While the magnetite stoichio'/> Influence of Magnetite Stoichiometry on the Binding of Emerging Organic Contaminants
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Influence of Magnetite Stoichiometry on the Binding of Emerging Organic Contaminants

机译:磁铁矿化学计量对新兴有机污染物结合的影响

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src="http://pubs.acs.org/appl/literatum/publisher/achs/journals/content/esthag/2018/esthag.2018.52.issue-2/acs.est.7b04849/20180111/images/medium/es-2017-04849k_0005.gif">While the magnetite stoichiometry (i.e., Fe(II)/Fe(III) ratio) has been extensively studied for the reductive transformation of chlorinated or nitroaromatic compounds, no work exists examining the influence of stoichiometry of magnetite on its binding properties. This study, for the first time, demonstrates that the stoichiometry strongly affects the capacity of magnetite to bind not only quinolone antibiotics such as nalidixic acid (NA) and flumequine (FLU), but also salicylic acid (SA), natural organic matter (humic acid, HA), and dissolved silicates. Fe(II)-amendment of nonstoichiometric magnetite (Fe(II)/Fe(III) = 0.40) led to similar sorbed amounts of NA, FLU, SA, silicates or HA as compared to the stoichiometric magnetite (i.e., Fe(II)/Fe(III) = 0.50). At any pH between 6 and 10, all magnetites exhibiting similar Fe(II)/Fe(III) ratio in the solid phase showed similar adsorption properties for NA or FLU. This enhancement in binding capability of magnetite for NA is still observed in the presence of environmentally relevant ligands (e.g., 10 mg L–1 of HA or 100 μM of silicates). Using surface complexation modeling, it was shown that the NA–magnetite complexation constant does not vary with Fe(II)/Fe(III) between 0.24 and 0.40, but increases by 8 orders of magnitude when Fe(II)/Fe(III) increases from 0.40 to 0.50.
机译:src =“ http://pubs.acs.org/appl/literatum/publisher/achs/journals/content/esthag/2018/esthag.2018.52.issue-2/acs.est.7b04849/20180111/images/medium /es-2017-04849k_0005.gif“>磁铁矿的化学计量比(即Fe(II)/ Fe(III)比)已被广泛研究用于氯代或硝基芳族化合物的还原转化,但目前尚无任何工作可检验化学计量比的影响。磁铁矿对其结合性能的影响。这项研究首次表明,化学计量学强烈影响磁铁矿结合能力,不仅结合喹诺酮类抗生素(如萘啶酸(NA)和氟美喹嗪(FLU)),而且还结合水杨酸(SA),天然有机物(腐殖质)酸,HA)和溶解的硅酸盐。与化学计量磁铁矿(即Fe(II))相比,非化学计量磁铁矿的Fe(II)修正(Fe(II)/ Fe(III)= 0.40)导致相似的NA,FLU,SA,硅酸盐或HA吸附量/ Fe(III)= 0.50)。在6至10之间的任何pH值下,所有在固相中表现出相似的Fe(II)/ Fe(III)比的磁铁矿均显示出相似的对NA或FLU的吸附特性。在与环境相关的配体(例如10 mg L HA或100μM硅酸盐)存在下,磁铁矿对NA的结合能力仍得到了增强。使用表面络合模型,表明NA-磁铁矿络合常数在0.24至0.40之间随Fe(II)/ Fe(III)的变化而变化,但当Fe(II)/ Fe(III)时增加了8个数量级。从0.40增加到0.50。

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  • 来源
    《Environmental Science & Technology》 |2018年第2期|467-473|共7页
  • 作者单位

    École Nationale Supérieure de Chimie de Rennes, UMR CNRS 6226, 11 Allée de Beaulieu, 35708 Rennes Cedex 7, France;

    École Nationale Supérieure de Chimie de Rennes, UMR CNRS 6226, 11 Allée de Beaulieu, 35708 Rennes Cedex 7, France,Géosciences Rennes, UMR 6118 CNRS, Université Rennes 1, Campus de Beaulieu, 35042 Rennes Cedex, France;

    École Nationale Supérieure de Chimie de Rennes, UMR CNRS 6226, 11 Allée de Beaulieu, 35708 Rennes Cedex 7, France;

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