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    基于模型计算及实测的土壤气中苯系物的浓度分析

    Analysis of Concentration of BTEX in Soil Gas Based on Model Calculations and Field Measurements

    • 摘要: 以北方某在产企业为案例场地,探讨了企业土壤和土壤气监测的污染揭露概率、苯系物空间分布情况、J&E和J&E-DED模型的适用性、模型计算与实测的土壤气浓度之间的关系、场地参数对模型的敏感性等。结果表明:案例场地土壤监测的污染揭露概率为58.2%,土壤气监测的污染揭露概率为91.1%,土壤气监测对苯系物的检出更敏感,更易揭露污染的存在。案例场地土壤和土壤气苯系物空间分布有一定差异,土壤气苯系物分布易受地下优先通道、地表覆盖层、地层生物降解条件等因素影响。当土壤苯浓度小于34 mg/kg,土壤甲苯浓度小于170 mg/kg时,J&E-DED模型比较适用,超过这一浓度范围时,J&E模型比较适用。对于乙苯、间,对二甲苯和邻二甲苯而言,J&E-DED模型比较适用,随着土壤乙苯、间,对二甲苯和邻二甲苯浓度增大,2个模型计算浓度差缩小。当土壤苯系物浓度增大至30 mg/kg时,J&E和J&E-DED模型计算浓度处于同一数量级,当土壤苯系物浓度增大至10 000 mg/kg甚至更大时,J&E-DED模型计算浓度仍小于J&E模型计算浓度,且两者比值基本稳定在0.77、0.65和0.66。实测的土壤气苯系物浓度为采样点本身的土壤气苯系物浓度与横向迁移至采样点附近的土壤气苯系物浓度的叠加,很多情况下,实测浓度高于模型计算浓度若干个数量级。但当土壤浓度较高时,辛醇-水分配系数较高的乙苯、间,对二甲苯和邻二甲苯可能出现模型计算浓度比实测浓度高2~4个数量级的情况。J&E模型对有机碳-水分配系数(Koc)和土壤有机碳质量分数(foc)较敏感,J&E-DED模型对foc比较敏感,对其他场地参数敏感度较低。

       

      Abstract: An operating enterprise in northern China was selected as a case study to explore the pollution detection probability of soil and soil gas monitoring in operating enterprises,spatial distribution patterns,the applicability of the J&E and J&E-DED models,the relationship between measured and model-calculated concentrations,and the sensitivity of site parameters to the models.The results showed that:The pollution detection probability of soil monitoring at the case site was 58.2%,while that of soil gas monitoring was 91.1%,indicating that soil gas monitoring is more sensitive to the detection of benzene-series compounds and more effective in revealing pollution presence.The spatial distribution of benzene-series compounds in soil and soil gas at the case site exhibited some differences,with soil gas distribution being more susceptible to factors such as preferential underground pathways,surface cover layers,and biodegradation conditions in the subsurface.When the benzene concentration in soil was below 34 mg/kg and the toluene concentration was below 170 mg/kg,the J&E-DED model was more applicable,whereas the J&E model was more suitable beyond these thresholds.For ethylbenzene,m&p-xylene,and o-xylene,the J&E-DED model was generally more applicable.As soil concentrations increased,the difference between the two models' calculated concentrations decreased.When concentrations reached approximately 30 mg/kg,the concentrations calculated by the J&E and J&E-DED models were of the same order of magnitude.When concentrations increased to 10000 mg/kg or even higher,the J&E-DED model's calculated concentrations remained lower than those of the J&E model,with their ratios stabilizing at approximately 0.77,0.65,and 0.66.The measured soil gas BTEX concentrations represented a combination of the in-situ soil gas concentration at the sampling point and the contribution from lateral migration of soil gas from nearby sources.In many cases,measured concentrations exceeded modeled concentrations by several orders of magnitude.However,under high soil concentration conditions,for ethylbenzene,m,p-xylene,and o-xylene,which have higher octanol-water partition coefficients,modeled concentrations could be 2 to 4 orders of magnitude higher than measured concentrations.The J&E model was more sensitive to the organic carbon-water partition coefficient (Koc) and soil organic carbon content (foc),while the J&E-DED model was primarily sensitive to soil organic carbon content (foc) and exhibited lower sensitivity to other site parameters.

       

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