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Soil organic carbon (SOC) content depends significantly upon changes in land use and vegetation cover. This study aimed to examine the redistribution of whole soil OC, water-soluble OC (WSOC), and different density-separated OC fractions in soil profiles of 0–100 cm under different land uses and to elaborate the mechanism of C sequestration in response to the land use change. The land use types include maize plots with or without chemical fertilizer application (i.e., Maize-nitrogen, phosphorus, and potassium (NPK) and Maize-NF plots), plots with vegetation removed (No Vegetation), plots with grass (Grass), and alfalfa plant (Alfalfa). These plots used to be maize cropping system with NPK fertilizer for many years before 2003. Significant difference in SOC content generally occurred in soil layers of 0–40 cm among the different plots after 11 years of land-use change. Long-term continuous maize planting decreased SOC content; the significant SOC decrease occurred in Maize plot in the range of 9.3–23.4% for different soil layers compared with the initial soil sampled in 2003. In addition, SOC in Maize plot decreased by 3.6% and 8.5% at top two soil layers, respectively, in comparison with No Vegetation plot. The similar reduction of OC was observed in heavy OC fractions. The calculated sensitivity index for OC decreased in the order of light fraction > water-soluble fraction > the whole soil > heavy fraction. Therefore, the young and labile carbon fractions are much sensitive to land use change relative to the old and recalcitrant carbon fractions. This study indicated that land use changes led to a redistribution of SOC in soil profile, particularly at top soil layers, and conversion from arable land to natural grass cover or nitrogen-fixation plant cultivation such as alfalfa led to the enrichment of SOC at different depths of soil profile.
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Hao et al. (2017) studied this question.
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