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Stocks and dynamics of SOC in relation to soil redistribution by water and tillage erosion

机译:SOC与水和耕作侵蚀对土壤再分配的影响

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Soil organic carbon (SOC) displaced by soil erosion is the subject of much current research and the fundamental question, whether accelerated soil erosion is a source or sink of atmospheric CO2, remains unresolved. A toposequence of terraced fields as well as a long slope was selected from hilly areas of the Sichuan Basin, China to determine effects of soil redistribution rates and processes on SOC stocks and dynamics. Soil samples for the determination of caesium-137 (Cs-137), SOC, total N and soil particle size fractions were collected at 5 m intervals along a transect down the two toposequences. Cs-137 data showed that along the long slope transect soil erosion occurred in upper and middle slope positions and soil deposition appeared in the lower part of the slope. Along the terraced transect, soil was lost over the upper parts of the slopes and deposition occurred towards the downslope boundary on each terrace, resulting in very abrupt changes in soil redistribution over short distances either side of terrace boundaries that run parallel with the contour on the steep slopes. These data reflect a difference in erosion process; along the long slope transect, water erosion is the dominant process, while in the terraced landscape soil distribution is mainly the result of tillage erosion. SOC inventories (mass per unit area) show a similar pattern to the Cs-137 inventory, with relatively low SOC content in the erosional sites and high SOC content in depositional areas. However, in the terraced field landscape C/N ratios were highest in the depositional areas, while along the long slope transect, C/N ratios were highest in the erosional areas. When the samples are subdivided based on Cs-137-derived erosion and deposition data, it is found that the erosional areas have similar C/N ratios for both toposequences, while the C/N ratios in depositional areas are significantly different from each other. These differences are attributed to the difference in soil erosion processes; tillage erosion is mainly responsible for high-SOC inventories at depositional positions on terraced fields, whereas water erosion plays a primary role in SOC storage at depositional positions on the long slope. These data support the theory that water erosion may cause a loss of SOC due to selective removal of the most labile fraction of SOC, while on the other hand tillage erosion only transports the soil over short distances with less effect on the total SOC stock.
机译:土壤侵蚀导致的土壤有机碳(SOC)是当前研究的主题,而加速土壤侵蚀是大气中CO 2的源还是汇的根本问题仍未解决。从中国四川盆地的丘陵地带选择了一定阶地和长坡度,以确定土壤再分配速率和过程对SOC储量和动力学的影响。沿两个正交样带以5 m的间隔收集用于测定铯137(Cs-137),SOC,总氮和土壤粒径分数的土壤样品。 Cs-137数据表明,沿长边坡断面,在上,中边坡位置均发生水土流失,而在边坡下部则出现土壤沉积。在梯田样带上,土壤流失在斜坡的上部,并且在每个梯田的下坡边界都发生了沉积,导致梯田边界两侧与梯田轮廓平行的短距离土壤重新分配发生了非常突然的变化。陡峭的斜坡。这些数据反映了侵蚀过程的差异。在长坡样带上,水土流失是主要过程,而在梯田景观中,土壤分布主要是耕作侵蚀的结果。 SOC清单(单位面积质量)显示出与Cs-137清单类似的模式,侵蚀位置的SOC含量相对较低,而沉积区域的SOC含量较高。然而,在梯田景观中,沉积区的碳氮比最高,而在长坡样带上,侵蚀区的碳氮比最高。当根据Cs-137得出的侵蚀和沉积数据对样品进行细分时,发现侵蚀面积的两个C / N比值相似,而沉积区域中的C / N比值却显着不同。这些差异归因于土壤侵蚀过程的差异。耕作侵蚀主要是造成梯田沉积位置高SOC的原因,而水蚀在长坡沉积位置的SOC储存中起主要作用。这些数据支持以下理论:水土流失可能由于选择性去除最不稳定的SOC部分而导致SOC损失,而另一方面,耕作侵蚀仅使土壤短距离运输,而对总SOC储量的影响较小。

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