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Factors inhibiting bioremediation of soil contaminated with weathered oils and drill cuttings

机译:阻碍被风化油和钻屑污染的土壤进行生物修复的因素

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Oily drill cuttings and a soil contaminated with weathered crude oils were treated by enhanced biodegradation under tropical conditions in industrial scaled experiments. Oil contaminants were characterized by gas chromatography and mass spectrometry. This allowed for the identification of a mixture of two crude oils in the contaminated soil. After 12 months of bioremediation process, the removal of hydrocarbons reached by biodegradation an extent of 60% although nutrient amendment with elevated concentration of N-urea had highly detrimental effects on the hydrocarbon degrading fungal populations due to the production of toxic concentration of ammonia gas by nitrification. The saturated hydrocarbons were extensively assimilated, though n-alkanes were not completely removed. Aromatic hydrocarbons were less degraded than saturated whereas resin and asphaltene fractions were, surprisingly, partly assimilated. In laboratory conditions, the residual hydrocarbons in the field-treated materials were 15—20% further degraded when metabolic byproducts resulting from biodegradation were diluted or removed.
机译:在工业规模的实验中,通过在热带条件下增强生物降解作用来处理油性钻屑和被风化原油污染的土壤。通过气相色谱法和质谱法表征油污染物。这样可以鉴定出受污染土壤中两种原油的混合物。经过12个月的生物修复过程,尽管随着氮脲浓度的升高而进行的营养改良剂对降解碳氢化合物的真菌种群产生了极大的有害影响,但由于生物降解过程中碳氢化合物产生的氨气毒性浓度较高,因此去除率高达60%。硝化作用。尽管未完全除去正构烷烃,但饱和烃被广泛吸收。芳香烃的降解程度低于饱和烃,而令人惊讶的是,树脂和沥青质馏分被部分吸收。在实验室条件下,当稀释或去除生物降解产生的代谢副产物时,田间处理过的材料中残留的碳氢化合物会进一步降解15-20%。

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