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  • 1.
    Li, H.
    et al.
    Research Group of Soil Fertility and Nutrient Management, Department of Environment, Ghent University, Coupure Links 653, Ghent, 9000, Belgium.
    Françoys, A.
    Isotope Bioscience Laboratory, Department of Green Chemistry and Technology, Ghent University, Coupure Links 653, Ghent, 9000, Belgium.
    Wang, Xiaolin
    Mälardalen University, School of Business, Society and Engineering, Future Energy Center.
    Zhang, S.
    SLU Swedish Species Information Center, Swedish University of Agricultural Sciences, Uppsala, 75007, Sweden.
    Mendoza, O.
    School of Architecture, Civil and Environmental Engineering EPFL, Lausanne, 1015, Switzerland.
    De Neve, S.
    Research Group of Soil Fertility and Nutrient Management, Department of Environment, Ghent University, Coupure Links 653, Ghent, 9000, Belgium.
    Dewitte, K.
    Department of Plants and Crops, Ghent University, Coupure Links 653, Ghent, 9000, Belgium.
    Sleutel, S.
    Research Group of Soil Fertility and Nutrient Management, Department of Environment, Ghent University, Coupure Links 653, Ghent, 9000, Belgium.
    Field-scale assessment of direct and indirect effects of soil texture on organic matter mineralization during a dry summer2023In: Science of the Total Environment, ISSN 0048-9697, E-ISSN 1879-1026, Vol. 899, article id 165749Article in journal (Refereed)
    Abstract [en]

    Soil texture plays a crucial role in organic matter (OM) mineralization through both direct interactions with minerals and indirect effects on soil moisture. Separating these effects could enhance the modelling of soil organic carbon (SOC) dynamics under climate change scenarios. However, the attempts have been limited small-scale experiments. Here, we studied the effects of soil texture on added OM mineralization in loamy sand, loam and silt loam soils in nine agricultural fields in Flanders, Belgium. Soil moisture, temperature, groundwater table depth and the mineralization of 13C-labeled ryegrass were monitored in buried mesocosms for approximately three months during a dry summer. Ryegrass-C mineralization was lowest in the loamy sand (39 ± 7 %) followed by silt loam (48 ± 7 %) and loam (63 ± 5 %) soils, challenging the current clay%-based moderation of C-mineralization rates in soil models. Soil temperature was not influenced by soil texture, whereas soil moisture was indeed dependent on soil texture. It appears that capillarity sustained upward water supply from groundwater to the topsoil in loam and silt loam soils but not in loamy sand soil, although this difference in capillary rise could not fully explain the higher moisture content in loam than that in silt loam soils. Additionally, soil texture only impacted remnant added ryegrass pieces (>500 μm) but not the finer ryegrass-derived SOC (<500 μm), which might point at the important indirect control of texture on OM mineralization during prolonged summer drought. However, these effects are only manifested during drought when no other factors (e.g., groundwater depth or subsurface water flows) exert an overriding impact on the soil water balance. Overall, our findings highlight the need to properly incorporate the indirect effects of soil texture on OM mineralization into soil carbon models to accurately predict soil C stocks under future climate change scenarios.

  • 2.
    Zhang, X.
    et al.
    State Key Laboratory of Soil Erosion and Dryland Farming on the Loess Plateau, Northwest A&F University, Shaanxi, Yangling, 712100, China.
    Zheng, J.
    State Key Laboratory of Soil Erosion and Dryland Farming on the Loess Plateau, Northwest A&F University, Shaanxi, Yangling, 712100, China.
    Wang, K.
    State Key Laboratory of Soil Erosion and Dryland Farming on the Loess Plateau, Northwest A&F University, Shaanxi, Yangling, 712100, China.
    Wang, Xiaolin
    Mälardalen University, School of Business, Society and Engineering, Future Energy Center.
    Zhang, Z.
    State Key Laboratory of Soil Erosion and Dryland Farming on the Loess Plateau, Northwest A&F University, Shaanxi, Yangling, 712100, China.
    Xie, X.
    State Key Laboratory of Soil Erosion and Dryland Farming on the Loess Plateau, Northwest A&F University, Shaanxi, Yangling, 712100, China.
    Cai, J.
    Institute of Resources and Environment, Ningxia Academy of Agriculture and Forestry Sciences, Yinchuan, 750002, China.
    Greater mineral and aggregate protection for organic carbon in the soil amended by weathered coal than by biochar: Based on a 3-year field experiment2023In: Geoderma, ISSN 0016-7061, E-ISSN 1872-6259, Vol. 438, article id 116639Article in journal (Refereed)
    Abstract [en]

    Soil carbon pool stability plays an important role in reaching carbon neutrality and mitigating global warming. Applying soil amendments is a practical strategy in agricultural production to improve soil environment. Weathered coal (WC) is an organic amendment that can be used to improve soil quality. However, the effects of WC application on soil organic carbon pool stability, and its differences from the effects of biochar (BC, a common amendment) application remains unclear. In this study, BC was selected as a comparison to further evaluate the potential of WC based on a 3-year field experiment, in which WC and BC were individually applied into a loamy clay soil at 0%, 1%, and 3% (w/w) rates. Soil organic carbon and its fractions (including particulate organic carbon and mineral-bound organic carbon), soil aggregate fractions and its stability, and the organic carbon content in aggregates were examined. The results showed that both WC and BC significantly increased soil total organic carbon, particulate and mineral-bound organic carbon (P < 0.05). The mineral-bound organic carbon content in WC treatment was significantly higher than that in BC treatment (by 32% under the 3% rate) (P < 0.05), whereas, there were no significant differences in soil total organic carbon content. Both WC and BC increased the soil organic carbon content in all aggregate fractions. While only the WC improved the soil aggregate stability, and which was 15% (under 1% rate) and 28% (under 3% rate) higher in WC treatments than in BC treatments (P < 0.05). The proportion of mineral-bound organic carbon to soil total organic carbon content and the soil aggregate stability were obviously related the soil C/N, and the WC treatments had a higher proportion of mineral-bound organic carbon and soil aggregate stability than BC treatments under the same soil C/N. The results indicated that the application of WC may be more effective than BC in increasing mineral and aggregate protection for soil organic carbon and thus improving soil carbon pool stability. Additionally, the purchase cost of WC was clearly lower than that of BC. Combined with the low cost and the benefits in soil structure and carbon pool stability, the application of WC appeared to have advantages over BC. Our findings provide robust evidence that WC is more effective than BC in improving soil carbon pool stability. 

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