- Research article
- Open Access
Diesel biodegradation capacities of indigenous bacterial species isolated from diesel contaminated soil
© Palanisamy et al.; licensee BioMed Central Ltd. 2014
- Received: 23 October 2013
- Accepted: 22 November 2014
- Published: 12 December 2014
Petroleum based products are the major source of energy for industries and daily life. Leaks and accidental spills occur regularly during the exploration, production, refining, transport, and storage of petroleum and petroleum products. In the present study we isolated the bacteria from diesel contaminated soil and screened them for diesel biodegradation capacity. One monoculture isolate identified by 16S rRNA gene sequence analysis to be Acinetobacter baumannii was further studied for diesel oil biodegradation. The effects of various culture parameters (pH, temperature, NaCl concentrations, initial hydrocarbon concentration, initial inoculum size, role of chemical surfactant, and role of carbon and nitrogen sources) on biodegradation of diesel oil were evaluated. Optimal diesel oil biodegradation by A. baumanii occurred at initial pH 7, 35°C and initial hydrocarbon concentration at 4%. The biodegradation products under optimal cultural conditions were analyzed by GC-MS. The present study suggests that A. baumannii can be used for effective degradation of diesel oil from industrial effluents contaminated with diesel oil.
- Acinetobacter baumannii
- Diesel oil
- Parameter optimization
- GC-MS analysis
Increasing industrial activities and technological progress have demanded a drastic increase in the use of petroleum hydrocarbons. There is considerable risk of environmental contamination during extraction, transportation, refining, storage, usage and ultimate disposal of these non-aqueous phase liquids composed of a large number of hazardous and toxic constituents . Marine and subsurface environment contamination has been reported due to accidental leakage of ships, cars, trucks, etc., leaks and spills from underground storage tank, pipelines and illegal disposals.
Diesel oil, a complex hydrocarbon pollutant is a mixture of alkanes and aromatic compounds that are reported frequently as soil contaminants . One of the best approaches to restoring contaminated soil is to make use of microorganisms able to degrade those toxic compounds in a bioremediation process . Bioremediation is a cost effective approach for cleaning up petroleum hydrocarbons from contaminated area because it is simple to maintain, applicable over large areas and leads to the complete destruction of the contaminant . Bioremediation of these pollutants are significantly affected by the inherent capabilities of the microorganisms to overcome the bioavailability limitations in multiphase environmental scenarios (oil–water–soil) and environmental factors such as temperature, pH, nutrients and electron acceptor availability .
The present study employed bacteria isolated from diesel contaminated soil for the biodegradation of diesel oil. Culture parameters for efficient degradation of diesel oil by a bacterial isolate were optimized.
Diesel oil used in this study was obtained from local petrol bunk, Tamil Nadu, India and sterilized by filter sterilization. All other chemicals used in the present study were of highest purity in grade.
Isolation, screening and identification
Bacterial species were isolated from diesel contaminated soil (petrol bunk, lorry shed, bus shed and automobile garage) from Sathyamangalam, Tamil Nadu, India ,. Soil samples were serially diluted, 100 μL of the diluted samples spread on the surface of nutrient agar plates and the plates incubated at 37°C for 24 h. The colonies obtained from the agar plates were further sub-cultured to obtain the pure colonies. The bacterial species were screened based on the ability of the bacterial species to degrade diesel oil. The degradation studies were performed in Mineral Salt Medium (MSM) that contains diesel oil as the sole source of carbon. The MSM consists of NH4 NO3 – 3 g/L, KH2PO4 - 0.5 g/L, K2HPO4.3H2O - 0.5 g/L and trace amounts of MgSO4.7H2O - 0.008 g/L, CuSO4.4H2O - 0.002 g/L, MnSO4.H2O - 0.002 g/L, FeSO4.7H2O - 0.002 g/L and CaCl2.2H2O - 0.002 g/L. The isolated bacterial species from different sites were cultured in Mineral Salt Medium containing diesel oil and incubated for 3 days at 37°C. The growths of the isolated bacterial species were monitored at regular intervals by measuring the optical density at 600 nm. Based on the growth of bacterial species on diesel oil degradation, the best degrader of diesel oil was selected and identified by 16S rRNA gene sequence analysis and used for further studies. Polymerase chain reaction (PCR) was conducted using 16S rRNA forward primer: AGA GTT TGA TCC TGG CTC AG and 16S rRNA reverse primer: ACG GCT ACC TTG TTA CGA CTT. The sequence of the PCR amplicon was submitted to GenBank to obtain accession number. NCBI BLASTN 2.2.26+ comparison software was used to reveal the identities of the isolate.
Effect of pH
The bacterial species were cultured in Luria Bertani (LB) broth and incubated at 37°C for 24 h. Then the culture was centrifuged at 5000 × g for 10 min, the pellets were collected and washed twice with saline to remove the trace amount of LB medium. To study the effect of pH on degradation, MSM supplemented with 1% of diesel oil was adjusted to different initial pH 4-11 using HCl or NaOH. Two hundred and fifty milliliter Erlenmeyer conical flasks containing 100 mL MSM were inoculated with 2 mL of 1.5 OD inoculum size of strain and incubated at 37°C under shaking condition (120 rpm). In the Control, without the inoculation of bacterial species was kept under similar condition. Samples were collected at regular intervals of time (6 h) up to 120 h.
Effect of temperature
The bacterial species was cultured in LB broth and was incubated at 37°C for 24 h. Then the culture was centrifuged at 5000 × g for 10 min, the pellets were collected and washed twice with saline to remove the trace amount of LB medium. To study the effect of temperature on degradation, MSM supplemented with 1% of diesel oil was incubated to different temperature such as 25, 30, 35, 40 and 45°C for optimizing the temperature. Two hundred and fifty milliliter Erlenmeyer conical flasks were inoculated with 1.5 optical density inoculum size which was prepared by diluting the bacterial culture with 0.9% NaCl and optical density value was adjusted to 1.5 using colorimeter. Flasks were kept under shaking condition (120 rpm). At regular intervals, the growth of the bacterial species was measured by recording the absorbance at 600 nm. In the control experiments, the flask containing inoculum devoid of diesel oil and the flasks containing diesel oil devoid of inoculum were run parallel at similar conditions.
Effect of initial hydrocarbon concentration
To study the effect of initial hydrocarbon concentration on degradation, MSM supplemented with different concentrations of diesel oil such as 1-5% was used as substrate. The flasks were inoculated with strain and incubated at 37°C under shaking condition (120 rpm). In the controls, without inoculation of strain were kept under similar conditions with inoculated flasks. Samples were collected at regular intervals of time (6 h) up to 120 h and analyzed for residual diesel oil.
Effect of initial inoculum size
To study the effect of initial inoculum concentration on degradation, MSM supplemented with 1% of diesel oil was inoculated with different inoculum quantity such as 0.1, 0.6, 1 and 1.5 OD (Absorbance at 600 nm). Two hundred and fifty milliliter Erlenmeyer conical flasks were incubated at 37°C under shaking condition (120 rpm). In the controls, without inoculation of strain were kept under similar conditions with inoculated flasks. Samples were collected at regular intervals of time (6 h) up to 120 h.
Role of chemical surfactants
To study the role of chemical surfactants on degradation, MSM supplemented with 4% of diesel oil along with 0.02% (w/v)/ (v/v) of different surfactants such as sodium dodecyl sulfate (SDS) and Tween 80 for enhancing the degradation. Two hundred and fifty milliliter Erlenmeyer conical flasks were inoculated with 1.5 OD inoculum size of strain flasks were inoculated with strain and incubated at 37°C under shaking condition (120 rpm). In the controls, without inoculation of strain, were kept under similar conditions with inoculated flasks. Samples were collected at regular intervals of time (6 h) up to 120 h.
Role of NaCl concentration
To study the role of NaCl concentration on degradation, MSM supplemented with 4% of diesel oil along with different concentrations of NaCl such as 1 mM, 100 mM, 500 mM, 1 M, 2 M and 5 M for checking the salinity condition. Two hundred and fifty milliliter Erlenmeyer conical flasks were inoculated with 1.5 OD inoculum size of bacterial culture. Flasks were inoculated with the bacterial strain and incubated at 37°C under shaking condition (120 rpm). In the controls, without inoculation of strain, were kept under similar conditions with inoculated flasks. Samples were collected at regular intervals of time (6 h) up to 120 h.
Effect of carbon and nitrogen sources
To study the effect of carbon and nitrogen sources on degradation, MSM supplemented with 4% of diesel oil along with 0.1% of carbon source such as Dextrose, Maltose and 0.1% of nitrogen source such Peptone and Yeast extract. Two hundred and fifty milliliter Erlenmeyer conical flasks were inoculated with 1.5 optical density inoculum size of strain was incubated at 37°C under shaking condition (120 rpm). In the controls, without inoculation of strain, were kept under similar condition with inoculated flasks. Samples were collected at regular intervals of time (6 h) up to 120 h.
Gas Chromatography- Mass Spectrometry (GC-MS) analysis
GC-MS analysis was done for detecting the degradation effect of diesel oil . After the incubation period, 5 mL of the cultures were extracted with two 20 mL volumes of n-hexane as a solvent by using separating funnels to remove cellular material. The residues were transferred to tarred vials and the volume of each extract was adjusted to 100 mL by adding further n-hexane. The vials were kept at 4°C until the gas chromatographic analysis. Uninoculated control was incubated in parallel to monitor abiotic losses of the substrate.
The degradation effect of diesel oil was detected by GC-MS (Thermo GC- Trace Ultra ver: 5.0, Thermo MS DSQ II), which was equipped with a DB 35- MS Capillary Standard Non-polar column (30 m × 0.25 mm × 0.25 μm). 1 microliter of the organic phase was analyzed by GC-MS. The gas chromatograph equipped with a split–split less injector (split ratios of 50:1) was used for the GC-MS analysis. The oven temperature was initially at 40°C and then programmed to 270°C at a rate of 8°C/min where it was held for 5 min. The temperatures of injector, transfer line and ionization source were all 250°C. The electron impact ionization was tuned at 70 eV and Helium was used as carrier gas with an average linear velocity of 1.0 mL/min.
Biodegradation capacity can be evaluated by performing a laboratory study or extensive waste characterization are put together with the bioremediation potential which depends on biodegradability of a specific type of hydrocarbon compound. In this section, isolation of pure cultures and effect of various parameters on hydrocarbon degradation, such as pH, temperature, NaCl concentration, initial hydrocarbon concentration, initial inoculums size, different carbon and nitrogen sources, and chemical surfactant were reported. The roles of biosurfactant effect in contaminant solubilization and biodegradation experiments also have been documented.
Isolation and identification of bacterial species
The isolated bacterial strain was screened based on the ability to utilize diesel oil. The isolate was identified by 16s rRNA analysis and the organism was Acinetobacter baumannii (Accession No. JQ975035). It utilizes hydrocarbons as the sole source of carbon and degrades it to maximum extent. Haritash and Kaushik  demonstrated that microorganisms are the main degraders of hydrocarbons. There are various abiotic factors which were optimized for maximum degradation of diesel oil.
Effect of pH
Effect of temperature
Effect of initial hydrocarbon concentration
Effect of initial inoculum size
Effect of NaCl concentrations
Role of carbon and nitrogen sources
Effect of chemical surfactants
Possibly, A. baumannii produced biosurfactants, which increased pseudo solubilization of diesel oil in the medium.
The present study focused on the degradation of diesel oil by a bacterial species isolated from diesel contaminated site. The success of oil bioremediation depends on our ability to optimize various physical, chemical, and biological conditions in the contaminated environment. Here, A. baumannii was able to degrade more than 99% of diesel oil at pH 7, 35°C and initial hydrocarbon concentration of 4%. The present study may be applied for the efficient removal of diesel oil containing industrial effluents released from petroleum refineries.
Authors thank Bannari Amman Institute of Technology, Sathyamangalam and SASTRA University, Thanjavur for providing facility to carry out the research work.
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