Carbon spectrum utilization by an indigenous strain of Pseudomonas aeruginosa NCIM 5514: Production, characterization and surface active properties of biosurfactant
Graphical abstract
Introduction
The demand for bio-based processes and materials in petroleum industry has significantly increased during last decade (Muller et al., 2012, Varjani and Upasani, 2016). Microorganisms present in oil polluted environments produce various bioactive compounds. Biosurfactant, a secondary metabolite is one of the several bioactive compounds that have attracted major interest and attention due to their structural and functional diversity (Soberon-Chavez et al., 2005, Janek et al., 2010, Muller et al., 2012). These natural compounds have many advantages over synthetic surfactants, such as lower toxicity, enhanced biodegradability, enhanced foaming capacity, high specificity, better environmental compatibility and ability to be synthesized from renewable feed-stocks (Desai and Banat, 1997, Janek et al., 2010, Gudina et al., 2016). Bacterial species belonging to the genera Bacillus, Halomonas and Pseudomonas can grow exclusively on hydrocarbons and produce biosurfactant(s) (Satpute et al., 2008). Pseudomonas is one of the most prominent hydrocarbon utilizers and biosurfactant producer reported from hydrocarbon polluted sites (Deziel et al., 1996, Das and Mukherjee, 2005, Batista et al., 2006, Thavasi et al., 2011, Phan et al., 2013, Varjani and Upasani, 2016). Biosurfactants have extensive applications in many industries such as petroleum, food, beverage, cosmetics, detergents, pharmaceuticals, lubricant formulation, mining and metallurgy and environmental protection as well as management, etc. (Benincasa et al., 2004, Rahman et al., 2003). They can be used as emulsifiers, de-emulsifiers, wetting, dispersing and foaming agents (Moya et al., 2015, Gudina et al., 2016).
Effective screening methodologies and improved purification techniques plays critical role in achieving desired quality and quantity of biosurfactant (Satpute et al., 2008). Screening methods used for biosurfactant producers are hemolytic activity, cetyltrimethyl ammonium bromide (CTAB) agar plate method, drop collapse, oil spread, emulsification activity, surface tension and interfacial tension (Satpute et al., 2008, Varjani et al., 2014).
The structure and production of this secondary metabolite strictly depends on medium composition, e.g. carbon and nitrogen sources (Rahman et al., 2002, Gudina et al., 2011). Microbial surfactants encompass a wide spectrum of molecules, such as lipopeptides, glycolipids, phospholipids, fatty acids, neutral lipids and polymeric biosurfactants (Rahman et al., 2003, Janek et al., 2010, Moya et al., 2015). Glycolipids are one of the most promising biosurfactants. They consist of carbohydrates and long-chain aliphatic or hydroxyaliphatic acids (Gudina et al., 2016). The most effective glycolipids with reference to surface active properties are trehalolipids of Rhodococcus erythropolis, sophorolipids of Candida bombicola, and rhamnolipids of Pseudomonas sp. (Wei et al., 2005, Raza et al., 2009, Varjani and Upasani, 2016). Rhamnolipids (RLs) produced by Pseudomonas strains have a glycosyl head group (a rhamnose moiety) and a 3-(hydroxyalkanoyloxy) alkanoic acid (HAA) (Soberon-Chavez et al., 2005, Gudina et al., 2016). Muller et al. (2012), reviewed that shake flask experiments are more useful for studying optimization of rhamnolipid production. They have critically reviewed factors influencing rhamnolipid production in Pseudomonas sp., and reported it to be capable of using both water soluble carbon substrates, such as glucose, glycerol, mannitol and fructose (Gudina et al., 2011, Hamzah et al., 2013, Varjani et al., 2014) as well as water immiscible n-alkanes to produce rhamnolipid (Varjani et al., 2013, Varjani et al., 2015). Not only the type of carbon and nitrogen source but also the respective C/N ratio strongly influence total rhamnolipid production (Wu et al., 2008, Muller et al., 2012).
Most methods for recovery of rhamnolipids have been very well reviewed (Desai and Banat, 1997, Heyd et al., 2008, Pornsunthorntawee et al., 2008). One of the easiest methods for recovery was precipitation by acid (Zhang and Miller, 1992; Deziel et al., 1996; Varjani and Upasani, 2016) or aluminium sulphate (Schenk et al., 1995), the latter precipitates the rhamnolipid by salting out process which can be recovered by centrifugation. However, solvent extraction is the most adopted method (Schenk et al., 1995, Varjani and Upasani, 2016). Extracted biosurfactant can be characterized by chromatographic and/or spectrophotometric techniques, viz. Thin layer chromatography (TLC), Fourier transform infrared spectroscopy (FTIR), Electrospray ionization mass spectrometry (ESI-MS), High-performance thin layer chromatography (HP-TLC), High performance liquid chromatography – mass spectrometry (HPLC-MS), Liquid chromatography – mass spectrometry (LC–MS) and Nuclear magnetic resonance (NMR), etc. (Rahman et al., 2002, Benincasa et al., 2004, Abdel-Mawgoud et al., 2009, Raza et al., 2009; Lotfabad et al., 2010, Varjani and Upasani, 2016).
In the present investigation, carbon spectrum utilization and biosurfactant production by P. aeruginosa NCIM 5514 has been studied. Physico-chemical properties of the biosurfactant such as surface activity (minimum surface tension and critical micelle dilution) and emulsification activity of the cell free supernatant have also been reported.
Section snippets
Bacterial strain and cultivation
Biosurfactant producing P. aeruginosa NCIM 5514 was isolated from petroleum-contaminated soil of South Gujarat, India. Sample collection, isolation, screening protocol and molecular identification of this isolate has been described earlier (Varjani et al., 2014, Varjani et al., 2015).
Inoculum preparation, preservation and maintenance
Axenic culture of P. aeruginosa NCIM 5514 was preserved in 20% (v/v) sterile glycerol solution at −70 °C. For routine experiments, the isolate was maintained on nutrient agar slant at 4 °C in refrigerator and
Results and discussion
Hydrocarbon degrading and biosurfactant producing P. aeruginosa NCIM 5514 was isolated from petroleum-contaminated soil sample of ONGC’s central tank farm (CTF) from South Gujarat, India. The isolate was screened by using seven different screening methods viz., primary (Hemolytic activity and Cetyltrimethyl ammonium bromide (CTAB) agar plate method), secondary (drop collapse, oil spread, emulsification index and surface tension) and tertiary (interfacial tension) as described elsewhere (Varjani
Conclusions
The culture of P. aeruginosa NCIM 5514 showed unique properties of carbon spectrum utilization, although glucose was best carbon substrate yielding high quantity of biosurfactant (3.178 ± 0.071 g/l) with desired surface active properties. Biosurfactant was composed of Rha-Rha-C10-C14:1 and Rha-C8-C10. Ex-situ bioaugmentation studies with production and surface active properties of biosurfactant produced by this bacterial isolate may open up avenues for its commercial feasibility in bioremediation
Acknowledgements
Authors are grateful to the Directorate of Forensic Science, Gandhinagar for providing FTIR analysis facilities, and scientists at Institute of Reservoir Studies (IRS), ONGC, Ahmedabad for their invaluable suggestions. We are also thankful to the Ahmedabad Education Society (AES) management, faculties and staff members of M. G. Science Institute, Ahmedabad, for their kind support.
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