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Biodegradative Potentials of Phytase-producing Bacterial Isolates Recovered from Spent Engine Oils Polluted-Soils

Received: 9 December 2018     Accepted: 2 January 2019     Published: 29 January 2019
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Abstract

Microbial remediation of environmental contaminants such as spilled and used petroleum products is an increasing auspicious technique, owing to its associated low-cost and eco-friendly outcomes compared to other methods. For this purpose, recovered bacteria isolates from contaminated soils in automobile workshops were screened for phytase activity and hydrocarbon biodegradative ability. Presumptive bacterium with inherently high phytase activity and biodegradative potential was further characterized using 16S rRNA gene sequence analysis. Soil total petroleum hydrocarbon (TPH) was determined using gas chromatographic technique (GC-FID). The identities of the isolates recovered from the samples include; Bacillus subtilis, B. licheniformis, Pseudomonas aeruginosa, Escherichia coli, Corynebacterium variabilis, Micrococcus luteus and Proteus vulgaris. Of all the isolates, P. aeruginosa had the highest phytase activity after 48 h of incubation whereas, P. vulgaris recorded the least phytase activity. E. coli and B. subtilis showed active phytase activity at pH 5.0 and 40°C. While P. aeruginosa exhibited proficient degrading ability on crude oil and spent engine oil at all days of incubation, E. coli and C. variabilis showed the most inaptitude. The 16S rRNA gene analysis shows that the isolate obtained from the automobile workshop is of the genus P. aeruginosa with reference to ATCC 27853. The TPH of the contaminated soils ranged from 545,168 to 856,328 Mg/kg. This study reveals the degradative potential of P. aeruginosa as suitable candidate in bioremediation of crude oil contaminated sites.

Published in Frontiers in Environmental Microbiology (Volume 4, Issue 5)
DOI 10.11648/j.fem.20180405.11
Page(s) 115-123
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2019. Published by Science Publishing Group

Keywords

Bacteria, Biodegradation, Bonny Light Crude Oil, Phytase

References
[1] Sei A., Fathepure B. Z. (2009). Biodegradation of BTEX at high salinity by an enrichment culture from hypersaline sediments of Rozel Point at Great Salt Lake. J. Appl. Microbiol. 107, 2001-2008
[2] Chen, Q., Li, J., Liu, M., Sun, H. and Bao, M., 2017. Study on the biodegradation of crude oil by free and immobilized bacterial consortium in marine environment. PloS one, 12 (3), p.e0174445.
[3] Cervantes, F. J., Duong-Dac, T., Roest, K., Akkermans, A. D. L., Lettinga, G. and Field, J. A., 2003. Enrichment and immobilization of quinone-respiring bacteria in anaerobic granular sludge. Water Science and Technology, 48 (6), pp. 9-16.
[4] Dasgupta, D., Ghosh, R. and Sengupta, T. K., 2013. Biofilm-mediated enhanced crude oil degradation by newly isolated Pseudomonas species. ISRN biotechnology, 2013.
[5] Sorkhoh, N. A., Al‐Hasan, R. H., Khanafer, M. and Radwan, S. S., 1995. Establishment of oil‐degrading bacteria associated with cyanobacteria in oil‐polluted soil. Journal of Applied Bacteriology, 78 (2), pp. 194-199.
[6] Das, K. and Mukherjee, A. K., 2007. Crude petroleum-oil biodegradation efficiency of Bacillus subtilis and Pseudomonas aeruginosa strains isolated from a petroleum-oil contaminated soil from North-East India. Bioresource technology, 98 (7), pp. 1339-1345.
[7] Esmaeil, A. S., Drobiova, H. and Obuekwe, C., 2009. Predominant culturable crude oil-degrading bacteria in the coast of Kuwait. International Biodeterioration & Biodegradation, 63 (4), pp. 400-406.
[8] Supaphol, S., Panichsakpatana, S., Trakulnaleamsai, S., Tungkananuruk, N., Roughjanajirapa, P. and O'Donnell, A. G., 2Li006. The selection of mixed microbial inocula in environmental biotechnology: example using petroleum contaminated tropical soils. Journal of Microbiological Methods, 65 (3), pp. 432-441.
[9] Lei, X. G., Weaver, J. D., Mullaney, E., Ullah, A. H. and Azain, M. J., 2013. Phytase, a new life for an “old” enzyme. Annu. Rev. Anim. Biosci., 1 (1), pp. 283-309.
[10] Hayes, J. E., Simpson, R. J. and Richardson, A. E., 2000. The growth and phosphorus utilisation of plants in sterile media when supplied with inositol hexaphosphate, glucose 1-phosphate or inorganic phosphate. Plant and Soil, 220 (1-2), pp. 165-174.
[11] Weaver, J. D., Ullah, A. H., Sethumadhavan, K., Mullaney, E. J. and Lei, X. G., 2009. Impact of assay conditions on activity estimate and kinetics comparison of Aspergillus niger PhyA and Escherichia coli AppA2 phytases. Journal of agricultural and food chemistry, 57 (12), pp. 5315-5320.
[12] Ekundayo, F. O. and Osunla, C. A., 2013. Phytase activity of fungi from oil polluted soils and their ability to degrade bonnylight crude oil. African Journal of Biotechnology, 12 (36).
[13] Sanbuga, E., Nadaroglu, H., Dikbas, N., Senol, M. and Cetin, B., 2014. Purification, characterization of phytase enzyme from Lactobacillus plantarum bacteria and determination of its kinetic properties. African Journal of Biotechnology, 13 (23).
[14] Chu J, Chung S, Tseng M, Wen C, Chu W. 2001. Phytase-producing bacteria, phytase and production method of phytase. United States Patent 6235517.
[15] Jensen, V., 1962. The dilution plate count technique for the enumeration of bacteria and fungi in soil. Zbl Bakteriol Parasitenkde, 116, pp. 13-32.
[16] Kerovuo, J., Lauraeus, M., Nurminen, P., Kalkkinen, N. and Apajalahti, J., 1998. Isolation, characterization, molecular gene cloning, and sequencing of a novel phytase from Bacillus subtilis. Applied and environmental microbiology, 64 (6), pp. 2079-2085.
[17] Yanke, L. J., Bae, H. D., Selinger, L. B. and Cheng, K. J., 1998. Phytase activity of anaerobic ruminal bacteria. Microbiology, 144 (6), pp. 1565-1573.
[18] Engelen, A. J., Randsdorp, P. H. and Smit, E. L., 1994. Simple and rapid determination of phytase activity. Journal of AOAC International, 77 (3), pp. 760-764.
[19] Gulati, H. K., Chadha, B. S. and Saini, H. S., 2007. Production and characterization of thermostable alkaline phytase from Bacillus laevolacticus isolated from rhizosphere soil. Journal of industrial microbiology & biotechnology, 34 (1), pp. 91-98.
[20] Zajic, J. E. and Supplisson, B., 1972. Emulsification and degradation of “Bunker C” fuel oil by microorganisms. Biotechnology and Bioengineering, 14 (3), pp. 331-343.
[21] Eja, M. E., Udo, S. M. and Asikong, B. E., 2003. Bioremediation potential of Bacillus species in oil-polluted soil from auto-mechanic workshops in Calabar, Nigeria. Afr. J. Environ. Pollut. Health, 2 (1), pp. 11-18.
[22] Adesodun, J. K. and Mbagwu, J. S. C., 2008. Biodegradation of waste-lubricating petroleum oil in a tropical alfisol as mediated by animal droppings. Bioresource technology, 99 (13), pp. 5659-5665.
[23] Hassanein, W. A. 2009. Molecular Identification of Antibiotics Resistant Pseudomonas aeruginosa Wt. Australian Journal of Basic and Applied Sciences, 3 (3), 2144-2153.
[24] Cabral, M. G., Viegas, C. A., Teixeira, M. C. and Sa-Correia, I., 2003. Toxicity of chlorinated phenoxyacetic acid herbicides in the experimental eukaryotic model Saccharomyces cerevisiae: role of pH and of growth phase and size of the yeast cell population. Chemosphere, 51 (1), pp. 47-54.
[25] Ijah, U. J. J. and Abioye, O. P. 2003. Assessment of physicochemical and microbiological properties of soil 30 months after kerosene spill. Journal of Research in Science and Management. 1 (1): 24-30.
[26] Maier, R. M. and Pepper, I. L., 2015. Bacterial growth. In Environmental Microbiology (Third Edition) (pp. 37-56).
[27] Mukhametzyanova, A. D., Akhmetova, A. I. and Sharipova, M. R., 2012. Microorganisms as phytase producers. Microbiology, 81 (3), pp. 267-275.
[28] Hosseinkhani, B. and Hosseinkhani, G., 2009. Analysis of phytase producing bacteria (Pseudomonas sp.) from poultry faeces and optimization of this enzyme production. African Journal of Biotechnology, 8 (17).
[29] Powar, V. K. and Jagannathan, V. E. N. K. A. T. A. R. A. M. A. N., 1982. Purification and properties of phytate-specific phosphatase from Bacillus subtilis. Journal of Bacteriology, 151 (3), pp. 1102-1108.
[30] Tung, E. T., Ma, H. W., Cheng, C., Lim, B. L. and Wong, K. B., 2008. Stabilization of beta-propeller phytase by introducing Xaa→ Pro and Gly→ Ala substitutions at consensus positions. Protein and peptide letters, 15 (3), pp. 297-299.
[31] Kim, M. S., Weaver, J. D. and Lei, X. G., 2008. Assembly of mutations for improving thermostability of Escherichia coli AppA2 phytase. Applied microbiology and biotechnology, 79 (5), p. 751.
[32] Yoon, S. J., Choi, Y. J., Min, H. K., Cho, K. K., Kim, J. W., Lee, S. C. and Jung, Y. H., 1996. Isolation and identification of phytase-producing bacterium, Enterobacter sp. 4, and enzymatic properties of phytase enzyme. Enzyme and microbial technology, 18 (6), pp. 449-454.
[33] Gibson, D. T. 1984. Microbial degradation of organic compounds. New York, Marcel Dekker. www.google.com. pp. 3-15.
[34] Mullaney, E. J. and Ullah, A. H., 2003. The term phytase comprises several different classes of enzymes. Biochemical and biophysical research communications, 312 (1), pp. 179-184.
[35] Singh, S. N., Kumari, B. and Mishra, S., 2012. Microbial degradation of alkanes. In Microbial degradation of xenobiotics (pp. 439-469). Springer, Berlin, Heidelberg.
[36] Khan, S. R., Kumar, J. I., Kumar, R. N. and Patel, J. G., 2013. Physicochemical properties, heavy metal content and fungal characterization of an old gasoline-contaminated soil site in Anand, Gujarat, India. Environmental and Experimental Biology, 11, pp. 137-143.
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    Osunla Charles Ayodeji. (2019). Biodegradative Potentials of Phytase-producing Bacterial Isolates Recovered from Spent Engine Oils Polluted-Soils. Frontiers in Environmental Microbiology, 4(5), 115-123. https://doi.org/10.11648/j.fem.20180405.11

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    Osunla Charles Ayodeji. Biodegradative Potentials of Phytase-producing Bacterial Isolates Recovered from Spent Engine Oils Polluted-Soils. Front. Environ. Microbiol. 2019, 4(5), 115-123. doi: 10.11648/j.fem.20180405.11

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    AMA Style

    Osunla Charles Ayodeji. Biodegradative Potentials of Phytase-producing Bacterial Isolates Recovered from Spent Engine Oils Polluted-Soils. Front Environ Microbiol. 2019;4(5):115-123. doi: 10.11648/j.fem.20180405.11

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  • @article{10.11648/j.fem.20180405.11,
      author = {Osunla Charles Ayodeji},
      title = {Biodegradative Potentials of Phytase-producing Bacterial Isolates Recovered from Spent Engine Oils Polluted-Soils},
      journal = {Frontiers in Environmental Microbiology},
      volume = {4},
      number = {5},
      pages = {115-123},
      doi = {10.11648/j.fem.20180405.11},
      url = {https://doi.org/10.11648/j.fem.20180405.11},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.fem.20180405.11},
      abstract = {Microbial remediation of environmental contaminants such as spilled and used petroleum products is an increasing auspicious technique, owing to its associated low-cost and eco-friendly outcomes compared to other methods. For this purpose, recovered bacteria isolates from contaminated soils in automobile workshops were screened for phytase activity and hydrocarbon biodegradative ability. Presumptive bacterium with inherently high phytase activity and biodegradative potential was further characterized using 16S rRNA gene sequence analysis. Soil total petroleum hydrocarbon (TPH) was determined using gas chromatographic technique (GC-FID). The identities of the isolates recovered from the samples include; Bacillus subtilis, B. licheniformis, Pseudomonas aeruginosa, Escherichia coli, Corynebacterium variabilis, Micrococcus luteus and Proteus vulgaris. Of all the isolates, P. aeruginosa had the highest phytase activity after 48 h of incubation whereas, P. vulgaris recorded the least phytase activity. E. coli and B. subtilis showed active phytase activity at pH 5.0 and 40°C. While P. aeruginosa exhibited proficient degrading ability on crude oil and spent engine oil at all days of incubation, E. coli and C. variabilis showed the most inaptitude. The 16S rRNA gene analysis shows that the isolate obtained from the automobile workshop is of the genus P. aeruginosa with reference to ATCC 27853. The TPH of the contaminated soils ranged from 545,168 to 856,328 Mg/kg. This study reveals the degradative potential of P. aeruginosa as suitable candidate in bioremediation of crude oil contaminated sites.},
     year = {2019}
    }
    

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  • TY  - JOUR
    T1  - Biodegradative Potentials of Phytase-producing Bacterial Isolates Recovered from Spent Engine Oils Polluted-Soils
    AU  - Osunla Charles Ayodeji
    Y1  - 2019/01/29
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    JF  - Frontiers in Environmental Microbiology
    JO  - Frontiers in Environmental Microbiology
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    AB  - Microbial remediation of environmental contaminants such as spilled and used petroleum products is an increasing auspicious technique, owing to its associated low-cost and eco-friendly outcomes compared to other methods. For this purpose, recovered bacteria isolates from contaminated soils in automobile workshops were screened for phytase activity and hydrocarbon biodegradative ability. Presumptive bacterium with inherently high phytase activity and biodegradative potential was further characterized using 16S rRNA gene sequence analysis. Soil total petroleum hydrocarbon (TPH) was determined using gas chromatographic technique (GC-FID). The identities of the isolates recovered from the samples include; Bacillus subtilis, B. licheniformis, Pseudomonas aeruginosa, Escherichia coli, Corynebacterium variabilis, Micrococcus luteus and Proteus vulgaris. Of all the isolates, P. aeruginosa had the highest phytase activity after 48 h of incubation whereas, P. vulgaris recorded the least phytase activity. E. coli and B. subtilis showed active phytase activity at pH 5.0 and 40°C. While P. aeruginosa exhibited proficient degrading ability on crude oil and spent engine oil at all days of incubation, E. coli and C. variabilis showed the most inaptitude. The 16S rRNA gene analysis shows that the isolate obtained from the automobile workshop is of the genus P. aeruginosa with reference to ATCC 27853. The TPH of the contaminated soils ranged from 545,168 to 856,328 Mg/kg. This study reveals the degradative potential of P. aeruginosa as suitable candidate in bioremediation of crude oil contaminated sites.
    VL  - 4
    IS  - 5
    ER  - 

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Author Information
  • Department of Microbiology, Adekunle Ajasin University, Akungba-Akoko, Nigeria

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