Institute of Geographical Sciences and Natural Resources Research, Beijing 100101, China; University of Chinese Academy of Sciences, Beijing 100049, China.
Institute of Geographical Sciences and Natural Resources Research, Beijing 100101, China; University of Chinese Academy of Sciences, Beijing 100049, China.
J Hazard Mater. 2022 Feb 15;424(Pt A):127368. doi: 10.1016/j.jhazmat.2021.127368. Epub 2021 Sep 27.
Ionic antibiotics and metals generally coexist, and their interaction can affect their sorption behaviors onto soil minerals, therefore determining their environmental hazards. This study investigated the sorption and cosorption of Zn(II) and chlortetracycline (CTC) onto montmorillonite at different solution pH (3-10) using batch experiments and extended X-ray absorption fine structure (EXAFS) analysis. The Langmuir model could reproduce well the sorption isotherms of Zn(II) and CTC. The presence of CTC/Zn(II) could promote the maximum sorption capacity (Q) of Zn(II)/CTC, based on site energy distribution (SED) theory. Generally, Zn(II) sorption increased with pH increasing. Comparatively, CTC sorption decreased as pH increased till approximately pH 5.0, then increased continuously with pH increasing. Both CTC and Zn(II) co-existence enhanced their individual sorption in both acidic and neutral environments. The processes behind CTC and Zn(II) sorption mainly included cation exchange and surface complexation. The EXAFS data evidenced that the presence of CTC could alter the species of Zn(II) on montmorillonite via surface complexation at pH 4.5 and 7.5, with Zn-CTC complexes being the predominant species on montmorillonite at pH 7.5. At pH 9.5, Zn(II) may exist onto montmorillonite in precipitated form similar to Zn-Al hydrotalcite-like compound (HTlc) regardless of CTC presence.
离子型抗生素和金属通常共存,它们的相互作用会影响它们在土壤矿物上的吸附行为,从而决定其环境危害。本研究采用批实验和扩展 X 射线吸收精细结构(EXAFS)分析,研究了不同溶液 pH 值(3-10)下 Zn(II)和金霉素(CTC)在蒙脱石上的吸附和共吸附。Langmuir 模型可以很好地再现 Zn(II)和 CTC 的吸附等温线。根据位能分布(SED)理论,CTC/Zn(II)的存在可以促进 Zn(II)/CTC 的最大吸附容量(Q)。一般来说,随着 pH 值的增加,Zn(II)的吸附增加。相比之下,随着 pH 值的增加,CTC 的吸附减少,直至约 pH 5.0,然后随着 pH 值的增加而持续增加。CTC 和 Zn(II)共存都能在酸性和中性环境中增强它们各自的吸附。CTC 和 Zn(II)吸附的背后过程主要包括阳离子交换和表面络合。EXAFS 数据表明,在 pH 4.5 和 7.5 时,CTC 的存在可以通过表面络合改变蒙脱石上 Zn(II)的形态,在 pH 7.5 时,Zn-CTC 复合物是蒙脱石上的主要形态。在 pH 9.5 时,无论 CTC 是否存在,Zn(II)可能以类似于 Zn-Al 水滑石类似物(HTlc)的沉淀形式存在于蒙脱石上。