochemically, and some mineral‐associated fractions of the physically protected pool. The unprotected pool and the aggregate‐protected POM showed linear, nonsaturating behavior. Evidence of C saturation of chemically and biochemically protected SOC pools was observed at sites far from their theoretical C saturation level, while saturation of aggregate‐protected fractions occurred in soils closer to their C saturation level.