College of Environmental Science and Engineering, Hunan University, Changsha, 410082, China; Key Laboratory of Environmental Biology and Pollution Control (Hunan University), Ministry of Education, Changsha, 410082, China.
College of Environmental Science and Engineering, Hunan University, Changsha, 410082, China; Key Laboratory of Environmental Biology and Pollution Control (Hunan University), Ministry of Education, Changsha, 410082, China.
Environ Pollut. 2024 Nov 15;361:124815. doi: 10.1016/j.envpol.2024.124815. Epub 2024 Aug 27.
In this study, the impact of surfactants on the adsorption behavior of Pb(II) onto microplastics-sediment (MPs-S) complexes was investigated. Firstly, virgin polyamide (VPA) and polyethylene (VPE) were placed in Xiangjiang River sediment for six months to conduct in-situ aging. The results indicated that the biofilm-developed polyamide (BPA) and polyethylene (BPE) formed new oxygen-containing functional groups and different biofilm species. Furthermore, the adsorption capacity of Pb(II) in sediment (S) and MPs-S complexes was in the following order: S > BPA-S > VPE-S > VPA-S > BPE-S. The addition of sodium dodecyl benzenesulfonate (SDBS) promoted the adsorption of Pb(II), and the adsorption amount of Pb(II) increased with the higher concentration of SDBS, while adding cetyltrimethylammonium bromide (CTAB) showed the opposite result. The adsorption process of MPs-S complexes to Pb(II) was dominated by chemical adsorption, and the interaction between MPs-S complexes and Pb(II) was multilayer adsorption involving physical and chemical adsorption when the surfactants were added. Besides, the pH exerts a significant effect on Pb(II) adsorption in different MPs-S complexes, and the highest adsorption amount occurred at pH 6. Noteworthy, CTAB promoted the adsorption ability of Pb(II) when the exogenous FA was added. The binding characteristic of sediment endogenous DOM components and Pb(II) was influenced by the addition of MPs and surfactants. Finally, it confirmed that adsorption mechanisms mainly involve electrostatic and hydrophobic interaction. This study provides a new perspective to explore the environmental behaviors of Pb(II) by MPs and sediments with the addition of surfactants, which was conducive to evaluating the ecological risks of MPs and heavy metals in aquatic environments.
在这项研究中,研究了表面活性剂对 Pb(II) 吸附到微塑料-沉积物(MPs-S)复合物的影响。首先,将新的聚酰胺(VPA)和聚乙烯(VPE)放置在湘江沉积物中进行原位老化 6 个月。结果表明,生物膜形成的聚酰胺(BPA)和聚乙烯(BPE)形成了新的含氧官能团和不同的生物膜物种。此外,沉积物(S)和 MPs-S 复合物中 Pb(II)的吸附能力顺序为:S>BPA-S>VPE-S>VPA-S>BPE-S。十二烷基苯磺酸钠(SDBS)的添加促进了 Pb(II)的吸附,吸附量随 SDBS 浓度的增加而增加,而添加十六烷基三甲基溴化铵(CTAB)则表现出相反的结果。MPs-S 复合物对 Pb(II)的吸附过程主要是化学吸附,当添加表面活性剂时,MPs-S 复合物与 Pb(II)之间的相互作用是涉及物理和化学吸附的多层吸附。此外,pH 值对不同 MPs-S 复合物中 Pb(II)的吸附有显著影响,在 pH 6 时吸附量最高。值得注意的是,当添加外源性 FA 时,CTAB 促进了 Pb(II)的吸附能力。添加 MPs 和表面活性剂会影响沉积物内源性 DOM 成分与 Pb(II)的结合特性。最后,确认吸附机制主要涉及静电和疏水相互作用。本研究为探索添加 MPs 和表面活性剂后 Pb(II)通过 MPs 和沉积物的环境行为提供了新的视角,有助于评估 MPs 和重金属在水环环境中的生态风险。