Comparative Bioremediation of Oil Contaminated Soil by Natural Attenuation, Biostimulation and Bioaugmentation

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In most field studies, enhancing biodegradation of petroleum hydrocarbons depends on the specific microbial population present. It is a dispute whether inoculation microbial consortium improved the degradation of petroleum because indigenous microorganism can easily adapt to surroundings and contend for inoculation microbial consortium. Therefore, all of three technologies (natural attenuation, biostimulation and bioaugmentation) were evaluated. After 8 weeks of bioremediation, it was observed that bioaugmentation most effectively removed 53% of oil under inoculation condition. Poor oil removal of below 4% was observed under natural attenuation without inoculation. In addition, it was found that the degradation of oil in oil-polluted soil followed second-order model and acquired the dynamics equations. The half-life of natural attenuation, biostimulation and bioaugmentation was 833 days, 75days, 25days, respectively. The results indicated bioaugmentation could improve efficiently the degradation of TPH and shorten the bioremediation period.

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258-262

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September 2013

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© 2013 Trans Tech Publications Ltd. All Rights Reserved

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[1] Colwell F S. Microbiological comparison of surface soil and unsaturated subsurface soil from a semiarid high desert. Applied and environmental Microbiology, 55(1989): 2420-2423.

DOI: 10.1128/aem.55.9.2420-2423.1989

Google Scholar

[2] Duncan K, Jennings E. Multi-species ecotoxicity assessment of petroleum-contaminated soil, Soil and Sediment Contamination, 12(2003): 181-206.

DOI: 10.1080/713610969

Google Scholar

[3] Gallego J R, Loredo J, Llamas J F, et al. Bioremediation of diesel-contaminated soils: evaluation of potential in situ techniques by study of bacterial degradation, 12(2001): 325-335.

Google Scholar

[4] Richard J Y, Vogel T M. Characterization of soil bacterial consortium capable of degrading diesel fuel. Int Biodet. Biod , 44(1999): 93-100.

DOI: 10.1016/s0964-8305(99)00062-1

Google Scholar

[5] Maki H, Hirayama N. Crude oil bioremediation field experiment in the Sea of Japan. marine Pollution bulletin, 47(2003): 74-77.

DOI: 10.1016/s0025-326x(02)00412-5

Google Scholar

[6] Margesin R, Schinner F. Laboratory bioremediation experiments with soil from a diesel-oil contaminated site-significant role of cold-adapted microorganisms and fertilizers, Journal of Chemical and Biotechnology, 70(1997) : 92-98.

DOI: 10.1002/(sici)1097-4660(199709)70:1<92::aid-jctb683>3.0.co;2-m

Google Scholar

[7] Admon S, Green M, Avnimelech Y. Biodegradation kinetics of hydrocarbons in soil during land treatment of oily sludge. Bioremed. J, 5(1995): 193-209.

DOI: 10.1080/20018891079285

Google Scholar

[8] Alef K. Estimation of microbial activities : dehydrogenase activity. In: Alef. K, Nannipieri, p (Eds), Methods in applied soil microbiology and Biochemistry. Academic press, New York: 228-231 (1995).

DOI: 10.1016/b978-012513840-6/50014-8

Google Scholar

[9] Cerniglia C E. Microbial metabolism of polycyclic aromatic hydrocarbons. Advances in Applied Microbiology. Vol 30, Academic press. Inc New York: 31-71 (1984).

DOI: 10.1016/s0065-2164(08)70052-2

Google Scholar