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Increase in removal of polycyclic aromatic hydrocarbons during bioremediation of crude oil-contaminated sandy soil.

机译:在原油污染的沙质土壤的生物修复过程中,多环芳烃的去除增加。

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A 23 full factorial experimental design was adopted to estimate the effects of three variables on the biodegradation of oil during soil bioremediation: bioaugmentation seeding a mixed culture, addition of fertilizer or mineral media, and correction of initial pH of the soil to 7.0. The tests were carried out in polyvinyl chloride reactors with 5.0 kg of crude oil-contaminated soil at 14 g/kg. After screening the variables, soil bioremediation tests were conduced with varied C:N ratios, yielding an increase in biodegradation of the oil heavy fraction from 24 to 65%, consumption of total n-paraffins, and a remarkable decrease in the concentration of residual polycyclic aromatic hydrocarbons of the soil.
机译:采用23个全因子实验设计来估算土壤生物修复过程中三个变量对油脂生物降解的影响:生物强化播种混合培养物,添加肥料或矿物培养基以及将土壤的初始pH值校正为7.0。该试验是在聚氯乙烯反应器中进行的,其中5.0 kg的原油被污染的土壤为14 g / kg。在筛选了变量之后,进行了土壤生物修复测试,改变了C:N比例,使重油馏分的生物降解率从24%提高到了65%,正链烷烃的总消耗量以及残留的多环化合物的浓度均显着下降。土壤中的芳香烃。

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