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Land use change impact on soil carbon cycling and elemental budget.

机译:土地利用变化对土壤碳循环和元素预算的影响。

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Soil carbon cycling and elemental budget are known to be sensitive to land use types. Here we focused on the carbon translocation and long-term accumulation of elements in two adjacent forest and agricultural soils that share virtually identical environments. Soil mixing rates were calculated based on 210Pb radioactivity. The mixing velocities in A horizon range from 0.1 to 0.7 cm yr-1 in the forest soil and from 1 to 10 cm yr-1 in the agricultural soil. The turnover times of organic carbon by mixing in A horizons are decadal in the forest but seasonal in the agricultural soil, indicating that the agricultural soils' low carbon content is partially due to the loss of the labile carbon pool of which decomposition is facilitated by the mixing. In another translocation mechanism, podzolization, the amounts of organically complexed and inorganic amorphous and pedogenic crystalline Fe and Al are all significantly lower in the agricultural soil. For a given organically complexed Fe and Al, smaller amounts of organic carbon are complexed in the agricultural soil. The reduction of organic carbon content and the increase of soil pH via liming in the agricultural soil have reduced the podzolization. A geochemical mass balance approach was employed in order to quantify the mass losses or gains via chemical weathering over the course of soil formation under the two land use types. Zirconium is used as an index element. The two soils and their underlying parent materials have identical X-ray diffraction-based mineralogy, supporting the assumptions that the two soils are developed in-situ from identical parent materials and that aeolian inputs can be ignored. Calculated fractional mass losses or gains show that the agricultural soil has net mass gains in Ca, Mg, Na and P relative to its parent material, while the forest soils show losses or less gain in the nutrient elements. Heavy metals such as Cr, Cu, Ni, Pb, Zn and Co are more enriched in the agricultural soil than in the forest soil. This showed that the accumulation of nutrient elements and incorporation of heavy metals by agricultural activities.
机译:已知土壤碳循环和元素预算对土地利用类型敏感。在这里,我们重点研究了碳在相邻的两个森林和农业土壤中的碳迁移和元素的长期积累,这些土壤和土壤共享相同的环境。土壤混合速率是根据210Pb放射性计算的。森林土壤中A层的混合速度为0.1至0.7 cm yr-1,农业土壤中为1至10 cm yr-1。在A层混合产生的有机碳周转时间在森林中是十年,但在农业土壤中是季节性的,这表明农业土壤的低碳含量部分是由于不稳定碳库的损失,而碳的分解有利于分解。混合。在另一种易位机理中,在农业土壤中,过磷酸化作用,有机复合物,无机无定形和成岩性结晶铁和铝的含量均显着降低。对于给定的有机络合的铁和铝,农业土壤中络合的有机碳量较少。通过在农业土壤中撒石灰来减少有机碳含量和增加土壤pH值,已经减少了过土壤化作用。为了量化两种土地利用类型下土壤形成过程中化学风化引起的质量损失或增加,采用了一种地球化学质量平衡方法。锆用作指标元素。两种土壤及其潜在的母体材料具有相同的基于X射线衍射的矿物学,支持以下假设:两种土壤是从相同的母体材料中原位发育的,而风积输入可忽略不计。计算得出的部分质量损失或增加值表明,相对于其母质,农业土壤的钙,镁,钠和磷净质量增加,而森林土壤的营养元素损失或更少。 Cr,Cu,Ni,Pb,Zn和Co等重金属在农业土壤中比在森林土壤中富集更多。这表明营养成分的积累和农业活动对重金属的吸收。

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