Degradation of Benzo [a] Pyrene by a novel strain Bacillus subtilis BMT4i (MTCC 9447)

ENVIRONMENTAL MICROBIOLOGY

Degradation of Benzo [a] Pyrene by a novel strain Bacillus subtilis BMT4i (MTCC 9447)

Madhuri Kaushish Lily^I, Ashutosh Bahuguna^I, Koushalya Dangwal^I,*, Veena Garg^II

^IDepartment of Biotechnology, Modern Institute of Technology (MIT), Dhalwala, Rishikesh-249201, Uttarakhand, India

IIDepartment of Bioscience and Biotechnology, Banasthali University, Rajasthan, India

ABSTRACT

Benzo [a] Pyrene (BaP) is a highly recalcitrant, polycyclic aromatic hydrocarbon (PAH) with high genotoxicity and carcinogenicity. It is formed and released into the environment due to incomplete combustion of fossil fuel and various anthropogenic activities including cigarette smoke and automobile exhausts. The aim of present study is to isolate bacteria which can degrade BaP as a sole source of carbon and energy. We have isolated a novel strain BMT4i (MTCC 9447) of Bacillus subtilis from automobile contaminated soil using BaP (50 μg /ml) as the sole source of carbon and energy in basal salt mineral (BSM) medium. The growth kinetics of BMT4i was studied using CFU method which revealed that BMT4i is able to survive in BaP-BSM medium up to 40 days attaining its peak growth (10²⁹ fold increase in cell number) on 7 days of incubation. The BaP degradation kinetics of BMT4i was studied using High Performance Liquid Chromatography (HPLC) analysis of BaP biodegradation products. BMT4i started degrading BaP after 24 hours and continued up to 28 days achieving maximum degradation of approximately 84.66 %. The above findings inferred that BMT4i is a very efficient degrader of BaP. To our best of knowledge, this is the first report showing utilization of BaP as a sole source of carbon and energy by bacteria. In addition, BMT4i can degrade a wide range of PAHs including naphthalene, anthracene, and dibenzothiophene therefore, it could serve as a better candidate for bioremediation of PAHs contaminated sites.

Key words: Benzo [a] Pyrene (BaP), polycyclic aromatic hydrocarbon (PAH), Bacillus subtilis BMT4i, colony forming units/ml (CFU/ml), high performance liquid chromatography (HPLC)

Introduction

High molecular weight (HMW) polycyclic aromatic hydrocarbons (PAHs) are considered environmentally significant because of their potential toxicity to the higher organisms and resistance to microbial attack (5). Usually, an increase in the number of fused rings increases the chemical stability and hydrophobicity of PAH molecules, making them more amenable to biodegradation. In mammals, PAHs are shown to possess high mutagenic, teratogenic or carcinogenic properties (9, 14, 24) therefore, many PAHs including phenanthrene, acenaphthene, acenaphthylene, fluoranthene, pyrene, benzo[a] pyrene (BaP) and benzo[a] anthracene are listed in the priority pollutant list of the United States Environmental Protection Agency (20, 26).

Benzo [a] Pyrene (BaP), a potent carcinogen is a pentacyclic high molecular weight PAH with high recalcitrant nature (4, 5, 24, 27). The natural sources of BaP are forest fires, volcanic eruptions, peat fires, burning of crude oil and shale oil, while anthropogenic sources include the incomplete combustion of fossil fuel, coke oven emissions, aluminum smelters, coal combustion and conversion industries, incinerators, vehicle exhausts, cigarette, cigar and marijuana smoke (2, 3). From contaminated soil and water, BaP enters into the food chain and metabolized to its ultimate genotoxic form which then interacts with nucleic acids and proteins forming highly reactive macromolecular adducts resulting in BaP induced toxicity, mutagenesis and carcinogenesis in mammals (8, 12, 23). In contrast to the mammalian system, some algal, fungal and bacterial species are shown to degrade BaP co-metabolically, alone or in a co-culture (16, 18, 22). However, bacteria capable of utilizing BaP as a sole source of carbon and energy have never been demonstrated.

In view of the above, the present study is focused on the isolation and characterization of bacterial species capable of degrading BaP as the sole source of carbon and energy.

Materials and Methods

Chemicals and Reagents

The benzo (a) pyrene (BaP) (99.9%), benzo (a) pyrene cis- 7, 8 dihydrodiol, naphthalene, anthracene and dibenzothiophene (purity > 98%) were purchased from Supelco, USA. Tryptone, peptone, beef extracts, bacto-agar, yeast extracts and staining reagents were obtained from HiMedia Laboratory Pvt. Ltd. India. The general chemicals including constituents of basal salt mineral media (BSM) and solvents of analytical grade were purchased from Glaxo Pvt. Ltd. India and Merck Pvt. Ltd. India.

Preparation of Media

BSM (pH 7.0) was prepared by dissolving 0.38g KH₂PO₄, 0.6g K₂HPO₄, 0.2g MgSO₄.7H₂O, 1.0g NH₄Cl and 0.05g FeCl₃ in one liter double distilled water and autoclaved. Autoclaved nutrient broth contained 5g peptone, 5g NaCl, 3g beef extracts, 3g yeast extracts per liter double distilled water. All the solid media contained 1.5% agar along with BSM or nutrient broth. The stock solution (10 mg/ml) of BaP, benzo (a) pyrene cis- 7, 8 dihydrodiol, naphthalene, anthracene and dibenzothiophene were made in dimethylformamide and was sterilized by Millipore micro syringe filter assembly (0.45µm pore size).

Isolation of BaP degrading bacteria

The subsurface PAH-contaminated soil sample was collected from automobile workshop situated in Srinagar Garhwal, Uttarakhand, India.

The automobile contaminated soil was suspended in BSM (10% w/v) with vigorous stirring for 10 minutes and then allowed to settle at room temperature for one hour. The supernatant was serially diluted up to 10^-9. 100 μl inoculum of 10^-7 diluted soil suspension was spread on BSM- agar plate supplemented with BaP (50 μg/ml) as sole source of carbon and energy and incubated for 1 week at 37ºC inside the clear plastic bags to conserve moisture. The bigger size bacterial colonies which appeared on BSM-BaP plate were aseptically removed and reselected on BSM-BaP plate to obtain their pure culture. Single colony of each isolate is then inoculated in 10 ml nutrient broth and grown for 24 h at 37 ⁰C with constant shaking at 150 rpm (Remi, India, Model no. CIS-24). The cell suspensions were centrifuged at 8000 rpm for 10 minutes to obtain cell pellets of each soil isolate. The cell pellets were washed with BSM three times to remove the trace of nutrient broth and finally suspended in BSM. The optical densities of cell suspensions were adjusted to 1.0 approximately equal to the 10⁸ cells per ml. The ability of each soil isolate to grow in the presence of BaP was checked by inoculating 1 ml of each soil isolates (approx. 10⁸ cells/ml) into the 10 ml of BSM supplemented with BaP (50 μg/ml) as the sole source of carbon and energy. The cultures were incubated at 37⁰C for 1 week with constant shaking at 150 rpm in dark to avoid photolysis of BaP. 100 μl each of grown culture were taken out and diluted serially upto 0- 10^-20. 100 μl of each serially diluted culture were spread over BSMG plate (BSM containing glucose 10gL^-1) and incubated for 12-24 h at 37⁰C. The colonies were counted and CFU/ml was determined for each culture. In addition, the cultures were virtually examined for the turbidity at 600 nm using UV-Vis Spectrophotometer (Systronics, India, model no. 119). The best BaP degrader (BMT4i) was selected on the basis of its highest growth in BaP-BSM as indicated by highest CFU/ml (Table 1) and turbidity at A_600.

Identification and characterization of the BaP degrading bacterium BMT4i

The BMT4i was maintained on BaP supplemented BSM agar plates. The identification and characterization of the BMT4i was done on the basis of the cell and colony morphology, growth characteristics, motility, various staining reactions and various biochemical tests as given by Bergey's Manual of Systematic Bacteriology (6) as mentioned in the results (Table 2). For molecular characterization, BMT4i genomic DNA was isolated and approximately 1.5 kb 16S rDNA gene fragment was amplified by PCR (Biometra, Germany, model Tpersonal) using the forward primers 5'-ACCACATGCAAGTGCAACG-3' and reverse primer 5'- ACGGGCGGTGTGTAC-3'. The amplified product was purified by agarose gel electrophoresis and clone into the pGEM-T vector (Promega Scientific, Santa Barbara, California). Both the strands of cloned approximately 1.5 kb 16S rDNA gene fragment were sequenced using sequencing facility provided by Bangalore Genei, India. The approximately 1.5 kb region of the 16S rDNA gene was used for alignment and phylogenetic analysis. The sequences were compared to those in GenBank by using the Blast Alignment Tool and the software based on "Neighbor Joining Method" was used to construct phylogenetic tree. The aligned sequences were deposited to the GenBank, EMBL and DDBJ libraries. The culture of BMT4i was deposited in Microbial Type Culture Collection (MTCC), Institute of Microbial Technology (IMTECH), Chandigarh, India.

Assessment of degradation ability of BMT4i

All the operations were carried out in dim yellow light in order to avoid photo degradation of BaP. All the experiments were set up in triplicates. A single colony of BMT4i maintained in BaP-BSM agar plate was inoculated in 10 ml nutrient broth and grown at 37⁰C with constant stirring till the A₆₀₀ reaches to 1.0 (approx. 1x10⁸ cells/ml). The cell culture was centrifuged at 8000 rpm for 10 minutes and washed three times with BSM to remove trace of nutrient broth. The BMT4i cell number was adjusted to 10⁸ cells /ml in BSM. For the time course studies, 1 ml of BMT4i- BSM suspension was re-inoculated in various flasks (10⁷ cells /ml) containing 10 ml BSM supplemented with 50 μg/ml of BaP as the sole source of carbon and energy and incubated at 37ºC in incubator shaker at 120 rpm for various time periods along with their respective controls devoid of BMT 4i. At various time points (0, 12 h, 1, 2, 3, 7, 14, 21, 28, 35, 42 days), first of all, the A₆₀₀ was recorded and then CFU/ml of BMT4i was checked by removing 100 µl culture from all the experimental and control flask, diluting up to 10^-40 and plating over BSM-glucose agar plate. After 24 h, the numbers of colonies were counted and the log₁₀CFU/ml was calculated to obtain the growth curve. The respective cultures were then extracted twice with ethyl acetate (1:1 v/v), acidified to pH 4.0 with 0.1 N HCl and re-extracted twice with ethyl acetate to enhance the recovery of acidic metabolites. The entire triplicate extracts of respective time period were separately dried in rotary evaporator (Perfit, Ambala, India, model no. 951) and finally suspended in 1.0 ml of methanol. The recovery of biodegraded products by ethyl acetate extraction was found to be more than 96 %. The extent of BaP biodegradation was checked by quantifying left over BaP in methanol suspension of biodegraded extracts by HPLC analysis (13, 21). The reverse phase HPLC was done on commercial basis from Herbal Research and Development Institute (HRDI), Selaqui, Dehradun, India (HPLC system: Waters, USA, model no. 600 E pump with Photo Diode Array (PDA) detector). For that, 20 μl of the methanol dissolved extracts were injected into an HPLC system fitted with 5 μm particle diameter C₁₈ column. The elution gradient was programmed as follows (shown as percent [by volume] of methanol in water, acidified with 0.76 ml of H₃PO₄ liter ^-1): 50% for 2 min, linear gradient to 80% at 5% min^-1, holding at 80ºC for 16 min. The flow rate was kept at 1ml min-¹. Peaks were measured at 254 nm. The percent degradation of BaP was assessed by subtracting left over BaP in experiments (with BMT4i) from the respective controls (without BMT4i; recovered products were considered as 100%) at various time intervals (0, 12 h, 1, 2, 3, 7, 14, 21, 28, 35, 42 days).

Viability of BMT4i in the presence of other PAH

To check the viability of BMT4i in the presence of other PAHs, the overnight grown nutrient broth culture of BMT4i was washed three times with BSM and spread over BSM plates containing 500 μg/ml each of naphthalene, anthracene and dibenzothiophene (DBT) as the sole sources of the carbon and energy. After 24-48 h of incubation at 37ºC, the plates were observed for appearance of colonies. The CFU/ml was determined by inoculating thoroughly washed BMT4i culture (10⁷cells/ml) inBSM broth containing naphthalene, anthracene and dibenzothiophene (DBT) (500 μg/ml) in separate flasks and CFU/ ml was calculated after 7 day of incubation at 37ºC, 150 rpm.

Results

Isolation and identification of a BaP degrading bacterium

The BaP degrading bacterial colonies were isolated from automobile contaminated soil by standard culture enrichment techniques with BaP as the sole source of carbon and energy. Among various BaP degrading bacterial isolates, the BMT4i was selected as best BaP degrader on the basis of its highest growth in BaP-BSM as indicated by highest CFU/ml (Table1) and turbidity at A₆₀₀ after 7 days of growth.BMT4i was further characterized on the basis of cell and colony morphology, various staining and biochemical activities (Table 2) and 16S rDNA gene analysis. The cellular and colony morphology, various staining reactions and biochemical reactions identified BMT4i as a Bacillus subtilis. Two of its unique biochemical characteristics viz-abundant mucilage secretion and urease positive reaction indicated BMT4i as a novel strain of Bacillus subtilis. The sequence and comparative phylogenetic analysis of PCR amplified 16S rDNA gene fragment of BMT4i to those in GenBank confirmed BMT4i as the closest homologue and a novel strain of Bacillus subtilis (NCBI GenBank Accession No. DQ911348, MTCC 9447) (Figure 1).

Growth Kinetics of BMT4i in the presence of BaP

The growth kinetics experiment revealed that the BMT4i possess ability to utilize BaP for its biomass production. As shown in the plot of log₁₀ of CFU/ml against incubation time, after 12 h of lag phase, log₁₀ CFU/ml of BMT4i increases exponentially with increase in incubation duration up to 7^th day and there after it declines (Figure 2). At the beginning, 7.46 log₁₀ CFU/ml (~ 2 x 10⁷ CFU/ml) of BMT4i was added to the BaP-BSM medium, which almost remain constant (7.5 log₁₀ CFU/ml) for 12 h, started increasing linearly after 24 h (8.4 log₁₀ CFU/ml) attaining maximum 36.77 log₁₀ CFU/ml (6.0 x 10³⁶) on 7^th day of incubation showing approx 4x10²⁹-fold increase in the cell number. The CFU/ml declined slowly after 7^th day reaching to zero on 42 day. About 4x10²⁹ fold increase in the CFU number is directly correlated with the ability of Bacillus subtilis BMT4i to utilize BaP as the sole source of carbon and energy which leads to high increase in cell number within just 7 days, which starts declining afterwards possibly due to the exhaustion of BaP.

Assessment of BaP degradation

The HPLC profile for BaP and its metabolites after 7 days of growth of BMT4i in BaP medium was compared with that of negative control (without BMT4i) (Figure 3 A and B ). The chromatogram showed six additional peaks (I, II, III, IV, V, VI) indicating different metabolites formed during the degradation of BaP. The analysis of metabolites is under study. The plot of percent BaP degradation against incubation time (Figure 4), demonstrated that Bacillus subtilis BMT4i possess ability to degrade BaP as shown by the linear increase in BaP degradation with time. BMT4i started degrading BaP after 24 h and continued up to day 28. On 12 h, no detectable amount of degradation was seen suggesting it as lag phase of degradation. On day 1, BMT4i mediated BaP degradation efficiency was about 5.18% that increased exponentially up to 7 day (about 48.34%), and there after with slow increase it became static on day 28 (84.66 %). Further incubation of 35 days and 42 days doesn't show any further increase in BaP degradation. Whereas, on day 2, 3, 14 and 21, BMT4i was able to degrade about 12.28%, 21.77%, 60.12% and 73.92% BaP respectively. Although, the number of viable cells (log₁₀ CFU/ml) decreased considerably after 7 day of growth in BaP medium, the BMT4i continued to degrade BaP up to 28 days.

Viability of BMT4i in the presence of other PAH

Bacillus subtilis BMT4i possess the ability to utilize naphthalene, anthracene and DBT as the sole source of carbon and energy as indicated by the appearance of numerous colonies after 48 h of growth over the respective PAH containing plates. This was further confirmed by CFU/ml after 7 days of growth in respective PAH containing broth. The CFU/ml was found to be about 10⁵² (naphthalene), 10⁴⁹ (anthracene) and 10⁵⁶ (DBT).

Discussion

Present study is the first report demonstrating the utilization of BaP as a sole source of carbon and energy by bacteria. The novel strain Bacillus subtilis BMT4i (MTCC 9447) showed 10²⁹ fold enhancement in biomass with in 7 days and about 84.66% of BaP degradation after 28 days of growth. The HPLC profile of 7 days incubation showed six additional peaks indicating intermediate metabolites. The identification of metabolites is under study. At present it is not clear whether the decrease in CFU/ml after 7 days is due to the accumulation of toxic metabolites or exhaustion of BaP as carbon and energy source. Our study is different from other studies in following three aspects. First, all the reported BaP degradation by bacteria have been shown to occur co-metabolically i.e., in the presence of additional carbon sources. Second, none of the bacterial species showed viability for such a long duration (40 days) in BaP-BSM medium. Third, this much of high BaP degradation efficiency has not been reported by earlier studies. Early observation of BaP biodegradation was made with mutant Beijerinckia sp. strain B8/36 and Pseudomonas sp. strain NCIB 9816 grown on succinate plus biphenyl and succinate plus salicylate (1, 7). Mycobacteriumvanbaalenii PYR-1 using peptone, yeast extracts, and soluble starch as the additional carbon sources was able to degrade 24.7 % of BaP in pure culture where as in sediment water microcosm experiment it was able to mineralize 36 % of added BaP after 28 days (10, 11). In another study, Mycobacterium sp. Strain RJGII-135 showed 25 % co-metabolic mineralization of BaP in soil after 180 days (8). In a different study, Mycobacterium sp. strain RJGII-135 demonstrated about 40% degradation of BaP after 32 days (25). Co-metabolic degradation (41%) of BaP was also demonstrated by Burkholderia cepacia strains after 56 days (15). Some of the other studies involved use of bacterial consortium derived from soil which co-metabolically mineralizes BaP to greater than 95% in 150 days and 33-65% with in two weeks when provided with a complex hydrocarbon co substrate such as crude oil and diesel fuel separately in soil (17, 19). In a recent study, Bacillus subtilis-tgr3 isolated from PAH contaminated soil was able to transform 55% and 65% of BaP with in 48 h and 72 h at 30ºC when grown on minimal media supplemented with sodium citrate (13). However, during incubation, tgr-3 showed only 10² fold enhancement in cell number after 48 hours after that it declined drastically becoming non-viable with in 96 hours.

Bacillus subtilis BMT4i also possess ability to degrade other PAHs such as naphthalene, anthracene and dibenzothiophene. Since Bacillus subtilis BMT4i has been isolated from automobile contaminated soil and is well adapted to PAHs including BaP contaminated environment, therefore it could serve as better model for bioremediation of PAH contaminated site and removal of PAHs including BaP from the environment.

Acknowledgements

This work was supported in part by the Modern Institute of Technology, Rishikesh, Uttarakhand, India and Uttrakhand Council of Science and Technology, Uttarakhand, India (UCOST; grant no. UCS and T/R and D/LS-46/06-07), thatare gratefully acknowledged. We also thank Prof Aditya Shastri, Vice Chancellor, Banasthali University, Rajasthan, India for providing facilities in the Dept. of Bioscience and Biotechnology at this university.

Submitted: October 01, 2008; Returned to authors for corrections: November 04, 2008; Approved: May 15, 2009.

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Publication Dates

• Publication in this collection
  06 Oct 2009
• Date of issue
  Dec 2009

History

• Accepted
  15 May 2009
• Received
  01 Oct 2008