Sb(III) and Sb(V) retention by aptian sands: Quantitative insights into adsorption and heterogeneous redox reactions controlled by iron-containing minerals

IF 5.8 2区 地球科学 Q2 CHEMISTRY, PHYSICAL
Esra Orucoglu , Sylvain Grangeon , Nicolas Marty , Nicolas Maubec , Myriam Agnel , Benoit Madé , Mathieu Debure
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引用次数: 0

Abstract

The retention of Sb(III) and Sb(V) by Aptian sands, which contain quartz and glauconite, was investigated as a function of Sb concentration and with 7 d and 30 d contact time. Two samples, collected along a vertical profile, were used for the experiments. They originated from the capillary fringe (SCFr) and saturated (SSat) horizons and were respectively representative of oxidizing and reductive redox conditions. The Aptian sands had a lower retention capacity for Sb(V) than for Sb(III). Sb(V) distribution coefficients (Rd) ranged between 10 ± 3 L∙kg−1 and 13 ± 4 L∙kg−1 in SSat and between 11 ± 3 L∙kg−1 and 19 ± 4 L∙kg−1 in SCFr, after 7 d interaction. These values almost doubled when the interaction time was increased to 30 d and, in all conditions, Sb(V) was the only species detected in the aqueous solution. The evolution of Sb(III) Rd as a function of Sb equilibrium concentration and time was more complex. When contact time was 7 d, Rd first increased from 68 ± 7 L∙kg−1 ([Sb]eq = 2.2∙10−8 M) to 547 ± 33 L∙kg−1 ([Sb]eq = 1.4∙10−7 M) and then decreased down to 323 ± 21 L∙kg−1 ([Sb]eq = 1.1∙10−6 M) for SSat after 7 d of interaction. Sb(III) retention by SCFr was slightly lower: Rd increased from 15 ± 4 ([Sb]eq = 3.4∙10−8 M) to 174 ± 13 L∙kg−1 ([Sb]eq = 7.7∙10−7 M) and then decreased down to 137 ± 10 L∙kg−1 ([Sb]eq = 2.3∙10−6 M). While Sb(V) was the only species detected in the aqueous solution at lower concentrations, Sb(III) was increasingly present when added Sb(III) concentration increased, hence pointing out to heterogeneous redox interaction between Sb(III) and the solid phase that could be successfully modeled.
Overall, this study demonstrated that Sb(III) and Sb(V) retention depended on the speciation of added Sb, on the redox reactivity of the sand samples, and on contact time. Such results are a step forward to our capacity to model, and hence quantitatively predict, Sb mobility in the natural environment.
aptian砂对Sb(III)和Sb(V)的保留:含铁矿物控制的吸附和非均相氧化还原反应的定量分析
研究了含石英和海绿石的Aptian砂对Sb(III)和Sb(V)的保留率随Sb浓度、接触时间分别为7 d和30 d的变化规律。实验中使用了沿垂直剖面收集的两个样本。它们起源于毛细条纹层(SCFr)和饱和层(SSat),分别代表氧化和还原性氧化还原条件。Aptian砂对Sb(V)的截留能力低于Sb(III)。相互作用7 d后,Sb(V)分布系数(Rd)在SSat中介于10±3 L∙kg - 1和13±4 L∙kg - 1之间,在SCFr中介于11±3 L∙kg - 1和19±4 L∙kg - 1之间。当作用时间增加到30 d时,这些值几乎翻了一番,并且在所有条件下,Sb(V)是水溶液中唯一检测到的物质。Sb(III) Rd随平衡浓度和时间的变化更为复杂。当接触时间为7 d时,SSat的Rd首先从68±7 L∙kg - 1 ([Sb]eq = 2.2∙10−8 M)增加到547±33 L∙kg - 1 ([Sb]eq = 1.4∙10−7 M),然后在相互作用7 d后下降到323±21 L∙kg - 1 ([Sb]eq = 1.1∙10−6 M)。SCFr对Sb(III)的保留略低:Rd从15±4 ([Sb]eq = 3.4∙10−8 M)增加到174±13 L∙kg−1 ([Sb]eq = 7.7∙10−7 M),然后下降到137±10 L∙kg−1 ([Sb]eq = 2.3∙10−6 M)。而Sb(V)是低浓度水溶液中唯一检测到的物质,随着添加Sb(III)浓度的增加,Sb(III)的存在越来越多,从而指出Sb(III)与固相之间的非均相氧化还原相互作用可以成功地建模。总的来说,本研究表明Sb(III)和Sb(V)的保留取决于添加Sb的形态、砂样的氧化还原反应性和接触时间。这样的结果使我们的建模能力向前迈进了一步,从而可以定量预测Sb在自然环境中的迁移。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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来源期刊
Applied Clay Science
Applied Clay Science 地学-矿物学
CiteScore
10.30
自引率
10.70%
发文量
289
审稿时长
39 days
期刊介绍: Applied Clay Science aims to be an international journal attracting high quality scientific papers on clays and clay minerals, including research papers, reviews, and technical notes. The journal covers typical subjects of Fundamental and Applied Clay Science such as: • Synthesis and purification • Structural, crystallographic and mineralogical properties of clays and clay minerals • Thermal properties of clays and clay minerals • Physico-chemical properties including i) surface and interface properties; ii) thermodynamic properties; iii) mechanical properties • Interaction with water, with polar and apolar molecules • Colloidal properties and rheology • Adsorption, Intercalation, Ionic exchange • Genesis and deposits of clay minerals • Geology and geochemistry of clays • Modification of clays and clay minerals properties by thermal and physical treatments • Modification by chemical treatments with organic and inorganic molecules(organoclays, pillared clays) • Modification by biological microorganisms. etc...
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