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Distribution of soil organic matter between fractions and aggregate size classes in grazed semiarid steppe soil profiles

机译:牧草半干旱草原剖面土壤有机质在组分和粒径类别之间的分布

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Grazed steppe ecosystems are discussed as one of the big global carbon sinks that may have the potential to sequester large amounts of atmospheric CO2 and mitigate the effects of global change if grazing is abandoned or management improved. But until today, little is known about sequestration potentials and stabilisation mechanisms in complete soil profiles of semiarid grasslands and how these systems react to grazing cessation. We applied a combined aggregate size, density and particle size fractionation procedure to sandy steppe soils under different grazing intensities (continuously grazed = Cg, winter grazing = Wg, ungrazed since 1999 = Ug99, ungrazed since 1979 = Ug79). Higher inputs of organic matter in ungrazed treatments led to higher amounts of OC in coarse aggregate size classes (ASC) and especially in particulate organic matter (POM) fractions across all depth. These processes started in the topsoil and took more than 5 years to reach deeper soil horizons (>10 cm). After 25 years of grazing cessation, subsoils showed clearly higher POM amounts. We found no grazing-induced changes of soil organic matter (SOM) quantity in fine ASC and particle size fractions. Current C-loading of fine particle size fractions was similar between differently grazed plots and decreased with depth, pointing towards free sequestration capacities in deeper horizons. Despite these free capacities, we found no increase in current C-loading on fine mineral soil fractions after 25 years of grazing exclusion. Silt and clay fractions appeared to be saturated. We suppose empirical estimations to overestimate sequestration potentials of particle size fractions or climatic conditions to delay the decomposition and incorporation of OM into these particle size fractions. POM quality was analysed using solid-state 13C NMR spectroscopy to clarify if grazing cessation changed chemical composition of POM in different ASC and soil depths via changing litter quality or changing decomposition dynamics. We found comparable POM compositions between different grazing intensities. POM is decomposed hierarchically from coarse to fine particles in all soil depths and grazing cessation has not affected the OM decomposition processes. The surplus of OM due to grazing cessation was predominately sequestered in readily decomposable POM fractions across all affected horizons. We question the long-term stabilisation of OM in these steppe soils during the first 25 years after grazing cessation and request more studies in the field of long-term OM stabilisation processes and assessment of carbon sequestration capacities to consider deeper soil horizons.
机译:放牧的草原生态系统被认为是全球最大的碳汇之一,如果放牧被放弃或管理得到改善,它们可能会隔离大量的大气CO 2 并减轻全球变化的影响。但是直到今天,人们对半干旱草原完整土壤剖面中的螯合潜力和稳定机制以及这些系统对放牧的反应知之甚少。我们对不同放牧强度的沙质草原土壤应用了组合的集料大小,密度和粒度分级程序(连续放牧= Cg,冬季放牧= Wg,自1999年以来未脱毛= Ug99,自1979年以来未脱毛= Ug79)。未磨砂处理中有机物的较高输入量会导致粗骨料尺寸类别(ASC)中的OC含量增加,尤其是在整个深度范围内的颗粒有机物(POM)分数中。这些过程始于表土,历时5年多才到达更深的土壤层(> 10 cm)。停止放牧25年后,底土的POM量明显增加。我们没有发现细ASC和粒径分数的放牧引起的土壤有机质(SOM)数量的变化。在不同的放牧地块之间,当前细颗粒级分的碳负荷相似,并且随着深度的增加而降低,这表明在更深的视野中存在游离固存能力。尽管有这些自由容量,但在排除放牧25年后,我们发现细矿质土壤上当前的碳负荷没有增加。淤泥和粘土部分似乎已饱和。我们假设经验估计高估了粒径分数或气候条件的螯合潜力,以延迟将OM分解和掺入这些粒径分数中。使用固态13 C NMR光谱分析了POM的质量,以阐明放牧是否通过改变凋落物质量或改变分解动力学来改变不同ASC和土壤深度下POM的化学成分。我们发现了不同放牧强度之间可比的POM组成。在所有土壤深度中,POM均从粗颗粒逐渐分解为细颗粒,并且放牧并未影响OM分解过程。在所有受影响的视野中,由于放牧而导致的多余有机物主要被隔离在易于分解的有机物组分中。我们质疑放牧后头25年内这些草原土壤中OM的长期稳定作用,并要求在长期OM稳定过程和碳封存能力评估领域进行更多研究,以考虑更深的土壤环境。

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