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朝向对磺胺类药物-土壤有机质相互作用的分子水平理解。

Towards a molecular level understanding of the sulfanilamide-soil organic matter-interaction.

机构信息

University of Rostock, Institute of Physics, Albert-Einstein-Str. 23-24, D-18059 Rostock, Germany; Steinbeis GmbH & Co. KG für Technologietransfer, 70174 Stuttgart, Germany; University of Cairo, Faculty of Science, Department of Chemistry, 12613 Giza, Egypt.

University of Trier, Soil Science, D-54286 Trier, Germany.

出版信息

Sci Total Environ. 2016 Jul 15;559:347-355. doi: 10.1016/j.scitotenv.2016.03.136. Epub 2016 Apr 16.

DOI:10.1016/j.scitotenv.2016.03.136
PMID:27088516
Abstract

Sorption experiments of sulfanilamide (SAA) on well-characterized samples of soil size-fractions were combined with the modeling of SAA-soil-interaction via quantum chemical calculations. Freundlich unit capacities were determined in batch experiments and it was found that they increase with the soil organic matter (SOM) content according to the order fine silt > medium silt > clay > whole soil > coarse silt > sand. The calculated binding energies for mass-spectrometrically quantified sorption sites followed the order ionic species > peptides > carbohydrates > phenols and lignin monomers > lignin dimers > heterocyclic compounds > fatty acids > sterols > aromatic compounds > lipids, alkanes, and alkenes. SAA forms H-bonds through its polar centers with the polar SOM sorption sites. In contrast dispersion and π-π-interactions predominate the interaction of the SAA aromatic ring with the non-polar moieties of SOM. Moreover, the dipole moment, partial atomic charges, and molecular volume of the SOM sorption sites are the main physical properties controlling the SAA-SOM-interaction. Further, reasonable estimates of the Freundlich unit capacities from the calculated binding energies have been established. Consequently, we suggest using this approach in forthcoming studies to disclose the interactions of a wide range of organic pollutants with SOM.

摘要

磺胺(SAA)在特征明确的土壤粒径样品上的吸附实验与通过量子化学计算对 SAA-土壤相互作用的建模相结合。通过批量实验确定了弗伦德利希单位容量,发现它们根据顺序细粉砂>中粉砂>粘土>全土>粗粉砂>砂而随土壤有机质(SOM)含量增加。通过质量光谱定量的吸附位的计算结合能遵循以下顺序:离子型>肽>碳水化合物>酚和木质素单体>木质素二聚体>杂环化合物>脂肪酸>甾醇>芳族化合物>脂质、烷烃和烯烃。SAA 通过其极性中心与极性 SOM 吸附位形成氢键。相比之下,SAA 芳环与 SOM 的非极性部分主要是通过色散和π-π相互作用。此外,SOM 吸附位的偶极矩、部分原子电荷和分子体积是控制 SAA-SOM 相互作用的主要物理性质。此外,还从计算的结合能中建立了弗伦德利希单位容量的合理估计。因此,我们建议在即将进行的研究中使用这种方法来揭示广泛的有机污染物与 SOM 的相互作用。

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