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改性芬顿反应对杂酚油污染土壤中微生物活性及多环芳烃去除的影响

Effect of modified Fenton's reaction on microbial activity and removal of PAHs in creosote oil contaminated soil.

作者信息

Palmroth M R T, Langwaldt J H, Aunola T A, Goi A, Münster U, Puhakka J A, Tuhkanen T A

机构信息

Environmental Engineering and Biotechnology, Tampere University of Technology, P.O. Box 541, Tampere 33101, Finland.

出版信息

Biodegradation. 2006 Mar;17(2):131-41. doi: 10.1007/s10532-005-6060-3. Epub 2006 Feb 2.

Abstract

This study describes the removal of polycyclic aromatic hydrocarbons (PAHs) from creosote oil contaminated soil by modified Fenton's reaction in laboratory-scale column experiments and subsequent aerobic biodegradation of PAHs by indigenous bacteria during incubation of the soil. The effect of hydrogen peroxide addition for 4 and 10 days and saturation of soil with H(2)O(2) on was studied. In both experiments the H(2)O(2) dosage was 0.4 g H(2)O(2)/g soil. In completely H(2)O(2)-saturated soil the removal of PAHs (44% within 4 days) by modified Fenton reaction was uniform over the entire soil column. In non-uniformly saturated soil, PAH removal was higher in completely saturated soil (52% in 10 days) compared to partially saturated soil, with only 25% in 10 days. The effect of the modified Fenton's reaction on the microbial activity in the soil was assessed based on toxicity tests towards Vibrio fischeri, enumeration of viable and dead cells, microbial extracellular enzyme activity, and oxygen consumption and carbon dioxide production during soil incubation. During the laboratory-scale column experiments, the toxicity of column leachate towards Vibrio fischeri increased as a result of the modified Fenton's reaction. The activities of the microbial extracellular enzymes acetate- and acidic phosphomono-esterase were lower in the incubated modified Fenton's treated soil compared to extracellular enzyme activities in untreated soil. Abundance of viable cells was lower in incubated modified Fenton treated soil than in untreated soil. Incubation of soil in serum bottles at 20 degrees C resulted in consumption of oxygen and formation of carbon dioxide, indicating aerobic biodegradation of organic compounds. In untreated soil 20-30% of the PAHs were biodegraded during 2 months of incubation. Incubation of chemically treated soil slightly increased PAH-removal compared to PAH-removal in untreated soil.

摘要

本研究描述了在实验室规模的柱实验中,通过改良芬顿反应从杂酚油污染土壤中去除多环芳烃(PAHs),以及在土壤孵化过程中土著细菌对PAHs的后续好氧生物降解。研究了添加过氧化氢4天和10天以及用H₂O₂使土壤饱和的效果。在两个实验中,H₂O₂用量均为0.4 g H₂O₂/g土壤。在完全H₂O₂饱和的土壤中,改良芬顿反应对PAHs的去除(4天内为44%)在整个土壤柱中是均匀的。在非均匀饱和土壤中,与部分饱和土壤相比,完全饱和土壤中PAH的去除率更高(10天内为52%),部分饱和土壤10天内仅为25%。基于对费氏弧菌的毒性测试、活菌和死菌计数、微生物胞外酶活性以及土壤孵化过程中的氧气消耗和二氧化碳产生,评估了改良芬顿反应对土壤中微生物活性的影响。在实验室规模的柱实验中,改良芬顿反应导致柱渗滤液对费氏弧菌的毒性增加。与未处理土壤中的胞外酶活性相比,在经过改良芬顿处理的孵化土壤中,微生物胞外酶乙酸酯酶和酸性磷酸单酯酶的活性较低。经过改良芬顿处理的孵化土壤中活菌数量低于未处理土壤。在血清瓶中于20℃孵化土壤导致氧气消耗和二氧化碳形成,表明有机化合物发生了好氧生物降解。在未处理土壤中,2个月的孵化期内20 - 30%的PAHs被生物降解。与未处理土壤中的PAH去除相比,化学处理土壤的孵化略微增加了PAH的去除。

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