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在 pH 值逐渐增加的条件下,腐殖酸的存在逐渐稳定针铁矿,从而增强了饱和介质中镉的固定。

Enhanced cadmium immobilization in saturated media by gradual stabilization of goethite in the presence of humic acid with increasing pH.

机构信息

Agro-Environmental Protection Institute, Ministry of Agriculture, Tianjin 300191, China.

Agro-Environmental Protection Institute, Ministry of Agriculture, Tianjin 300191, China; College of Natural Resources and Environment, South China Agricultural University, Guangzhou 510642, China.

出版信息

Sci Total Environ. 2019 Jan 15;648:358-366. doi: 10.1016/j.scitotenv.2018.08.086. Epub 2018 Aug 7.

Abstract

Goethite (Gt) and humic acid (HA) are important components of soil that significantly affect Cd mobility. In this study, the co-transport of Cd and Gt with/without HA in saturated sand columns was investigated by monitoring the breakthrough curves at different pH values. A solute transport model was used to study Cd transport and retention in the saturated sand in the presence of Gt and HA, and a colloid transport model was used to describe the Gt colloid (Gt) transport in the columns. Our results showed that the transport behaviors of Cd and Gt colloids/aggregates were regulated by pH. Cadmium transport was significantly inhibited at high pH due to its adsorption on the sand and Gt. Moreover, Gt retention was gradually stabilized with increasing pH regardless of its forms, i.e., individual colloids (Gt) or larger assemblages of particles due to aggregation (Gt). This retention was obviously enhanced in the presence of HA. Thus, the superposition of increased Cd adsorption on Gt and Gt retention (stabilization) enhanced the immobilization of Cd at high pH. In addition to stabilizing Gt, HA further enhance Cd adsorption on Gt, thus promoting Cd immobilization. However, only a small amount of organic-matter-bound Cd was observed in the columns with injected HA. The major fractions of retained Cd were exchangeable Cd and Fe-oxide-bound Cd. Our results provide new insights into the roles of Gt and HA in the transport and mobilization of Cd in soil-groundwater systems.

摘要

针铁矿(Gt)和腐殖酸(HA)是土壤的重要组成部分,它们显著影响 Cd 的迁移性。在这项研究中,通过监测不同 pH 值下的穿透曲线,研究了 Cd 与 Gt 以及有/无 HA 在饱和砂柱中的共运移。采用溶质运移模型研究了 Gt 和 HA 存在下饱和砂中 Cd 的运移和保留,采用胶体运移模型描述了柱中 Gt 胶体(Gt)的运移。结果表明,Cd 和 Gt 胶体/聚集体的运移行为受 pH 调节。由于 Cd 在砂和 Gt 上的吸附,Cd 的运移在高 pH 下受到显著抑制。此外,无论 Gt 的形式是单个胶体(Gt)还是更大的颗粒聚集体(Gt),Gt 的保留都随着 pH 的增加而逐渐稳定,这是由于团聚作用。在 HA 的存在下,这种保留作用明显增强。因此,Cd 在 Gt 上的吸附增加和 Gt 的保留(稳定)的叠加增强了 Cd 在高 pH 下的固定化。除了稳定 Gt 之外,HA 还进一步促进了 Cd 在 Gt 上的吸附,从而促进了 Cd 的固定化。然而,在注入 HA 的柱中仅观察到少量有机物质结合的 Cd。保留的 Cd 的主要部分是可交换 Cd 和铁氧化物结合的 Cd。研究结果为 Gt 和 HA 在土壤-地下水系统中 Cd 的迁移和活化作用提供了新的认识。

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