American Journal of Life Sciences
Volume 4, Issue 3, June 2016, Pages: 71-75

Ex Situ Biodegradation of Crude Oil Using Bacterial Isolates From Palm Oil Mill Effluent

Amechi Sampson Nwankwegu*, Emmanuel Michael Ikpe, Edna Ifeoma Chukwura, Richard Chidiebere Irondi,
Emmanuel Ifeanyi Obika

Department of Applied Microbiology and Brewing, Nnamdi Azikiwe University, Awka, Anambra State, Nigeria

Email address

(A. S. Nwankwegu)

*Corresponding author

To cite this article:

Amechi Sampson Nwankwegu, Emmanuel Michael Ikpe, Edna Ifeoma Chukwura, Richard Chidiebere Irondi, Emmanuel Ifeanyi Obika. Ex Situ Biodegradation of Crude Oil Using Bacterial Isolates From Palm Oil Mill Effluent. American Journal of Life Sciences. Vol. 4, No. 3, 2016, pp. 71-75. doi: 10.11648/j.ajls.20160403.11

Received: May 18, 2016; Accepted: May 27, 2016; Published: June 14, 2016


Abstract: Bioremediation of crude oil is quite unique, complex and relatively a slow process. They study area for this research work was a cottage industry located in Orumba North local government area of Anambra state, Nigeria. Evaluating the degradation potential of bacterial isolates from palm oil mill effluent on crude oil was conducted using standard methods, which includes screening, inoculums development and degradation studies to assess the most promising hydrocarbon degraders. Pooled samples collected from different points on the palm oil mill effluent disposal channels were inoculated mineral salt medium containing crude oil to assess degradation abilities of different bacterial species. Data indicated that these bacterial isolates were capable of thriving in the mineral salt medium between the pH range of 6.0-7.0 and bacterial proliferation were quantified by assessing the total viable count which ranged between 2 x 105-9 x 105 cfu/ml based on individual abilities to utilize crude oil as a sole carbon source.Cultural, morphological and biochemical characterizations were conducted on these isolates and Bergey’s manual of determinative bacteriology was used to suggest possible isolates, while molecular identification was done Centre for Agriculture and biosciences International (CABI), UK using partial 16S rDNA sequencing analysis and FASTA algorithm with prokaryote database from EBI. Escherichia fergosonii, Klebsiella variicola and Microccocus luteus were identified. Gas chromatographic analysis was applied to quantify the extent of degradation of crude oil by the isolates. All the isolated bacterial species displayed varying degree of crude hydrocarbon biodegradation.

Keywords: Palm Oil Mill Effluent, Crude Oil, Biodegradation, Bacteria, Ex Situ


1. Introduction

Crude oil is the major source of energy for industry and daily activities. Crude oil has been known to belong to the carcinogenic and neurotoxic family of organic pollutants. Accidental leakages and spillages occur at regular intervals during the exploration, production, refining, transportation and storage of crude oil. The amount of natural crude oil seepage was estimated to be 600,000 metric tons per year with a range of uncertainty of 200,000 metric tons per year [1]. Biodegradation of crude oil in natural ecosystem is a very slow and complex process thet requires the microbial transformation into a toxic and approximately non-toxic for as well as utilization as a biosynthetic substance [2].

Crude oil contaminated environments loose it fertility and agricultural seeds/plants also loose viability. Hence, inhibiting agricultural yields [3]. Bioremediation of crude oil contaminated environments has been very reliable due to the exposure of certain oil tolerant microbial species with biodegradable potentials or genetically modified for efficiency targeted towards oil utilization [4]. The application of microorganisms from palm oil mill effluent (POME) in the remediation of crude oil and other saturated/unsaturated hydrocarbon is a cutting-edge research area of solving crude oil spillage problems [5]. This research work is designed at determining the crude oil degrading bacterial isolates from palm oil mill effluent, examining the most suitable bacterial strain (s) to serve as potential seeders for crude oil contaminated sites was also evaluated.

2. Materials and Methods

2.1. Study Area

Small cottage oil palm processing industry was visited at Ufuma in Orumba North local government area of Anambra state, Nigeria. Pooled sample of raw palm oil mill effluent (POME) was collected from different points of the effluent discharge channels.

2.2. Sample Collection

Samples were collected into sterile plastic bottles specified for collecting liquid effluent samples after which they were carefully transported in an ice box at 4°C.

The crude oil used in this experiment was purchased from Eleme refinery in Port Harcout and stored in dark at ambient temperature throughout the study. Before used, the crude oil was sterilized at 121°C.

2.3. Physicochemical Analysis of Palm Oil Mill Effluent

Determination of pHof the sample using pH meter with 5:1 sample and distilled water ratio [6, 7].

2.4. Culturing Condition/Inoculation

The mineral salt medium contained the following salts; 1.2 g of KH2PO4, 1.8 g K2HPO4, 0.2 g MgSO4.7H2O, 4.0 g NH4Cl, 0.1 g Nacl 0.01 g FeSO4.7H2O dissolved in 1000ml distilled H2O. Nutrient broth and mineral salt medium (MSM) as modified by [8] were the liquid media and mineral salt oil agar was the only solid medium used. Bacterial isolates where maintained in a liquid mineral salt medium. The experiment was set-up by artificial pollution of the palm oil mill effluent with sterilized/filtered crude oil using test-tube method.

2.5. Screening Test for Hydrocarbon (Crude Oil) Utilization

The medium used to study the crude oil utilization ability by the bacterial isolates was a mineral salt medium containing 4% (v/v) (0.2ml in 5ml of mineral salt) of the crude oil. The medium was made out in 30ml test tube containing 5ml of the mineral salt medium and sterilized as stated before. Incubation was done at 30°C for two week with a loopful of bacterial isolates in a test tube shaker. The optical densities of the cultures were measures at 550nm with the aid of a colorimeter to study the efficiency of the isolates based on utilization abilities of the crude oil as a sole carbon source.

2.6. Inoculums Development

The most potent bacterial crude oil be grading isolate with high utilization ability was chosen for the degradation test. Mineral salt broth containing 0.3ml of crude oil was dispensed in 30ml quantities in 250ml Erlenmeyer flask with 5 loopful of the isolated and incubated at 30°C for 24hours at 120rpm in a shaker. pH (Fig. 1), optical densities (OD) at 550nm wavelength of individual flask (Fig. 2) and Total viable count (Fig. 3) were measured.

Figure 1. Change in pH with time in days.

Figure 2. Change in optical density with time in days.

Figure 3. Changes in total viable counts with time in days.

2.7. Biodegradation Study of Crude Oil

One and half ml of culture from inoculums development were added in 500ml conical flask containing sterilized 1.2ml crude oil in mineral salt and one flask served as a control were subjected to 15days incubation at 30°C, place in an orbital shaker at 180rpm. Samples were drawn at 5 days interval of incubation to measure the pH, total viable count, and optical density at 550nm wavelength with a colorimeter. The residual hydrocarbon content was examined/analyzed by gas chromatography as described by [9]. Measurement and observation were recorded.

2.8. Molecular Identification

Total of three bacterial isolates were submitted to Centre for Agriculture and Biosciences International (CABI) for microbial identification. Briefly, a unique CABI reference number (IMI number) was assigned to each of the samples. All the original samples were subjected to purity check. All procedures were validated and processing undertaken in accordance with CABI’s in-house method as documented in TPs 61-68 and TP70. Procedures involved the following steps: Molecular assays were carried out on each sample using nucleic acid as a template. A proprietary formulation [micro LYSIS®-PLUS (MLP) Microzone, UK)] was subjected to the rapid heating and cooling of a thermal cycler, to lyse cells and release deoxyribonucleic acid (DNA). Following DNA extraction, polymerase chain reaction (PCR) was employed to amplify copies of the rDNA invitro. The quality of the PCR product was assessed by undertaking gel electrophoresis. PCR purification step was carried out to remove unutilized dNTPs, primers, polymerase and other PCR mixture compounds and obtained a highly purified DNA template for sequencing. This procedure also allowed concentration of low yield amplicons. Sequencing reactions were undertaken using BigDye® Terminator v 3.1 kit from Applied Biosystems (Life Technologies, UK) which utilizes fluorescent labeling of the chain terminator ddNTPs, to permit sequencing. Removal of excess unincorporated dye terminators was carried out to ensure a problem-free electrophoresis of fluorescently labelled sequencing reaction products on the capillary array AB 3130 Genetic Analyzer (DS1) DyeEx™ 2.0 (Qiagen, UK). Modules containing prehydrated gel-filtration resin were optimized for clean-up of sequencing reactions containing BigDye® terminators. Dye removal was followed by suspension of the purified products in highly deionized formamide Hi-Di™ (Life Technologies, UK) to prevent rapid sample evaporation and secondary structure formation. Samples were loaded onto the AB 3130 Genetic Analyzer and sequencing undertaken to determine the order of the nucleotide bases, adenine, guanine, cytosine, and thymine in the DNA oligonucleotide. Following sequencing, identifications were undertaken by comparing the sequence obtained with those available in European Molecular Biology Laboratory (EMBL) via the European Bioinformatics Institute (EBI).

2.9. Statistical Analysis

Statistical analysis was carried out on the values obtained from the experimental study using statistical package for social science (SPSS; version 20.0) and analysis of variance (ANOVA). P-values test of significance carried out at 95% level of confidence using SPSS.

3. Results

3.1. Physicochemical Parameters of Soil Samples

The palm oil mill effluent pH ranged from 6.0-7.0 and temperature range of 28°C-32°C. Bacterial cell proliferation was quantified by assessing the total viable count which ranged from 2x105-9x105 cfu/ml. Three bacterial isolates were identified on the basis of their cultural, morphological and biochemical characterization and with reference to Bergey’s manual of determinative bacteriology (Table 1).

Table 1. Cultural, Morphological and Biochemical Characteristics of the Bacterial Isolates.

Parameters Isolate characteristics
1 2 3
Elevation Convex Convex Convex
Margin Irregular Undulated Irregular
Colour Gray Creamy Creamy yellow
Shape Regular Irregular Irregular Cluster (Tetra)
Gram stain - - +
Oxidase - - +
Indole production + - -
Methly Red + - -
Voges Proskaeur - + -
Citrate (simmon’s) - + -
Urease + + +
Motility + - -
Lactose + + +
Glucose + + -
Maltose - + -
Mannitol + + +
Sucrose - - -
Catalase + + +
Starch utilization - + -
Galactose - + -
Fructose + + -
Xylose + - -
Isolates identities Escherichia fergusonii Klebsiella variicola Micrococcus luteus

3.2. Bacterial Growth Dynamics

Microbial hydrocarbon degraders after an initial growth lag in week 1 experienced a steady rate of growth through week 2 to week 4 with an observable decline by week 6 of the study period. 16S and ITS rDNA sequencing analyses of the three bacterial isolates reported Escherichia fergosonii, Klebsiella Variicola, and Micrococcus luteus by 16S rDNA sequence analysis using the FASTA algorithm with the Prokaryote database from EBI. Top matches were mainly to the species Escherichia coli and Escherichia fergusonii although the validated type strains of these species did not feature in the top 250 results. However, there were many complete genome studies and published sequences for these species amongst the list of top matches. Several other closely related genera belonging to this family were also suggested with slightly lower probabilites. As there was no clear distinction between genera, identification is given to family level.

Top matches of >99% were made to members of this genus and include the validated type strains of K. pneumoniae (X87276) with a match of 99.2% and a sequence from the type strain of Klebsiella variicola DSM 15968 (CP010523) with a match of 100%. Top matches were made to Micrococcus luteus and the validated type strain sequence (AJ536198) gave a match of 99%.

3.3. TPH Quantification

The gas chromatographic technique carried out on the sample supernatant revealed that total petroleum hydrocarbon (TPH) content was greatest in the control (sample without bacterial seeding) with a value of 4362.60ml/kg, while the least TPH value was obtained in the sample in which Escherichia fergosonii, was added with value from 7653.69 mg/ml-153.07 mg/ml, showing a significant reduction in the oil content which was expressed statistically at p>0.05. The sample in which Klebsiella Variicola was added had higher hydrocarbon loss than the Micrococcus luteus seeded sample but was lower than Escherichia fergosonii, sample. Hyrocarbon loss from 7653.69 mg/ml-1301.13 mg/ml occurred in sample seeded with Klebsiella Variicola while hydrocarbon loss from 7653.69 mg/ml-1913.42 mg/kg in the sample seeded with Micrococcus luteus A remarkably low hydrocarbon loss from 7653.69mg/kg-4362.60 mg/ml was an indicative of a very slow biodegradative process in the microcosm. There a significant difference in the total hydrocarbon losses among the studied sample at p>0.05. The duration of bacterial isolates exposed to crude oil determined their survival, as only crude oil degrading bacterial isolates had the potentials to tolerate/utilize crude oil as a carbon source. The specific hydrocarbonnoclastic microorganisms degraded phytane and pristine of the crude oil fractions. Escherichia fergosonii was observed to be the most effective bacterial isolate which showed 98% degradation ability and others; Klebsiella variicola showed 83% and Micrococcus luteus showed 75% of crude oil degradation within 15days in respect to the control (sterile liquid mineral salt medium and crude oil without bacterial isolates) which was 43%. The 43% crude oil loss in the control was attributed to natural process of volatilization which was remarkably low and poor. In other words, the bacterial population did not only speed up the process but resulted in high removal efficiencies.

4. Discussion

When accidental or indiscriminate crude oil spillages occur and pollute the natural environments, certain microbial pollution of different strains with the potential to degrade crude oil and other chemical pollutants colonize such environment (10). It is however, an important fact that the mineral salt medium used to culture crude oil (petroleum) degrading possesses significant selective effect on the proliferation of bacterial population (11). Statistical analysis showed a positive correlation between test microbial samples and control with significant value of p= 0.05.

The study has shown the degradative potentials of certain microbial stains in palm oil mill effluent that are capable of utilizing crude oil and the interrelationship of the microbial strains in the complex environment [12] [13]. A suitable environment that will expedite the degradation of crude oil by certain oleophilic microorganisms; pH, nutrient, (N, P, K), temperature and other growth factors are often needed to boost this biodegradation action and achieve desired results at a calculated time interval. In this course of research, knowledge obtained could assist in the biodegradation of crude oil contaminated sites by adopting the palm oil mill effluent microbial population as suitable hydrocarbon degraders to aid transformation of oil fractions into harmless compounds which are generally eco-friendly. It is important to note that introduction of bacterial isolates into hydrocarbon containing medium often results in temporary deceleration in growth of such microbial diversity (lag time) and once acclimation in the medium is initiated steady rate of growth is brought about due to utilization of the hydrocarbon contaminant as the sole source of energy and carbon (Log time). Once the hydrocarbon concentration in the microcosm depletes, cell decline often follows and later cell death due to starvation stress exerted on the hydrocarbonoclastic microorganisms that solely depended on the carbon content of the hydrocarbon contaminant [6] [14] [15]. Again, no bioremediation technology has been found to be 100% effective as the process is known to be accompanied by metabolites production which in itself can become inhibitory to hydrocarbon degraders. In the present study, even the most effective method (i.e. use of Escherichia fergosonii) was not 100% efficient but a significant removal efficiency (98%) was achieved. It is for this reason that the essence or goal of bioremediation using either limiting factors addition/biostimulation (nutrients) or use of microorganisms (bioaugmentation) is usually to increase biodegradtion speed and contaminant removal efficiency following a threatened hydrocarbon spill. All the bacterial seeded systems (Escherichia fergosonii, Klebsiella Variicola, Micrococcus luteus) resulted in remarkable hydrocarbon losess (98%, 83% and 75%) respectively except the control (43%) which was questionably low and insignificant.

5. Conclusion

At the end of this experimental study, hydrocarbon removal under natural system resulted in poor biodegradation performance. Bioaugmentation with some bacterial species generate significant hydrocarbon loses. It was concluded that palm oil mill effluent autochthonous bacterial population had high petroleum hydrocarbon degradation potential. Palm mill effluent therefore, serves as alternative source of exogenous/allochthonous bacterial hydrocarbon degraders with the ability to solving crude oil pollution in contaminated sites and to achieve a condition of immediate hydrocarbon remediation response results, Escherichia fergosonii, Klebsiella Variicola, Micrococcus luteus be used as microbial seeders.

Acknowledgments

We immensely thank Centre for Agriculture and Biosciences International (CABI) Microbial Identification Services United Kingdom for the molecular identification of the isolates. We also thank International Energy Services (IESL) ltd Port-Harcourt, River State Nigeria, for gas chromatographic analysis.


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