Impact of bioaugmentation of soil with n-hexadecane-degrading bacteria and phosphorus source on the rate of biodegradation in a soil-slurry system

M. Dehghani
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引用次数: 7

Abstract

In recent years, n-hexadecane, a component of diesel petroleum hydrocarbons, is frequently detected as the contaminant in many soils and water resources. The main aims of this study were focused on the feasibility of using the biodegradation for the removal of n-hexadecane from the soil-slurry system, by assessing the effects of phosphorus sources on biodegradation rate and determining the optimal conditions of the process. This study was carried out using an experimental method at the laboratory scale. The Taguchi method was used to optimize variables and their levels using the Qualitek-4 (w32b) software. We investigated the effects of initial concentration of n-hexadecane as the sole source of carbon (1-80 g/kg of soil), the role of phosphorus sources, at the concentration ranges from 10 to 600 g per Kg of soil, released by different bacterial species (Acinetobacter radioresistens, Pseudomonas aeruginosa, Bacillus subtilis, and the bacterial consortium) at the incubation time between 0 and 30 days. The optimum values of the response variables were predicted through signal-to-noise ratio (S/N). Results indicated that Bacillus subtilis were more effective in n-hexadecane degradation compared to the others (42%). Optimization process by Taguchi method suggested that the optimal conditions for the removal of n-hexadecane in a soil-slurry system are as follows: the initial n-hexadecane concentration as sole source of carbon in soil, Na2HPO4.12H2O as phosphorus source at the concentration of 300 mg per kg of soil and, finally, level of significance for the study parameters were 74.31, 6.48 and 8.51, respectively. In conclusion, bioaugmentation of soil with n-hexadecane-degrading bacteria providing an adequate supply of phosphorus source may enhance the biodegradation rate in a polluted soil.
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正十六烷降解菌和磷源对土壤-泥浆系统生物降解速率的影响
近年来,正十六烷作为柴油和石油烃的一种成分,在许多土壤和水资源中被频繁检测到。本研究的主要目的是通过评估磷源对生物降解率的影响并确定该过程的最佳条件,研究利用生物降解技术去除土壤-泥浆系统中正十六烷的可行性。本研究采用实验室规模的实验方法进行。使用Qualitek-4 (w32b)软件,采用田口法优化变量及其水平。我们研究了正十六烷作为唯一碳源(1-80 g/kg土壤)的初始浓度的影响,磷源的作用,在浓度范围为10 - 600 g/kg土壤,由不同细菌种类(抗辐射不动杆菌、铜绿假单胞菌、枯草芽孢杆菌和细菌群)在0 - 30天的孵育时间内释放。通过信噪比(S/N)预测响应变量的最优值。结果表明,枯草芽孢杆菌对正十六烷的降解效果较好(42%)。田口法优化结果表明,土壤-泥浆体系中正十六烷去除的最佳条件为:初始正十六烷浓度为土壤中唯一碳源,Na2HPO4.12H2O浓度为300 mg / kg土壤中磷源,最终研究参数的显著性水平分别为74.31、6.48和8.51。综上所述,利用正十六烷降解菌对土壤进行生物强化,提供充足的磷源,可以提高污染土壤的生物降解率。
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