HYDROCARBONOCLASTIC POTENTIAL OF BACTERIA ISOLATED FROM HAIR SALON WASTEWATER IMPACTED SOILS

Authors

  • Dr Christy Etuk AKWA Ibom State Polytechnic, Ikot Ekpene Author
  • Nkeneke E. Akpainyang Akwa Ibom State Polytechnic, Ikot Ekpene, Akwa Ibom State Author

DOI:

https://doi.org/10.60787/

Keywords:

Hydrocarbonoclastic bacteria, dichlorophenol indophenol indicator, salon wastewater, polluted soil,

Abstract

The hydrocarbonoclastic potential of bacteria isolated from hair salon wastewater-impacted soils was studied. Isolation of hydrocarbonoclastic bacteria from hair salon wastewater-impacted soil (SWS) and non-salon wastewater-impacted soil (NWS) samples were determined. Total mean bacterial counts of the soil samples were carried out using standard microbiological techniques. The total bacterial counts were 1.2x106 ±0.5 and 8.0 ±0.2 x105 Cfu g-1 in the SWS and NWS, respectively. Hydrocarbonoclastic bacteria identified included Staphylococcus, Bacillus, Pseudomonas, Micrococcus, and Streptococcus spp. Utilization of some hydrocarbons tests were carried out on kerosene, petrol, diesel, and waste engine oil on the isolates under aerobic conditions and were determined using Dichlorophenol Indophenol indicator (DCPIP) in hydrocarbon medium and incubated for 48 hours at 30 C. Biosurfactants production potential using the drop collapse test indicated that most of the bacterial isolates which tested positive have good bio-surfactants production potentials. The result of the emulsification index, E24 % of diesel and petrol for Staphylococcus sp. was significantly higher (50.70± 1.21 and 51.50± 0.50 respectively) than that obtained for kerosene and waster-engine oil (31.40± 1.05 and 23.47± 0.57 respectively) (p<0.05).

 

In contrast, the amount of waste engine oil was significantly less than that of kerosene. There was no significant difference in emulsification index (p<0.05) between diesel (50.70± 1.21) and petrol (51.50± 0.50). Salon wastewater-impacted soils have been shown in this study to harbour bacteria with hydrocarbonoclastic potentials as indicated by the emulsification index E24% of the different isolates. The results suggest that the isolates are potential candidates for hydrocarbon utilization studies and application in bioremediation.

 

Author Biographies

  • Dr Christy Etuk , AKWA Ibom State Polytechnic, Ikot Ekpene

    Department of Biological Sciences 

     

  • Nkeneke E. Akpainyang, Akwa Ibom State Polytechnic, Ikot Ekpene, Akwa Ibom State

    Department of Biological Sciences

     

References

REFERENCES

Al-Saleh, H. J. ,and Drobiova, C. O. (2009).Predominant culturable crude oil degrading bacteria in the coast of Kuwait. International Biodetorioration and Biodegradation, 63(4),400-406.

Antia, S. P. (1990). Biodegradation of Bony light crude oil by Bacillus sp. and Pseudomonas species. Waste Management, 60(10),61-64.

Chaerum, S. K. , Tazaki, U. K ., Asada, R. R. and Kogure, O. K. (2004). Bioremediation of coastal areas 5 years after the Nakhodkaoil spill in the sea of Japan: isolation and characterization of hydrocarbon degradation.Bacteria Environ. International,30,911-922.

Cheesebrough, M. (2005).District laboratory practice in tropical countries(2nd part, pp23-39,372).Cambridge University press .

Diaz, E., Ferrandez, J. L. (2001). Biodegradation of aromatic compounds by E. coli. Microbiology,molecular biology review,65,523-569.

El-Gebaly, E. O. (2020).Screening of biosurfactant production by bacterial strains isolated from oil contaminated sites near gas stations in Egypt .Az. Journal of Pharmaceutical Science,61,134-145 . Holt, J. G., Kreig, N. R., Sneath, P. H. A., Staley, J. T. ,and Williams, S. T. (1994). Bergey’s manual of determinative bacteriology (9th ed., 894p). Lippincott; Williams and Wilkins.

Kubicki, S., Bollinger, A., Katzke, N., Jaeger, K., Loeschcke, A., and Thies S. (2019). Marine biosurfactants: Biosynthesis, structural diversity and biotechnological applications. Marine Drugs, 17(7), 408-420.

Lal, V. P. and Khama, T. C. (1996).Effect of hydrocarbon pollution on the microbial properties of a sandy and clay soil.Chemosphere, 66,1863-1871. Mahjoubi, M. , Jaouani, A., Guesmi, A., Ben Amor, S., Jouini, A., Cherif, H. A., Boudabous, A., Koubaa, N., and Cherif, A. (2013). “Hydrocarbonoclastic bacteria isolated from petroleum contaminated sites in Tunisia: Isolation, identification and characterization of the biotechnological potential”. New Biotechnology, 30(6), 723-733.

Nakuleshivas, D. J., Richa, S. S., and Subhash, C. Q. (2018). Isolation and identification of microorganism from playhouse agriculture soil of Rajasthan. Afri. J. Mocrobiol. Research,7(4),4886-4891.

Okpokwasili,G. C. and Okorie, B. B.(1990).Degradation of aldrin by bacterial isolates. Nigerian J. of Technological Research, 2, 1-6

Olayide, F. O., Angus, C. O., and Simon, C. N. (2010). Bioremediation of crude petroleum polluted stagnant water. Journal of Botany and Microbiology, 2(11), 81-86.

Onwusah, B. N., Amafina, I. M., and Obire, O. (2015). Microflora of different wastewater from some hairdressing salons in Port Harcourt in Nigeria. Current Studies in Comparative Education, Science and Tech, 2(2), 303-311..

Pathak, S. H., and Jaroli, D. P. (2014).Factors affecting the rate of biodegradation of polycyclic aromatic hydrocarbons(PAHs).Journal of Bioremed. Biodegradation, 1(3),124-133..

Rahman, K. S. (2002). Bioremediation of gasoline contaminated soil by a bacterial consortium amended with poultry litter,coir pith and rhamnolipid biosurfactant. Bioresource Technology, 81(3), Rosenberg, E. (1998). The hydrocarbon-oxidizing bacteria. In E. Rosenberg,E. DeLong and P. Thompson, S. Lore and E. Stackebrandt (Eds.),The prokaryotes(4thEd.,Chapter 5).Springer.Saminathan, P., and Rajendran, P. (2014). Screening and identification of potential biosurfactant producing microorganisms isolated from oil contaminated soil. International Journal of Pharma and Biosciences, 5(1), 1096-1106.

Shahid, M , Al-surhanee, A., Kouadri, F., Ali, S., Nawaz, N., Afzal, M., Rizwan, M., Ali, B. and Spoliman, M. (2020).Role of microorganisms in bioremediation nof wastewater in floating wetlands: Review.Sustainabiklity,12: 55-59. Doi-10.3390/su12145559.

Sidkey, N. M., Mohamed, H. F. , and Elkhouly, H. I. (2016). Evaluation of different screening methods for biosurfactant producers isolated from contaminated Egyptian samples grown on industrial olive oil processing waste.British Microbiology Research Journal,17(4),1-9.

Smulek, W., Zdarta, A., Grzwaczyk, A., Guzik, U., Siwińska-Ciesielczyk, K., Ciesielczyk, F., Strzemiecka, B., Jesionowski, T., Voelkel, A., and Kaczorek, E. (2020).Evaluation of the physico-chemical properties of hydrocarbons-exposed bacterial biomass. Journal of Biointerfaces,196, 111-116.

Willey, J. M., Sherwood, L. M., Woolverton, C. J., Presscott, B., Harley, R. and Klein, A. (2008).Microbiology(seventh edition, pp.643-742).

McGrawHill. Youssef, N.H., Duncan, K. E., Nagle, D. P., Savage, K. N., and Knapp, R. M. (2004).Comparison of methods to detect biosurfactant production by diverse microorganisms.Journal of Microbial Methods,56,339-347.

Downloads

Published

2024-12-16

How to Cite

HYDROCARBONOCLASTIC POTENTIAL OF BACTERIA ISOLATED FROM HAIR SALON WASTEWATER IMPACTED SOILS. (2024). Akwapoly Journal of Communication & Scientific Research, 9(1). https://doi.org/10.60787/