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A step towards a holistic assessment of soil degradation in Europe: Coupling on-site erosion with sediment transfer and carbon fluxes

机译:欧洲全面评估土壤退化的步骤:将现场侵蚀与沉积物转移和碳通量耦合

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摘要

Soil degradation due to erosion is connected to two serious environmental impacts: (i) on-site soil loss and (ii) off-site effects of sediment transfer through the landscape. The potential impact of soil erosion processes on biogeochemical cycles has received increasing attention in the last two decades. Properly designed modelling assumptions on effective soil loss are a key pre-requisite to improve our understanding of the magnitude of nutrients that are mobilized through soil erosion and the resultant effects. The aim of this study is to quantify the potential spatial displacement and transport of soil sediments due to water erosion at European scale. We computed long-term averages of annual soil loss and deposition rates by means of the extensively tested spatially distributed WaTEM/SEDEM model. Our findings indicate that soil loss from Europe in the riverine systems is about 15% of the estimated gross on-site erosion. The estimated sediment yield totals 0.164 ± 0.013 Pg yr−1 (which corresponds to 4.62 ± 0.37 Mg ha−1 yr−1 in the erosion area). The greatest amount of gross on-site erosion as well as soil loss to rivers occurs in the agricultural land (93.5%). By contrast, forestland and other semi-natural vegetation areas experience an overall surplus of sediments which is driven by a re-deposition of sediments eroded from agricultural land. Combining the predicted soil loss rates with the European soil organic carbon (SOC) stock, we estimate a SOC displacement by water erosion of 14.5 Tg yr−1. The SOC potentially transferred to the riverine system equals to 2.2 Tg yr−1 (~15%). Integrated sediment delivery-biogeochemical models need to answer the question on how carbon mineralization during detachment and transport might be balanced or even off-set by carbon sequestration due to dynamic replacement and sediment burial.
机译:侵蚀造成的土壤退化与两个严重的环境影响有关:(i)现场土壤流失和(ii)沉积物通过景观的非现场影响。在过去的二十年中,土壤侵蚀过程对生物地球化学循环的潜在影响越来越受到关注。正确设计有效土壤流失的建模假设,是增进我们对通过土壤侵蚀而动员的养分数量及其后果的理解的关键前提。这项研究的目的是在欧洲范围内量化由于水蚀造成的土壤沉积物潜在的空间位移和迁移。我们通过广泛测试的空间分布WaTEM / SEDEM模型,计算了年度土壤流失和沉积速率的长期平均值。我们的发现表明,欧洲河流系统中的土壤流失约占现场总侵蚀量的15%。在侵蚀中估算的沉积物总产量为0.164±0.013 Pg yr -1 (相当于4.62±0.37 Mg ha -1 yr -1 区域)。在农田中,最大的现场侵蚀和土壤流失最多(93.5%)。相比之下,林地和其他半天然植被区的沉积物总体过剩,这是由从农业土地侵蚀下来的沉积物的重新沉积所驱动的。结合预测的土壤流失率和欧洲土壤有机碳(SOC),我们估计因水蚀造成的SOC位移为14.5 Tg yr -1 。可能转移到河流系统的SOC等于2.2 Tgyryr -1 (〜15%)。综合的沉积物输送-生物地球化学模型需要回答以下问题:在分离和运输过程中,由于动态置换和沉积物埋藏,碳固存如何平衡甚至抵消碳矿化。

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