聚丙烯微塑料对土壤中环丙沙星吸附-解吸的影响机制研究

Study on the Mechanism of Polypropylene Microplastics Affecting the Adsorption-Desorption of Ciprofloxacin in Soil

  • 摘要: 微塑料(MPs)和抗生素等新污染物在土壤中普遍检出且呈现复合污染特征,其迁移受土壤吸附-解吸过程影响,但已有研究多聚焦于单纯土壤中抗生素的吸附-解吸或单纯微塑料中抗生素的吸附,对土壤-微塑料复合体系中抗生素的吸附-解吸研究尚有不足。本文基于环境中抗生素检出浓度和MPs环境丰度,选取环丙沙星(CIP)和聚丙烯(PP)分别作为代表性抗生素和MPs,通过吸附-解吸实验,研究添加不同比例PP的土壤中CIP的吸附-解吸过程。采用高效液相色谱法(HPLC)检测CIP浓度,并通过两种动力学模型(准一级、准二级)和两种吸附等温模型(Freundlich、Linear)对实验数据进行拟合。结果表明:未添加及添加PP土壤对CIP的吸附均符合准一级和准二级动力学模型(R2 ≥ 0.997);相较于Linear模型(R2 ≥ 0.952),添加PP土壤对CIP的等温吸附-解吸特征更符合Freundlich模型(R2 ≥ 0.991),表明添加PP土壤对CIP吸附受阳离子交换、疏水分配等机制共同作用;未添加与添加PP土壤对CIP的平衡吸附量无明显差异,土壤在高达20%的PP添加比例下仍对CIP的吸附起主导作用,但等温吸附拟合参数表明随PP添加比例增大,土壤对CIP的吸附能力减弱,解吸能力增强。解吸滞后系数(HI)为0.043 ~ 0.066,该值随PP添加比例增大而单调递增,说明CIP解吸滞后现象明显,PP添加比例越高,解吸迟滞效应越弱,CIP更易从土壤中释放,环境迁移风险上升。本研究揭示了PP对土壤中CIP吸附-解吸的影响特征,为进一步探究土壤中MPs与抗生素的相互作用机制和环境行为提供了数据支撑。

     

    Abstract: Microplastics (MPs) and emerging pollutants such as antibiotics are commonly detected in soil and exhibit characteristics of combined pollution. Their migration is influenced by soil adsorption-desorption processes. However, existing research has primarily focused on the adsorption-desorption of antibiotics in pure soil or the adsorption of antibiotics on pure microplastics, with limited studies on the adsorption-desorption of antibiotics in soil-microplastic composite systems. Based on the detected concentrations of antibiotics and the environmental abundance of MPs, this paper selects ciprofloxacin (CIP) and polypropylene (PP) as representative antibiotics and MPs, respectively. Through adsorption-desorption experiments, the adsorption-desorption process of CIP in soil added with different proportions of PP was investigated. High-performance liquid chromatography (HPLC) was used to detect CIP concentration, and experimental data were fitted using two kinetic models (pseudo-first-order, pseudo-second-order) and two adsorption isotherm models (Freundlich, Linear). The results showed that the adsorption of CIP in soil with and without PP added conformed to both pseudo-first-order and pseudo-second-order kinetic models (R2 ≥ 0.997). Compared to the Linear model (R ≥ 0.952), the isothermal adsorption-desorption characteristics of CIP in soil with PP added were more consistent with the Freundlich model (R2 ≥ 0.991), indicating that the adsorption of CIP in soil with PP added was influenced by a combination of cation exchange and hydrophobic partitioning mechanisms. There was no significant difference in the equilibrium adsorption capacity of CIP between soil with and without PP added, suggesting that soil still played a dominant role in CIP adsorption even with up to 20% PP added. However, the isothermal adsorption fitting parameters indicated that as the proportion of PP added increased, the adsorption capacity of soil for CIP decreased, while the desorption capacity increased. Using the desorption hysteresis index (HI) to analyze the desorption experiment results, it was found that the HI value (0.043–0.066) increased monotonically with the increase in PP addition proportion, indicating a significant desorption hysteresis phenomenon of CIP. The higher the proportion of PP added, the weaker the desorption hysteresis effect, making CIP easier to release from soil and increasing the environmental migration risk. This study reveals the impact of PP on the adsorption-desorption of CIP in soil, providing data support for further exploring the interaction mechanism and environmental behavior of MPs and antibiotics in soil.

     

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