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钙质有机物质涂层会在碱性土壤中螯合铁载体。

Calcareous organic matter coatings sequester siderophores in alkaline soils.

机构信息

Environmental Molecular Sciences Laboratory, Pacific Northwest National Laboratory, Richland, WA 99354, United States of America; College of Earth, Ocean, Atmospheric Sciences, Oregon State University, Corvallis, OR 97331, United States of America.

Environmental Molecular Sciences Laboratory, Pacific Northwest National Laboratory, Richland, WA 99354, United States of America.

出版信息

Sci Total Environ. 2020 Jul 1;724:138250. doi: 10.1016/j.scitotenv.2020.138250. Epub 2020 Mar 26.

Abstract

Although most studies of organic matter (OM) stabilization in soils have focused on adsorption to aluminosilicate and iron-oxide minerals due to their strong interactions with organic nucleophiles, stabilization within alkaline soils has been empirically correlated with exchangeable Ca. Yet the extent of competing processes within natural soils remains unclear because of inadequate characterization of soil mineralogy and OM distribution within the soil in relation to minerals, particularly in C poor alkaline soils. In this study, we employed bulk and surface-sensitive spectroscopic methods including X-ray diffraction, Fe-Mössbauer, and X-ray photoemission spectroscopy (XPS), and transmission electron microscopy (TEM) methods to investigate the minerology and soil organic C and N distribution on individual fine particles within an alkaline soil. Microscopy and XPS analyses demonstrated preferential sorption of Ca-containing OM onto surfaces of Fe-oxides and calcite. This result was unexpected given that the bulk combined amounts of quartz and Fe-containing feldspars of the soil constitute ~90% of total minerals and the surface atomic composition was largely Fe and Al (>10% combined) compared to Ca (4.2%). Soil sorption experiments were conducted with two siderophores, pyoverdine and enterobactin, to evaluate the adsorption of organic molecules with functional groups that strongly and preferentially bind Fe. A greater fraction of pyoverdine was adsorbed compared to enterobactin, which is smaller, less polar, and has a lower aqueous solubility. Using NanoSIMS to map the distribution of isotopically-labeled siderophores, we observed correlations with Ca and Fe, along with strong isotopic dilution with native C, indicating associations with OM coatings rather than with bare mineral surfaces. We propose a mechanism of adsorption by which organics aggregate within alkaline soils via cation bridging, favoring the stabilization of larger molecules with a greater number of nucleophilic functional groups.

摘要

尽管大多数关于土壤中有机质(OM)稳定化的研究都集中在与有机亲核试剂的强相互作用有关的铝硅酸盐和氧化铁矿物的吸附上,但碱性土壤中的稳定化作用已经与可交换的 Ca 经验性相关。然而,由于对土壤矿物学和 OM 分布的描述不足,以及与矿物的关系,特别是在 C 贫乏的碱性土壤中,天然土壤中竞争过程的程度仍不清楚。在这项研究中,我们采用了包括 X 射线衍射、Fe-Mössbauer 和 X 射线光电子能谱(XPS)以及透射电子显微镜(TEM)在内的批量和表面敏感光谱方法,研究了碱性土壤中单个细颗粒内的矿物学以及土壤有机碳和氮的分布。显微镜和 XPS 分析表明,含有 Ca 的 OM 优先吸附在 Fe 氧化物和方解石的表面上。这一结果出人意料,因为土壤中石英和含 Fe 长石的总合量占总矿物质的~90%,而表面原子组成主要是 Fe 和 Al(>10%的总合),而不是 Ca(4.2%)。我们进行了两次铁载体(pyoverdine 和 enterobactin)的土壤吸附实验,以评估具有强烈和优先结合 Fe 的官能团的有机分子的吸附。与较小、极性较低且水溶性较低的 enterobactin 相比,pyoverdine 被吸附的比例更大。使用 NanoSIMS 对同位素标记的铁载体的分布进行映射,我们观察到与 Ca 和 Fe 的相关性,以及与天然 C 的强烈同位素稀释,这表明它们与 OM 涂层有关,而不是与裸露的矿物表面有关。我们提出了一种吸附机制,即有机物通过阳离子桥接在碱性土壤中聚集,有利于具有更多亲核官能团的较大分子的稳定化。

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