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Transformation of redox-sensitive to redox-stable iron-bound phosphorus in anoxic lake sediments under laboratory conditions

机译:实验室条件下氧氧沉积物中氧化还原氧化铁磷敏感的转化

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摘要

Phosphorus (P) can be retained in mineral association with ferrous iron (Fe) as vivianite, Fe(II)(3) (PO4)(2) center dot 8 H2O, in lake sediments. The mineral is formed and remains stable under anoxic non-sulphidogenic conditions and, therefore, acts as a long-term P sink. In laboratory experiments under anoxic conditions, we investigated whether P adsorbed to amorphous Fe(III)-hydroxide functioned as a precursor phase of vivianite when added to different sediments as a treatment. The untreated sediments served as controls and were naturally Fe-rich (559 mu mol/g DW) and Fe-poor (219 umol/g DW), respectively. The solid P binding forms analysed by sequential extraction and X-ray diffraction were related to coinciding pore water analyses and the bacterial community compositions of the sediments by bacterial 16S rRNA gene amplicon sequencing. In the treatments, within a period of 40 d, 70 % of the redox-sensitive Fe(III)-P was transformed into redox-stable P, which contained vivianite. The mineral was supersaturated in the pore water, but the presence of Fe(III)-P functioning as a precursor was sufficient for measurable vivianite formation. The composition of the microbial community did not differ significantly (PERMANOVA, p = 0.09) between treatment and control of the naturally Fe-rich sediment. In the naturally Fe-poor sediment, the microbial community changed significantly (PERMANOVA, p = 0.001) in response to the addition of Fe(III)-P to the sediment. The freshly formed redox-stable P was not retransferred to a redox-sensitive compound by aeration for 24 h until 90 % O-2 saturation was reached in the sediment slurry. We conclude that 1) Fe(III)-hydroxide bound P, resulting from oxic conditions at the sediment-water interface, is immobilised during anoxic conditions and stable even after re-oxygenation; 2) the process is feasible within the time scales of anoxic lake stratification periods; and 3) in relatively Fe-poor lakes, Fe dosing can provide excess Fe to form the precursor. (C) 2020 Elsevier Ltd. All rights reserved.
机译:磷(P)可与矿铁(Fe)保留在矿物联合中,作为Vivianite,Fe(II)(3)(PO4)(2)中心DOT 8 H2O,在湖泊沉积物中。在缺氧非硫化物疾病下形成矿物质并保持稳定,因此,作为长期P水槽作用。在缺氧条件下的实验室实验中,我们研究了当加入到不同沉积物作为治疗的不同沉积物时用作vivianite的前体阶段的无定形Fe(III) - 羟基的P.未处理的沉积物作为对照,分别是自然的Fe富含Fe的(559μmmol/ g)和Fe差(219umol / g dw)。通过顺序萃取和X射线衍射分析的固体P结合形式与细菌16SRRNA基因扩增子测序的重合孔隙水分析和沉积物的细菌群落组成有关。在治疗中,在40 d时,将70%的氧化还原敏感Fe(III)-P转化为含有vivianite的氧化芳烃稳定性p。将矿物质在孔隙水中饱和,但是Fe(III)-P作为前体的存在的存在足以进行可测量的育种形成。微生物群落的组成在天然Fe的富含沉积物的治疗和控制之间没有显着(vallova,p = 0.09)。在天然的Fe贫困沉积物中,微生物群体响应于沉积物的加入Fe(III)-P,微生物群体变化显着(vallova,p = 0.001)。通过通气将新鲜形成的氧化氧稳定性P未被曝气重新转移到氧化还原敏感化合物中,直至在沉积物浆料中达到90%O-2饱和度。我们得出结论,沉积物 - 水界面中的氧化条件导致的1)-Hy(III) - 羟基氧化物结合P在缺氧条件下固定,即使在再氧气后也稳定; 2)该过程在缺氧湖分层期的时间尺度范围内是可行的; 3)在相对的湖泊中,Fe计量可以提供过量的Fe以形成前体。 (c)2020 elestvier有限公司保留所有权利。

著录项

  • 来源
    《Water Research》 |2021年第1期|116609.1-116609.12|共12页
  • 作者单位

    Leibniz Inst Freshwater Ecol & Inland Fisheries I Dept Chem Analyt & Biogeochem Muggelseedamm 301 D-12587 Berlin Germany|Tech Univ Berlin Dept Urban Water Management Gustav Meyer Allee 25 D-13355 Berlin Germany;

    German Environm Agcy Umweltbundesamt Worlitzer Pl 1 D-06844 Dessau Rosslau Germany;

    Tech Univ Berlin Dept Environm Microbiol Ernst Reuter Pl 1 D-10587 Berlin Germany;

    Leibniz Inst Freshwater Ecol & Inland Fisheries I Dept Chem Analyt & Biogeochem Muggelseedamm 301 D-12587 Berlin Germany;

  • 收录信息 美国《科学引文索引》(SCI);美国《工程索引》(EI);
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    Iron hydroxide adsorbed phosphorus; vivianite; sink-switch; re-aeration; lake management; microbial community composition;

    机译:氢氧化铁吸附磷;vivianite;inf-switch;重新曝气;湖泊管理;微生物群落组成;

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