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铁同位素在北方腐殖质水中有机铁胶体的生物和光降解过程中的分馏作用。

Iron Isotope Fractionation during Bio- and Photodegradation of Organoferric Colloids in Boreal Humic Waters.

机构信息

Geosciences and Environment Toulouse (GET), UMR 5563 CNRS , 14 Avenue Edouard Belin , 31400 Toulouse , France.

Geological Faculty of Moscow State University , 1 Leninskie Gory , 119234 Moscow , Russia.

出版信息

Environ Sci Technol. 2019 Oct 1;53(19):11183-11194. doi: 10.1021/acs.est.9b02797. Epub 2019 Sep 17.

Abstract

Biodegradation and photolysis of dissolved organic matter (DOM) in boreal high-latitude waters are the two main factors controlling not only the aquatic fluxes and residence time of carbon but also metal nutrients associated with DOM such as Fe. The DOM is usually present in the form of organic and organomineral colloids, which also account for the majority of dissolved Fe. Here, we use the stable Fe isotope approach to unravel the processes controlling Fe behavior during bio- and photodegradation of colloids in boreal Fe- and DOM-rich humic waters (a stream and a fen). The adsorption of Fe colloids onto heterotrophic bacteria produced enrichment in +0.4‰ (δFe) in the heavier isotopes of the cell surface relative to the remaining solution. In contrast, long-term assimilation of Fe by live cells yielded preferential incorporation of lighter isotopes into the cells (-0.7‰ relative to aqueous solution). The sunlight-induced oxidation of Fe(II) in fen water led to the removal of heavier Fe isotopes (+1.5 to +2.5‰) from solution, consistent with Fe(III) hydroxide precipitation from Fe(II)-bearing solution. Altogether, bio- and photodegradation of organoferric colloids, occurring within a few days of exposure time, can produce several per mil isotopic excursions in shallow lentic and lothic inland waters of high-latitude boreal regions. Considerable daily scale variations of Fe isotopic composition should therefore be taken into account during the interpretation of the riverine flux of Fe isotopes to the ocean or tracing weathering processes using Fe isotopes in surface waters at high latitudes.

摘要

在高纬度北方水域中,溶解有机质(DOM)的生物降解和光解是控制碳的水相通量和停留时间以及与 DOM 相关的金属营养物(如 Fe)的两个主要因素。DOM 通常以有机和有机矿物胶体的形式存在,这些胶体也占溶解 Fe 的大部分。在这里,我们使用稳定的 Fe 同位素方法来揭示胶体在生物和光降解过程中控制 Fe 行为的过程,该胶体存在于富腐殖质的高纬度 Fe 和 DOM 水中(一条溪流和一个沼泽)。异养细菌产生的 Fe 胶体对 Fe 的吸附导致细胞表面相对于剩余溶液中较重同位素的富集(+0.4‰,δFe)。相比之下,活细胞对 Fe 的长期同化导致较轻同位素优先进入细胞(相对于水溶液为-0.7‰)。阳光诱导的沼泽水中 Fe(II)氧化导致溶液中较重的 Fe 同位素(+1.5 到+2.5‰)的去除,这与 Fe(II)承载溶液中 Fe(III)氢氧化物的沉淀一致。总之,在几天的暴露时间内,有机铁胶体的生物和光降解可以在高纬度北方浅水和深水内陆水中产生几个千分位的同位素偏移。因此,在解释河流向海洋输送 Fe 同位素或在高纬度地表水使用 Fe 同位素追踪风化过程时,应考虑到 Fe 同位素组成的每日尺度变化。

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