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Interaction of Polar and Nonpolar Organic Pollutants with Soil Organic Matter: Sorption Experiments and Molecular Dynamics Simulation

机译:极地与非极地有机污染物与土壤有机污染物的相互作用   问题:吸附实验和分子动力学模拟

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摘要

The fate of organic pollutants in the environment is influenced by severalfactors including the type and strength of their interactions with soilcomponents especially SOM. However, a molecular level answer to the questionHow organic pollutants interact with SOM? is lacking. In order to exploremechanisms of this interaction, we have developed a new SOM model followed bycarrying out molecular dynamics (MD) simulations in parallel with sorptionexperiments. The new SOM model comprises free SOM functional groups (carboxylicacid and naphthalene) as well as SOM cavities (with two different sizes),representing the soil voids, containing the same SOM functional groups. Toexamine the effect of the hydrophobicity on the interaction, the organicpollutants hexachlorobenzene (HCB, non-polar) and sulfanilamide (SAA, polar)were considered. The experimental and the theoretical outcomes explored fourmajor points regarding sorption of SAA and HCB on soil. 1. The interactiondepends on the SOM chemical composition more than the SOM content. 2. Theinteraction causes a site-specific adsorption on the soil surfaces. 3. Sorptionhysteresis occurs, which can be explained by inclusion of these pollutantsinside soil voids. 4. It was observed that the hydrophobic HCB is adsorbed onsoil stronger than the hydrophilic SAA. Moreover, the theoretical resultsshowed that HCB forms stable complexes with all SOM models in the aqueoussolution while most of SAA complexes are accompanied by dissociation. TheSOM-cavity modeling showed a significant effect on binding of organicpollutants to SOM.
机译:环境中有机污染物的命运受多种因素影响,包括它们与土壤成分(特别是SOM)相互作用的类型和强度。但是,从分子水平上回答了有机污染物如何与SOM相互作用的问题。是缺乏。为了探索这种相互作用的机理,我们开发了一种新的SOM模型,随后与吸附实验并行进行了分子动力学(MD)模拟。新的SOM模型包含自由的SOM官能团(羧酸和萘)以及SOM空腔(具有两个不同的大小),代表包含相同SOM官能团的土壤孔隙。为了检查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)。实验和理论结果探讨了SAA和HCB在土壤上的吸附的四个主要方面。 1.相互作用对SOM化学成分的依赖性大于对SOM含量的依赖性。 2.相互作用导致土壤表面发生特定位置的吸附。 3.发生吸附滞后现象,这可以通过将这些污染物包含在土壤空隙中来解释。 4.观察到疏水性HCB的吸附能力强于亲水性SAA。此外,理论结果表明,六氯代苯与水溶液中的所有SOM模型均形成稳定的配合物,而大多数SAA配合物则伴随有离解作用。 SOM腔模型显示出对有机污染物与SOM结合的显着影响。

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