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Diffusive mobility of aromatic hydrocarbons in unsaturated and saturated soils.

机译:芳香烃在非饱和土壤和饱和土壤中的扩散迁移率。

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Contamination of soil and groundwater systems by petroleum hydrocarbons is a widespread concern. Use of organic chemicals by refinery and chemical industries has led to an abundance of environmental hazards due to such things as surface spills, leaking underground storage tanks, and broken pipes. The resulting contamination may be in the form of contaminants dissolved in the aqueous phase, sorbed to the soil solid phase, or as a component of a dispersed or continuous non-aqueous phase liquid (NAPL). Development of improved predictive models for contaminant transport in these multiphase systems would assist in human risk assessments and feasibility studies of remediation technologies.; In this study, diffusion of both volatile (benzene and toluene) and non-volatile (phenanthrene) aromatic hydrocarbons was examined. The effect of phase distribution (soil, aqueous, vapor, and NAPL) on contaminant partitioning among the phases was studied. Investigation of sorption from the NAPL to the soil solid phase indicated that contaminant mass distribution among the phases could be predicted by two-phase partitioning data, along with soil pore size distribution and specific surface area data. Adsorption from the NAPL to soil also was shown to be significant in some cases and to be related to the contaminant type, as well as soil organic carbon and specific surface area.; Diffusion through individual vapor and NAPL phases was independently studied in a multiphase system. Argon was used as a vapor phase diffusion tracer in unsaturated soils with a fixed NAPL relative saturation. Results showed that pore filling by NAPL had the same effect on the vapor phase effective diffusivity as pore filling by water. A previously developed parallel resistance model could accurately predict the experimental data. A tracer through a continuous NAPL phase also was studied as a function of NAPL content, water content, and soil type. Mercury intrusion and extrusion analysis were used to estimate pore connectivity. Using these results, a model was developed to predict the diffusion resistance through the NAPL and thus determine the NAPL phase effective diffusivity.; Simultaneous diffusion and sorption mechanisms were studied based on the mobility of phenanthrene through the aqueous phase in unsaturated soils. Phenanthrene diffusion tube experiments were carried out as a function of soil type, moisture content, and aging. Results indicate the phenanthrene diffusive mobility was most affected by dissolved organic carbon (DOC) concentration. This was found to be inversely related to the soil moisture content. Diffusive mobility of phenanthrene through unsaturated soil systems was much greater than that predicted for water saturated soil systems.; Diffusion controlled release of benzene and toluene from both saturated and unsaturated soil beds containing a fixed relative saturation of NAPL was studied. The soil beds were evaluated at various NAPL and water contents. Three soils were examined. A mathematical model, with parameters accounting for diffusion and sorption in each phase, was shown to accurately describe the experimental data.
机译:石油碳氢化合物污染土壤和地下水系统是人们普遍关注的问题。精炼厂和化学工业对有机化学品的使用已导致大量的环境危害,例如表面溢出,地下储罐泄漏和管道破裂等。产生的污染物可以是溶解在水相中,吸附到土壤固相中的污染物,也可以是分散或连续的非水相液体(NAPL)的组分。在这些多相系统中开发改进的污染物迁移预测模型将有助于人类风险评估和补救技术的可行性研究。在这项研究中,检查了挥发性(苯和甲苯)和非挥发性(菲)芳烃的扩散。研究了相分布(土壤,水,蒸气和NAPL)对各相之间污染物分配的影响。从NAPL吸附到土壤固相的研究表明,两相间的污染物质量分布可以通过两相分配数据以及土壤孔径分布和比表面积数据进行预测。在某些情况下,从NAPL到土壤的吸附也很明显,并且与污染物类型,土壤有机碳和比表面积有关。在多相系统中独立研究了通过各个蒸气相和NAPL相的扩散。在固定的NAPL相对饱和度的非饱和土壤中,氩气用作气相扩散示踪剂。结果表明,NAPL的孔隙填充对气相有效扩散的影响与水的孔隙填充相同。先前开发的并联电阻模型可以准确预测实验数据。还研究了通过连续NAPL相形成的示踪剂与NAPL含量,水含量和土壤类型的关系。汞入侵和挤压分析被用来估计孔隙连通性。利用这些结果,建立了一个模型来预测通过NAPL的扩散阻力,从而确定NAPL相的有效扩散率。基于菲在非饱和土壤中通过水相的迁移率,研究了同时的扩散和吸附机理。菲扩散管实验是根据土壤类型,含水量和老化进行的。结果表明,菲的扩散迁移率受溶解的有机碳(DOC)浓度的影响最大。发现这与土壤水分含量成反比。菲在非饱和土壤系统中的扩散迁移率远大于对水饱和土壤系统的预测迁移率。研究了从固定和相对饱和的NAPL饱和土壤床和非饱和土壤床中扩散控制释放的苯和甲苯。在各种NAPL和水含量下评估土壤床。检查了三种土壤。显示了一个数学模型,该模型具有解释每个阶段中扩散和吸附的参数,可以准确地描述实验数据。

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