地下水水化学条件影响下微纳层状双金属氢氧化物(LDHs)对全氟辛酸(PFOA)的吸附性能与机制

Adsorption of Perfluorooctanoic Acid (PFOA) by Micro/Nanoscale Layered Double Hydroxides (LDHs) under Groundwater Hydrochemical Conditions: Performance and Mechanisms

  • 摘要: 全氟辛酸(PFOA)作为典型全氟及多氟烷基化合物(PFAS), 因难降解、迁移性强且在地下水等水环境中频繁检出, 具有潜在健康风险。吸附法因工艺简单、成本可控而成为去除PFAS的重要技术手段。在多种吸附材料中, 层状双金属氢氧化物(LDHs)因其层板带正电而具备良好的阴离子富集能力, 具有应用潜力。基于此, 本研究以Mg、Ni、Zn为二价金属元素, 以Al为三价金属元素, 采用尿素水解法制备MgAl-LDH、NiAl-LDH和ZnAl-LDH材料, 系统评价其在地下水环境相关浓度下对PFOA的吸附性能, 并结合地下水环境条件解析作用机制。结果表明, 3种LDHs均表现出快速吸附动力学, 30 min内即可达到平衡吸附量的95%以上; 等温吸附可由Langmuir模型较好描述, 其中NiAl-LDH表现最佳, qmax为1 483.46 μg·g-1, 分配系数(lg Kd, Kd单位为L·kg-1)为4.56。地下水相关因素实验显示: Cl-和NO3-(10 mg·L-1)、天然有机质(< 10 mg·L-1)以及共存典型PFAS对PFOA去除影响较小; HCO3-与SO42-(10 mg·L-1)则显著抑制吸附。结合3种LDHs性质表征结果、pH-Zeta电位响应与不同链长PFAS的去除差异可知, PFOA去除以静电吸引为主, 并叠加氢键、孔隙填充等非静电贡献。本研究结果阐明了LDHs在地下水相关水化学条件下去除PFOA的作用机制、吸附性能及环境适用性, 可为污染场地地下水中PFAS类污染物吸附材料的筛选及修复技术的选型提供理论依据与技术支撑。

     

    Abstract: Perfluorooctanoic acid (PFOA), a representative per- and polyfluoroalkyl substance (PFAS), has attracted widespread concern because of its extreme persistence, mobility, and frequent occurrence in groundwater and other aquatic environments, where it poses potential risks to health. Adsorption is considered a practical option for PFAS removal because of its operational simplicity and relatively low cost. Among available adsorbents, layered double hydroxides (LDHs), which possess positively charged metal hydroxide layers and exchangeable interlayer anions, exhibit strong affinity for anionic contaminants and therefore show promise for PFOA removal. In this study, MgAl-LDH, NiAl-LDH, and ZnAl-LDH were synthesized via a urea hydrolysis route using Mg, Ni, and Zn as divalent metals and Al as the trivalent metal. Their adsorption performance toward PFOA at groundwater-relevant concentrations was systematically evaluated, and the governing mechanisms were explored under representative groundwater geochemical conditions. All three LDHs showed rapid adsorption kinetics, reaching more than 95% of equilibrium uptake within 30 min. The adsorption data were well fitted by the Langmuir model, with NiAl-LDH exhibiting the highest adsorption capacity (qmax=1 483.46 μg·g-1) and affinity (lg Kd =4.56). Groundwater matrix experiments further showed that Cl- and NO3- (10 mg·L-1), natural organic matter (< 10 mg·L-1), and coexisting PFAS exerted only minor effects on PFOA removal, whereas HCO3- and SO42-(10 mg·L-1) significantly inhibited adsorption. Combined with the pH-dependent zeta potential responses and chain-length-dependent removal trends, these results indicate that PFOA adsorption is mainly driven by electrostatic attraction to positively charged surface sites, with additional contributions from non-electrostatic interaction such as hydrogen bonding and pore filling. Overall, this study clarifies the performance and environmental applicability of LDHs for PFOA removal under groundwater-relevant hydrochemical conditions and provides practical guidance for adsorbent selection and remediation strategy development at PFAS-impacted sites.

     

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