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PAH mobility in contaminated industrial soils: a Markov chain approach to the spatial variability of soil properties and PAH levels

机译:多环芳烃在受污染的工业土壤中的迁移性:土壤属性和多环芳烃水平的空间变异性的马尔可夫链方法

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The consideration of spatially variable contaminant sources and sinks is crucial for the quantification of contaminant transport in industrial soils. To assess the seepage of polycyclic aromatic hydrocarbons (PAH) at a former manufactured gas plant, a combined approach was used comprised of a field survey, stochastic representation of site heterogeneity and numerical simulation of contaminant mobility. Based on field and laboratory data, the vertical transition probabilities of soil materials and PAH-contamination classes were derived and a non-stationary Markov chain model of site heterogeneity was developed. The model was used to generate representative soil profiles by stochastic simulation. Eighty profiles covered 61% of the spatial variability of the site in terms of soil forming materials and PAH levels. Positions and thickness of horizons agreed with the field survey. The seepage of different PAH (fluoranthene, pyrene, benzo(b)fluoranthene, phenathrene, and benzo(a)pyrene) was calculated by numerical simulation using experimentally derived isotherm data. The cumulative output for the individual PAH covered a range of three orders of magnitude, demonstrating the effect of site heterogeneity on contaminant transport. While calculated local maximum concentrations exceeded the critical values for potable water, the weighted average of PAH concentration in seepage water was low. Stochastic generation of soil profiles based on Markov chain theory provides a powerful tool for the consideration of soil variability at contaminated industrial sites. Total profile probability relates to the area fractions represented by each profile. Therefore, contaminant seepage may be estimated without a costly three-dimensional deterministic representation of the field site.
机译:考虑到空间变化的污染物源和汇对于量化工业土壤中污染物的迁移至关重要。为了评估以前的天然气工厂中多环芳烃(PAH)的渗漏,采用了一种组合方法,包括现场调查,现场异质性的随机表示以及污染物迁移率的数值模拟。根据现场和实验室数据,推导了土壤材料和PAH污染类别的垂直转变概率,并建立了场地异质性的非平稳Markov链模型。该模型用于通过随机模拟生成代表性土壤剖面。根据土壤形成材料和多环芳烃水平,八十个剖面覆盖了该场地空间变化的61%。层位的位置和厚度与现场调查一致。通过使用实验得出的等温线数据进行数值模拟,计算出不同PAH(荧蒽,pyr,苯并(b)荧蒽,菲和苯并(a)py)的渗透率。单个PAH的累积输出覆盖了三个数量级的范围,证明了场地异质性对污染物迁移的影响。尽管计算出的局部最大浓度超过了饮用水的临界值,但渗水中PAH浓度的加权平均值很低。基于马尔可夫链理论的土壤剖面随机生成为考虑受污染的工业场地的土壤变异性提供了强大的工具。总轮廓概率与每个轮廓表示的面积分数有关。因此,可以在没有昂贵的现场现场三维确定性表示的情况下估算污染物的渗漏。

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