School of Environmental Science and Engineering, Zhejiang Gongshang University, Hangzhou, Zhejiang, 310018, China.
College of Environmental and Resource Sciences, Zhejiang University, Hangzhou, 310058, Zhejiang, China.
Environ Pollut. 2023 Jan 1;316(Pt 1):120456. doi: 10.1016/j.envpol.2022.120456. Epub 2022 Oct 21.
Antibiotic resistance genes (ARGs) and nanoplastics (NPs) have been identified as emerging pollutants in water environment; the interactions between antibiotic resistance plasmids (ARPs) and NPs will influence ARG transport in sediments. Herein, the adsorption experiments of a typical ARP onto polystyrene nanoplastics (PS-NPs) in river and lake sediments were conducted to elucidate the adsorption mechanisms and the effects of environmental factors. Results indicated that the adsorption amounts of PS-NPs increased with the dosages while decreased with the particle size of sediments. Multi-layer adsorption of PS-NPs was found to exist mainly in sand and silt sediments, whereas the filling adsorption dominated in the clay. Moreover, the adsorbed PS-NPs enhanced the physisorption of ARPs in sediments through stimulating the intraparticle diffusion of ARPs induced by electrostatic force. Besides, the adsorption amounts of ARPs onto the PS-NPs decreased with the increasing pH and dissolve organic matter due to the enhanced electrostatic repulsion and competitive adsorption. The ion strength played catalytic roles by increasing the electrostatic attraction and adsorption sites of ARPs on PS-NPs. The adsorbed ARPs in sediments were closely related with the ARGs in extra/intracellular DNA of biofilms, influencing the distribution and proliferation of ARGs largely. The findings indicate that ARG-associated pollution might be enhanced by the solid-liquid interface adsorption induced by NPs, which was controlled by pH, ion strength and dissolve organic matter. This study provides supplementary insights into the roles of NPs as carriers of ARP in sediments, and advances our understanding on the risks of NP-ARG co-occurring contamination in aquatic ecosystems.
抗生素耐药基因 (ARGs) 和纳米颗粒 (NPs) 已被确定为水环境中的新兴污染物;抗生素耐药质粒 (ARPs) 和 NPs 之间的相互作用将影响沉积物中 ARG 的迁移。本研究通过开展典型 ARP 在河流和湖泊沉积物中对聚苯乙烯纳米颗粒 (PS-NPs) 的吸附实验,阐明了吸附机制和环境因素的影响。结果表明,PS-NPs 的吸附量随剂量的增加而增加,随沉积物粒径的减小而减小。研究发现 PS-NPs 主要以多层吸附的形式存在于砂和粉砂沉积物中,而在粘土中则以填充吸附为主。此外,吸附的 PS-NPs 通过刺激 ARPs 的颗粒内扩散,增强了静电引力诱导的 ARPs 的物理吸附。此外,由于静电排斥和竞争吸附的增强,吸附到 PS-NPs 上的 ARPs 的吸附量随 pH 值和溶解有机质的增加而减少。离子强度通过增加 ARPs 在 PS-NPs 上的静电吸引和吸附位点,起到了催化作用。沉积物中吸附的 ARPs 与生物膜中外层/内层 DNA 中的 ARGs 密切相关,对 ARGs 的分布和增殖有很大影响。研究结果表明,由于 NPs 诱导的固-液界面吸附,可能会增强与 ARG 相关的污染,而这一过程受到 pH 值、离子强度和溶解有机质的控制。本研究为 NPs 作为沉积物中 ARP 载体的作用提供了补充见解,并加深了我们对水生生态系统中 NP-ARG 共污染风险的认识。