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Quantifying nutrient uptake as driver of rock weathering in forest ecosystems by magnesium stable isotopes

机译:镁稳定同位素量化营养吸收作为森林生态系统岩石风化的驱动因素

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Plants and soil microbiota play an active role in rock weathering and potentially couple weathering at depth with erosion at the soil surface. The nature of this coupling is still unresolved because we lacked means to quantify the passage of chemical elements from rock through higher plants. In a temperate forested landscape characterised by relatively fast (~?220?t?kmsup?2/sup?yrsup?1/sup) denudation and a kinetically limited weathering regime of the Southern Sierra Critical Zone Observatory (SSCZO), California, we measured magnesium (Mg) stable isotopes that are sensitive indicators of Mg utilisation by biota. We find that Mg is highly bio-utilised: 50–100?% of the Mg released by chemical weathering is taken up by forest trees. To estimate the tree uptake of other bio-utilised elements (K, Ca, P and Si) we compared the dissolved fluxes of these elements and Mg in rivers with their solubilisation fluxes from rock (rock dissolution flux minus secondary mineral formation flux). We find a deficit in the dissolved fluxes throughout, which we attribute to the nutrient uptake by forest trees. Therefore both the Mg isotopes and the flux comparison suggest that a substantial part of the major element weathering flux is consumed by the tree biomass. The enrichment of sup26/supMg over sup24/supMg in tree trunks relative to leaves suggests that tree trunks account for a substantial fraction of the net uptake of Mg. This isotopic and elemental compartment separation is prevented from obliteration (which would occur by Mg redissolution) by two potential effects. Either the mineral nutrients accumulate today in regrowing forest biomass after clear cutting, or they are exported in litter and coarse woody debris (CWD) such that they remain in qsolid/q biomass. Over pre-forest-management weathering timescales, this removal flux might have been in operation in the form of natural erosion of CWD. Regardless of the removal mechanism, our approach provides entirely novel means towards the direct quantification of biogenic uptake following weathering. We find that Mg and other nutrients and the plant-beneficial element Si (qbio-elements/q) are taken up by trees at up to 6?m depth, and surface recycling of all bio-elements but P is minimal. Thus, in the watersheds of the SSCZO, the coupling between erosion and weathering might be established by bio-elements that are taken up by trees, are not recycled and are missing in the dissolved river flux due to erosion as CWD and as leaf-derived bio-opal for Si. We suggest that the partitioning of a biogenic weathering flux into eroded plant debris might represent a significant global contribution to element export after weathering in eroding mountain catchments that are characterised by a continuous supply of fresh mineral nutrients.
机译:植物和土壤微生物群在岩石风化中起着积极的作用,并可能在深度风化与土壤表面的侵蚀相耦合。这种耦合的性质仍未解决,因为我们缺乏量化岩石中化学元素通过高等植物的通道的方法。在温带森林景观中,特征是相对较快的剥蚀作用(〜220?t?km ?2 ?yr ?1 ),并且南部塞拉利昂暴风雨的动力学受限制。加利福尼亚州的天文台(SSCZO),我们测量了镁(Mg)稳定同位素,这些同位素是生物群对镁利用的敏感指标。我们发现,镁是高度生物利用的:化学风化释放的镁中有50-100%由树木吸收。为了估计其他生物利用元素(钾,钙,磷和硅)的树木吸收量,我们将这些元素和镁在河流中的溶解通量与岩石中的溶解通量(岩石溶解通量减去次生矿物形成通量)进行了比较。我们发现整个溶解通量中存在赤字,这归因于林木对养分的吸收。因此,Mg同位素和通量比较都表明树木生物质消耗了大部分主要元素风化通量。相对于叶子,树干中 26 Mg超过 24 Mg的富集表明树干占Mg净吸收的很大一部分。通过两个潜在的作用,可以防止这种同位素和元素隔室的分离(由于镁的再溶解而导致的消失)。如今,矿物质养分要么在清除砍伐后积累在森林生物量的生长中,要么以凋落物和粗木屑(CWD)的形式出口,从而保留在固体生物量中。在森林管理前的风化历程中,这种清除通量可能以CWD的自然侵蚀形式运行。不论去除机理如何,我们的方法为风化后对生物摄取的直接定量提供了全新的手段。我们发现,Mg和其他养分以及植物有益元素Si( bio-elements )被树吸收的深度最大为6?m,所有生物元素的表面再循环,但P为最小的。因此,在SSCZO的流域中,侵蚀和风化之间的耦合可能是由树木吸收的生物元素建立的,这些元素未被循环利用,并且由于CWD和叶片衍生的侵蚀而在溶解的河流通量中丢失Si的生物蛋白石。我们建议将生物风化通量划分为侵蚀的植物残渣可能代表着侵蚀后的山区流域风化后对元素出口的重要全球贡献,这些山区流域的特征是不断供应新鲜的矿质营养素。

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