Study on biological degradation and transform characteristics of different components in petroleum hydrocarbon used by bacterial consortium

被引:7
作者
Chen, Lihua [1 ]
Xiao, Chaohu [1 ]
Luo, Xiaofang [1 ]
Sun, Wanhong [1 ]
机构
[1] Northwest Univ Nationalities, Expt Ctr, Lanzhou 730030, Peoples R China
基金
中国国家自然科学基金;
关键词
Mixed bacteria; Biodegradation; Petroleum-contaminated soil; GC-MS; OIL BIODEGRADATION; SOIL; RHIZOSPHERE;
D O I
10.1007/s12665-016-5599-0
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Some oil-degradation bacterial strains, designated as F1, F2, A5, A6, and D4, were screened and isolated from oil-contaminated soil at the Huaqing Oilfield of Gansu Province, China. The degradation of n-alkanes, hopanes and aromatic hydrocarbons was detected by GC-MS, and biological transform characteristics of n-alkanes, hopanes, aromatic hydrocarbon had been analyzed by various biological marker ratios. The results show that the highest degradation rate of A5, D4 and the mixed bacteria H for high carbon normal alkanes (C-28-C-39) is more than 70 %. The degradation rate of mixed bacteria H for n-alkanes is relatively balanced. The max w(Sigma C-21-/Sigma C22+) ratio is 0.75, indicating that F2 predominately degrades higher molecular weight n-alkanes. The various strains can promote the transition from less stable R configuration of pentacyclic triterpenes to stable S configuration in 7 days. The w(Ts)/w(Tm) of A5 for hopanes is biggest (0.96), indicating that transformation is most complete. For hopanes, the mixed bacteria H have the best degradation rate and the advantages are obvious. Single bacteria and the mixed bacteria H all have a strong demethylation effect on the naphthalene ring, wherein F1, A5 and D4 have the strongest effects. The mixed bacteria H have an obvious degradation effect on chrysenes. As the research object, this paper systematically studied the degradation and biomarkers of n-alkanes, hopanes and aromatic hydrocarbons by means of ultraviolet spectroscopy and GC-MS to provide basic information for further study of petroleum-contaminated soil remediation technologies.
引用
收藏
页数:12
相关论文
共 27 条
[1]   Bioremediation of a crude-oil polluted agricultural-soil at Port Harcourt, Nigeria [J].
Ayotamuno, M. J. ;
Kogbara, R. B. ;
Ogaji, S. O. T. ;
Probert, S. D. .
APPLIED ENERGY, 2006, 83 (11) :1249-1257
[2]   Isolation and characterization of polycyclic aromatic hydrocarbon-degrading bacteria associated with the rhizosphere of salt marsh plants [J].
Daane, LL ;
Harjono, I ;
Zylstra, GJ ;
Häggblom, MM .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 2001, 67 (06) :2683-2691
[3]   Crude petroleum-oil biodegradation efficiency of Bacillus subtilis and Pseudomonas aeruginosa strains isolated from a petroleum-oil contaminated soil from North-East India [J].
Das, Kishore ;
Mukherjee, Ashis K. .
BIORESOURCE TECHNOLOGY, 2007, 98 (07) :1339-1345
[4]  
DAVIS GB, 1997, LAND CONTAM RECLAM, V5, P287
[5]  
Díaz-Ramírez IJ, 2003, CAN J MICROBIOL, V49, P755, DOI [10.1139/w03-098, 10.1139/W03-098]
[6]   Polycyclic aromatic hydrocarbon transformation with laccases of a white-rot fungus isolated from a Mediterranean schlerophyllous litter [J].
Farnet, A. M. ;
Gil, G. ;
Ruaudel, F. ;
Chevremont, A. C. ;
Ferre, E. .
GEODERMA, 2009, 149 (3-4) :267-271
[7]   Bioremediation of crude oil polluted seawater by a hydrocarbon-degrading bacterial strain immobilized on chitin and chitosan flakes [J].
Gentili, Alejandro R. ;
Cubitto, Maria A. ;
Ferrero, Marcela ;
Rodriguez, Maria S. .
INTERNATIONAL BIODETERIORATION & BIODEGRADATION, 2006, 57 (04) :222-228
[8]  
Gu Chuanhui, 2000, ECOL SCI, V19, P67
[9]  
Gu GZ, 2013, CHINA PET PROCESS PE, V15, P82
[10]  
Guo Ting Guo Ting, 2009, Research of Environmental Sciences, V22, P1472