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极性和非极性有机污染物与土壤有机质的相互作用:吸附实验和分子动力学模拟。

Interaction of polar and nonpolar organic pollutants with soil organic matter: sorption experiments and molecular dynamics simulation.

机构信息

University of Rostock, Institute of Physics, D-18051 Rostock, 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. 2015 Mar 1;508:276-87. doi: 10.1016/j.scitotenv.2014.11.087. Epub 2014 Dec 6.

Abstract

The fate of organic pollutants in the environment is influenced by several factors including the type and strength of their interactions with soil components especially SOM. However, a molecular level answer to the question "How organic pollutants interact with SOM?" is still lacking. In order to explore mechanisms of this interaction, we have developed a new SOM model and carried out molecular dynamics (MD) simulations in parallel with sorption experiments. The new SOM model comprises free SOM functional groups (carboxylic acid and naphthalene) as well as SOM cavities (with two different sizes), simulating the soil voids, containing the same SOM functional groups. To examine the effect of the hydrophobicity on the interaction, the organic pollutants hexachlorobenzene (HCB, non-polar) and sulfanilamide (SAA, polar) were considered. The experimental and theoretical investigations explored four major points regarding sorption of SAA and HCB on soil, yielding the following results. 1--The interaction depends on the SOM chemical composition more than the SOM content. 2--The interaction causes a site-specific adsorption on the soil surfaces. 3--Sorption hysteresis occurs, which can be explained by inclusion of these pollutants inside soil voids. 4--The hydrophobic HCB is adsorbed on soil stronger than the hydrophilic SAA. Moreover, the theoretical results showed that HCB forms stable complexes with all SOM models in the aqueous solution, while most of SAA-SOM complexes are accompanied by dissociation into SAA and the free SOM models. The SOM-cavity modeling had a significant effect on binding of organic pollutants to SOM. Both HCB and SAA bind to the SOM models in the order of models with a small cavity>a large cavity>no cavity. Although HCB binds to all SOM models stronger than SAA, the latter is more affected by the presence of the cavity. Finally, HCB and SAA bind to the hydrophobic functional group (naphthalene) stronger than to the hydrophilic one (carboxylic acid) for all SOM models containing a cavity. For models without a cavity, SAA binds to carboxylic acid stronger than to naphthalene.

摘要

有机污染物在环境中的命运受到多种因素的影响,包括它们与土壤成分(尤其是 SOM)相互作用的类型和强度。然而,对于“有机污染物如何与 SOM 相互作用?”这一问题,仍然缺乏分子水平的答案。为了探索这种相互作用的机制,我们开发了一种新的 SOM 模型,并进行了分子动力学(MD)模拟和吸附实验。新的 SOM 模型包含游离 SOM 官能团(羧酸和萘)以及 SOM 腔(两种不同大小),模拟土壤空隙,其中包含相同的 SOM 官能团。为了研究疏水性对相互作用的影响,考虑了有机污染物六氯苯(HCB,非极性)和磺胺(SAA,极性)。实验和理论研究探讨了关于 SAA 和 HCB 在土壤上吸附的四个主要问题,得出以下结果。1--相互作用取决于 SOM 的化学成分而不是 SOM 的含量。2--相互作用导致在土壤表面的特异性吸附。3--发生吸附滞后,这可以通过将这些污染物包含在土壤空隙中来解释。4--疏水性的 HCB 比亲水性的 SAA 在土壤上吸附更强。此外,理论结果表明,HCB 在水溶液中与所有 SOM 模型形成稳定的配合物,而大多数 SAA-SOM 配合物伴随着 SAA 和游离 SOM 模型的解离。SOM 腔模型对有机污染物与 SOM 的结合有显著影响。HCB 和 SAA 都按照小腔>大腔>无腔的顺序结合到 SOM 模型上。虽然 HCB 与所有 SOM 模型的结合都比 SAA 强,但后者受腔存在的影响更大。最后,对于含有腔的所有 SOM 模型,HCB 和 SAA 与疏水性官能团(萘)的结合比与亲水性官能团(羧酸)的结合更强。对于没有腔的模型,SAA 与羧酸的结合比与萘的结合更强。

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