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Interaction of Arsenic Species with Organic Ligands: Competitive Removal from Water by Coagulation-Flocculation-Sedimentation (C/F/S)

机译:砷与有机配体的相互作用:通过混凝-絮凝-沉淀(C / F / S)从水中竞争去除

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摘要

The co-occurrence of arsenic (As) and organic ligands in water bodies has raised environmental concerns due to their toxicity and adverse effects on human health. The present study aims to elucidate the influences of hydrophobic/hydrophilic organic ligands, such as humic acid (HA) and salicylic acid (SA), on the interactive behavior of As species in water. Moreover, the competitive removal behaviors of As(III, V) species and total organic carbon (TOC) were systematically investigated by coagulation-flocculation-sedimentation (C/F/S) under various aqueous matrices. The results showed the stronger binding affinity of As(V) than As(III) species, with a higher complexation ability of hydrophobic ligands than hydrophilic. The media containing hydrophilic ligands require smaller ferric chloride (FC) doses to achieve the higher As(III, V) removal, while the optimum FC dose required for As(III) removal was found to be higher than that for As(V). Moreover, hydrophobic ligands showed higher TOC removal than hydrophilic ligands. The pronounced adverse effect of a higher concentration of hydrophobic ligands on the removal efficiencies of As(V) and TOC was observed. The adsorption of As(V) on Fe precipitates was better fitted with the Langmuir model but the Freundlich isotherm was more suitable for As(III) in the presence of hydrophilic SA. Moreover, TOC removal was substantially decreased in the As(V) system as compared to the As(III) system due to the dissolution of Fe precipitates at higher As(V) concentrations. The results of FC composite flocs demonstrated that the combined effect of oxidation, charge neutralization and adsorption played an important role in the removal of both toxicants during the C/F/S process. In summary, the findings of the present study provide insights into the fate, mobility and competitive removal behavior of As(III, V) species and organic ligands in the water treatment process.
机译:砷(As)和有机配体在水体中的共存由于其毒性和对人体健康的不利影响而引起了环境方面的关注。本研究旨在阐明疏水/亲水有机配体(如腐殖酸(HA)和水杨酸(SA))对水中As物种相互作用的影响。此外,通过在各种含水基质下进行混凝-絮凝-沉淀(C / F / S)系统研究了As(III,V)物种和总有机碳(TOC)的竞争去除行为。结果表明,As(V)的结合亲和力强于As(III)种类,疏水配体的络合能力高于亲水性。包含亲水性配体的介质需要较小的氯化铁(FC)剂量才能实现更高的As(III,V)去除,而发现As(III)去除所需的最佳FC剂量要高于As(V)。而且,疏水性配体显示出比亲水性配体更高的TOC去除率。观察到较高浓度的疏水配体对As(V)和TOC的去除效率有明显的不利影响。在Fe沉淀物上吸附As(V)更好地符合Langmuir模型,但在亲水性SA存在下,Freundlich等温线更适合于As(III)。此外,与As(III)体系相比,由于As(V)体系中Fe沉淀物在较高的As(V)浓度下溶解,TOC的去除量显着降低。 FC复合絮凝物的结果表明,在C / F / S过程中,氧化,电荷中和和吸附的综合作用在两种毒物的去除中都起着重要作用。总之,本研究的发现为水处理过程中As(III,V)物种和有机配体的命运,迁移性和竞争性去除行为提供了见识。

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