Open Access

Molecular Characterization of camphor utilizing bacterial isolates from refinery sludge and detection of target loci-Cytochrome P-450 cam mono oxygenase (cam C gene) by PCR and gene probe

SpringerPlus20132:170

DOI: 10.1186/2193-1801-2-170

Received: 7 February 2013

Accepted: 12 April 2013

Published: 17 April 2013

Abstract

This study presents the isolation and molecular characterization of bacterial strains utilizing 1, 7, 7-Trimethylbicyclo (2.2.1) heptane-2-one (camphor) as a sole source of carbon, isolated from the biomass sludge sample collected from an effluent treatment plant of Mathura Refinery Limited (MRL), India. Initial screening was carried out where the 16S rDNA PCR was performed using reported eubacterial primer set followed by Amplified Ribosomal DNA Restriction Analysis (ARDRA). About 47% of the isolates have shown unique ARDRA pattern based on which, 15 distinct isolates were selected and tested for the presence of cam C gene that was successfully demonstrated by PCR using gene specific primers. A Dot-Blot experiment was designed to detect the cam C loci in the plasmid DNA of all camphor isolates based on non-radioactive “Biotin-Streptavidin” detection system. The bacterial identity with respect to partial 16S rDNA gene sequences of all camphor isolates placed them in 9 major genera viz., Pseudomonas sp., Staphylococcus sp., Alcaligenes sp., Agromyces sp., Stenotrophomonas sp., Reichenowia sp., Achromobacter sp., Brevibacterium sp. and Pseudaminobacter sp. A detailed phylogentic tree was also constructed to establish their evolutionary status from the gene sequence data.

Keywords

Sludge sample Camphor 16S r DNA PCR ARDRA cam C gene PCR Dot-blot Phylogenetic analysis

Background

Poly aromatic hydrocarbons (PAHs) are imposing serious threats to human health and are constantly affecting the surrounding environment due to its highly recalcitrant nature that reduces its bioavailability to natural degradation and leads to its prolonged existence in the environment. This has forced researchers to look out for efficient bioremediation strategies to degrade these hazardous pollutants. Microbial biodegradation is an efficient and promising solution to such environmental restoration (Stapleton and Sayler 1998). The application of available advanced molecular biology tools have led to the designing of rapid and accurate strategies to monitor, discover and identify novel bacteria and their catabolic potentialities with respect to degradation of several environmental xenobiotics such as PAHs (Ahn et al. 1999; Goyal and Zylstra 1996; Hedlund et al. 1999; Zylstra et al. 1997). The unbound limits of microbial ecology demonstrate that, different bacteria exist in same ecosystem having similar catabolic options for survival. The survival of bacteria using PAH as substrate has always remained a challenging area of research. With an increase in information of diverse genes that encode enzymes for PAH catabolism (Mueller et al. 1997; Saito et al. 1999), the next step is to understand the functions of these genes and also to determine their ecological significance in context of environmental pollution. Hence in-depth knowledge of PAH-catabolic genes from diverse groups of bacteria will provide valuable information pertaining to fundamentals of bacterial catabolic mechanisms and will aid in designing efficient bioremediation strategies (Shimada 2006). However there is a trial calculation stating, only 1% of bacteria that actually exist on earth have been isolated (Rodon et al. 1999). Therefore, a molecular approach with PCR and gene probes targeting important catabolic genes would be very useful for further detection and characterization of cultivable as well as uncultivable microbial degraders (Hamann et al. 1999; Meyer et al. 1999).

In our present study we have used sludge sample collected from the sewage outlets of the Mathura Refinery Limited (MRL). This refinery located at Mathura, was commissioned in the year 1982 as India’s sixth oil refinery. Refineries commonly face issues of environmental safety and concerns and have to strictly abide by the environmental protection regulations set by the Governmental agencies. However the various complex stages of refinery procedures are associated with inevitable elimination of large amount of chemicals especially the PAHs that pollute the surrounding. Earlier studies have reported presence of PAHs in refinery soils. Masih and Taneja (2006) have estimated the average concentration of PAHs in the soil samples collected from sites adjacent to Mathura Refinery ranging from 3.1 to 28.5 μg/g of soil. Yet another study revealed Fluoranthene, Chrysene and benzo fluoranthene as most abundant PAHs of this site (Rawat and Sharma 2008). The presence of heterotrophic microorganisms in soil act as significant biological factors, that allows these chemicals to be utilized as a carbon source. In other words the microbial flora is highly influenced by the type of pollutant persisting in the contaminated site. This in turn results in enhanced degradation capabilities by means of activated expression of key genes associated with catabolic enzymes as a vital step towards adaptation and enrichment of such microbial degraders. In this study we have targeted one such significant gene, the “Cytochrome P-450 cam mono oxygenase loci” also known as cam C gene with respect to the chosen substrate i.e., Camphor, that was used for enrichment of microbes present in the collected sludge sample. Earlier report by (Chakrabarty 1976), clearly states that the various genes coding for Cytochrome P-450 cam and many other enzymes of the camphor degradative pathway reside in a 230 kbp CAM plasmid operon which constitutes the camC gene (M12546.1) loci. The complete nucleotide sequence of the cam C gene in Pseudomonas putida as reported by Unger et al. (1986) was successfully cloned and also expressed in Escherichia coli. The Cytochrome dependent mono oxygenases are known for their broad substrate specificity and play a pivotal role in catabolizing a series of PAHs, especially the low molecular weight PAHs like phenanthrene, naphthalene, anthracene, salicylate, catechol etc., which are known for years to be good substrates for bacteria (Harford-Cross et al. 2000; Kim et al. 2004). Since camphor is the natural substrate to this ubiquitous enzyme- Cytochrome P-450 cam mono oxygenase (Susanna et al. 2000), hence we used camphor as a sole source of carbon to isolate and characterize bacteria from the PAH contaminated sludge sample collected from the MRL sewage outlets.

Results

Selection of diverse camphor degrading bacteria based on 16S r DNA PCR and ARDRA

This is a preliminary report on a diverse group of bacteria isolated from the MRL sludge that were fed with camphor as a sole source of carbon. The cultures were enriched twice with 100 ppm of camphor in the minimal media to selectively isolate strains efficiently using camphor as a substrate. Initially about 32 distinct bacterial colonies were selected based on their basic morphological features such as shape, size and color. The PCR amplification of 16S r DNA gene was done using the Universal Eubacterial primer set 27 F and 1492 R. All bacterial isolates have shown successful amplification of 1450 bp PCR amplicon of 16S r DNA gene (Figure 1, lanes a-c). As a follow-up step, 16S r DNA PCR amplicons were subjected to ARDRA using restriction enzyme Hae III. Digestion analysis revealed that, out of 32 test isolates, about 15 isolates were showing discrete fragmentation pattern accounting to 47% of the total camphor utilizing HPC strains isolated in this study. The unique ARDRA patterns for the final 15 camphor isolates are shown in Figure 2.
Figure 1

(a-c) 16S rDNA gene PCR in camphor isolates. Lanes: a- DNA ladder; b –positive control; c- camphor isolate. (d-f)camC gene PCR in camphor isolates. Lanes: d- DNA ladder; e- positive control; f- camphor isolate. (g-i)Eco RV Restriction digestion pattern of the cam C gene PCR amplicon. Lanes: g- DNA ladder; h & i- restriction digestion patterns of the cam C gene of positive control and camphor isolate showing two bands corresponding to 306 and 210 base pairs respectively. (j) Lane shows 1 kb DNA ladder from Gibco-BRL with detailed MW specifications. Note: Gel picture is divided in three segments, showing results of positive control and one test isolate only (representing remaining camphor isolates that are not included in the gel image).

Figure 2

ARDRA: Unique band pattern for the 15 camphor-utilizing bacteria obtained by restriction digestion of 16S r DNA PCR products of each isolate withHaeIII restriction enzyme. Lanes: a &j- 1.0 kb DNA ladder (Gibco-BRL); lanes b-i and k-q shows the unique digestion pattern of the 16S ribosomal DNA with respect to the different camphor isolate.

PCR amplification of target cam C gene and its detection in camphor isolates using gene specific probe

The colony PCR was carried out for all the 15 isolates targeting the cam C gene. The primers were designed with reference to the conserved regions of cam C gene of Pseudomonas putida (Unger et al., 1986, AC# M12546) as shown in Figure 3. Hence, P. putida standard strain was taken as a positive control in PCR reaction. All strains showed successful amplification of the gene with expected size of 516 base pairs (Figure 1, lanes d-f). The authenticity of the amplified cam C PCR product was further confirmed by restriction digestion analysis using Eco RV with reference to the restriction map of the cam C gene of P. putida. The restriction pattern of the cam C gene product from the isolates was compared to that of the positive control as shown in Figure 1 (lanes g-i).
Figure 3

Pseudomonas putida- camC gene, encoding Cytochrome P-450-cam, complete cds. AC#M12546. Unger et al. (1986). Gene sequence amplified by PCR (516 bp) has been highlighted. Primer sequences are underlined.

In this study we further did the DNA dot-blot experiment for all camphor isolates (Figure 4) by spotting their Plasmid DNA along with the positive control onto the N-Bond Nylon membrane using the Dot-Blot apparatus. The cam C PCR product of the positive control was used for generating the biotinylated probe that was conjugated to SA-AP during the blotting steps. The detection of probe, bound to the target site was successfully demonstrated, based on the chemiluminescence reaction between the Streptavidin linked alkaline phosphatase and the chemiluminescent substrate–Lumiphos, where the final detection signals were captured in a photographic film.
Figure 4

DNA dot-blot experiment: detection ofcamC gene in from the Plasmid DNA of camphor isolates. P – Plasmid DNA of positive control ; 1 to 15 shows positive signal with respect to the presence of cam C gene in Plasmid DNA of all 15 unique camphor utilizing HPC-isolates.

Identification of bacterial strains and their Phylogenetic relationships

In order to establish the identity of 15 camphor isolates, the 16S r DNA PCR products were cloned, sequenced and submitted to GenBank of the NCBI and were matched with the available sequences in database. The BLAST search results have placed the camphor isolates belonging to 9 major genera viz., Pseudomonas sp. (Isolates_HPC-319, HPC-326 and HPC-330), Staphylococcus sp. (Isolates_HPC-322, HPC-323 and HPC-324), Alcaligenes sp. (Isolates_HPC-328 and HPC-333), Stenotrophomonas sp. (Isolates_HPC-320 and HPC-329), Brevibacterium sp. (HPC-331), Reichenowia, sp. (HPC-332), Agromyces sp. (HPC-334), Achromobacter sp. (HPC-325) and Pseudaminobacter sp. (HPC-321). The GenBank Accession numbers for all 15 camphor utilizing HPC- strains along with their identity are mentioned in Table 1.
Table 1

Details of strain identity along with their accession numbers as submitted in NCBI GenBank for the 15 camphor utilizing HPC strains

Isolate

GenBank accession No.

Bacterial strain

HPC-319

AY897403

Pseudomonas putida strain

HPC-320

AY897404

Stenotrophomonas acidaminiphila

HPC-321

AY897405

Pseudaminobacter sp.

HPC-322

AY897406

Staphylococcus aureus strain

HPC-323

AY897407

Staphylococcus aureus strain

HPC-324

AY897408

Staphylococcus epidermis

HPC-325

AY897409

Achromobacter xylosoxidans

HPC-326

AY897410

Pseudomonas sp.

HPC-328

AY897412

Alcaligenes sp.

HPC-329

AY897413

Stenotrophomonas sp.

HPC-330

AY897414

Pseudomonas sp.

HPC-331

AY897415

Brevibacterium sp.

HPC-332

AY897416

Reichenowia sp.

HPC-333

AY897417

Alcaligenes sp.

HPC-334

AY897418

Agromyces sp.

As a conclusive step to our study, the phylogenetic inference was drawn. A dendrogram was generated based on the partial 16S r DNA nucleotide sequences of all test isolates. The sequence alignment was done using CLUSTAL-MUSCLE program clubbed with the latest 5th version of software-MEGA for generation of tree, as shown in Figure 5. We have used the Neighbor joining Algorithm (NJ) method. All positions containing gaps and missing data were eliminated from the data set by complete deletion option. The percentage of replication trees in which the taxa clustered together in bootstrap test (500 replicates) is shown next to branch point.
Figure 5

Phylogenetic tree for the 15 camphor utilizing HPC-Strains based on their partial 16S r DNA gene sequences. Dendrogram generated using CLUSTAL-MUSCLE for sequence analysis and MEGA-5 for tree construction using Neighbor Joining methods. Boot strap values for clustered taxa are mentioned at the tree branch points (500 replicates taken).

Discussion

Our lab has previously reported on isolation of bacteria from environmental niches degrading phenolics (Kutty et al. 2000, 2001; Narde et al. 2004; Qureshi et al. 2001, Qureshi and Purohit 2002). Refinery sludge is a challenging waste, highly polluted with PAHs. The present study focuses on diverse bacterial population surviving in such environments, capable of utilizing these hazardous chemicals as carbon source. Hence, the target is looking for specific catabolic genes present in these microbes, that can be applied in near future for designing intrinsic bioremediation strategies of the polluted sites.

Cytochrome P450 monooxygenases (CYPs or P450s) are from ubiquitous protein family existing in all eukaryotes, and in most of the prokaryotes and Archae. These heme containing enzymes are versatile biocatalysts, involving monooxygenation of large variety of substrates and therefore the discovery of new P450s with novel activities from diverse organisms is being focused for potential biotechnological applications. In a recent review, Urlacher and Girhard (2012) have presented an overview on recent advancements with respect to P450 engineering for synthetic applications such as drug development, bioremediation and production of fine chemicals. In our study we have targeted the Cytochrome P450 cam monooxygenase gene (cam C) in the isolated strains.

The widely accepted PCR based 16S rDNA gene analysis (Weisburg et al. 1991), was used for bacterial identification and Phylogenetic studies, since it is highly conserved on evolutionary scale, yet diverse enough to identify and classify Eubacteria (Purohit et al. 2003). The 16S rDNA gene PCR products were subjected to ARDRA technique as reported by Gurtler et al. (1991). This has been proved to be a powerful tool to identify different polymorphic groups among the amplicons that in turn reflects the differences within the sequence of the 16S r RNA gene and therefore allows the inference on the phylogenetic relationships among taxonomically, relatively close and distant organisms reflecting Eubacterial diversity (Ludwig et al. 1998). In addition, novel or rare microorganisms could also be identified on the basis of unique sequences and digestion patterns. Based on this principle, ARDRA has also been used as a diagnostic tool (Backermans and Madsen 2002).

All the diverse isolates selected by 16S rDNA and ARDRA analysis were further screened for the presence of target gene of our interest i.e., cam C gene, that was successfully amplified in all the test isolates. Based on the the restriction map of reference gene, Eco RV was chosen for restriction analysis as a step towards establishing sequence authenticity. Since, it has a single restriction site at position 306 bps, thereby cleaves the gene product into two fragments corresponding to molecular sizes of 306 bps and 210 bps respectively. An exact match of the digested pattern of cam C gene amplicon of all test isolates with respect to that of the positive control was established, which confirmed the correctness in cam C gene sequence of the studied isolates.

The detection of target loci cam C using gene probe was based on the popular nonradioactive, chemiluminescent and extremely sensitive approach of the Biotin-Streptavidin system (Diamandis and Christopoulos 1991). Our Dot-Blot experiment has successfully demonstrated the positive binding of cam C gene probe to the spotted plasmid DNA from all 15 camphor isolates along with the positive control, which suggests the localization of cam C gene to the plasmid DNA. This result is in consistence with the earlier report by Shaham et al. (1973) who clearly described about the camphor utilizing strains of P. putida carrying the genetic information required for camphor degradation on a plasmid.

The sequencing of the 16S r DNA from the isolates revealed that, most of the bacterial strains were members of the Proteobacteria (α-, β-, γ- Proteobacteria) class. Among the 15 strains isolated from the sludge sample the predominant group was γ- Proteobacteria (Pseudomonas sp., Stenotrophomonas sp.). Isolates belonging to α- Proteobacteria (Reichenowia sp., Pseudaminobacter sp.) were also present. Representatives of β-Proteobacteria (Alkaligenes sp., Achromobacter xylosoxidans) were also found beside members of classes Actinobacteria (Agromyces sp., Brevibacterium sp.) and Fermicutus (Staphylococcus aureus strain and Staphylococcus epidermis). Interestingly we have isolated three strains belonging to the genera of Staphylococcus sp. These strains are generally related to skin and respiratory infections in human and are rarely associated with PAH degradation. However there have been a few relevant reports before. Survery et al. (2004) have reported strains of Staphylococcus sp. isolated from soil near to petrol pumps in Karachi city, Pakistan, that were able to degrade base oil. Yet another interesting report by Mallick et al. (2007) states about a Staphylococcus sp. strain PN/Y capable of degrading Phenanthrene as a sole source of carbon. This strain was isolated from the petroleum contaminated soil of Noonmati Refinery site, India and was found to carry a mega plasmid-p PHN, approximately of 112 kb size, that was responsible for the degradation of Phenanthrene by a novel assimilation pathway. Kafilzadeh et al. (2011) have also reported bacterial strains belonging to Staphylococcus sp. isolated from contaminated soils of Iran, which were able to degrade naphthalene. So far, plasmid mediated biodegradation of PAHs have been widely reported in both Gram positive and Gram negative bacteria, but very little is known about the hydrocarbon degradation capability by genus Staphylococcus sp. The acquisition of catabolic ability mediated through plasmids in such unusual bacterial hosts has been attributed to two possible mechanisms of horizontal gene transfer and recombination by transpositions that are closely linked (Obayori and Salam 2010) and thus plays a vital role in acclimatization of bacterial communities to various pollutants. Thus in our study, we predict that horizontal transfer of cam C gene may have occurred in Staphylococcus sp. strains from the surrounding bacterial population resulting in camphor uptake and its utilization.

Earlier report by Kumar and Khanna (2010), who determined the bacterial community structure of a coal-tar contaminated soil by establishing a clone library of 16S r RNA genes, had clearly stated that most of the hydrocarbon polluted sites are inhabited with Proteobacteria consortia which majorly constitute the Gammaproteobacteria and Actinobacteria. Our findings confirm this report.

Conclusions

Biodegradation of organic chemical pollutants is one of the many important processes affected in field sites by microorganisms which use them as a source of carbon and energy. The predominance and persistence of a particular type of pollutant also shifts the microbial communities towards those organisms which can utilize these contaminants and survive. Hence they also act as an indicator species to monitor specific pollutants on site. Thus in this study we have attempted to isolate a diverse group of bacterial strains belonging to various genera from a PAH contaminated sludge sample collected from a refinery site using camphor as a carbon source and tried to characterize them at a phylogenetic level in order to check their diversity. The localization of target loci, Cytochrome P-450 camphor mono oxygenase gene in host plasmid was successfully demonstrated by PCR and gene probe methods. Microbial communities are promising source for diverse catabolic potentialities which should be harnessed by human to generate novel bioremediation strategies to clean up this heavily polluted environment.

Methods

Chemicals

All the growth media components were purchased from Sigma Chemical Co. (St. Louis, USA). Taq DNA polymerase (Bangalore Genei-Merck), Agarose (USB) and 1 kb DNA ladder (Gibco-BRL) were used. Restriction enzymes (Hae III and Eco RV), N-Bond nylon membrane for Dot-Blot were procured from Amersham-GE Healthcare. Components for Hybridization buffer and blocking solution were procured from Sigma Chemical Co. (St. Louis, USA). BioPrime DNA Labelling System for probe generation and TA-Cloning Kit were from Invitrogen. Lumiphos (Chemiluminescent dye) was procured from Thermo Scientific.

Growth media

The media employed in the bio-reactor was 0.1X M9 Media, containing (per liter) 20 ml of 5X Salts (Na2HPO4 - 64 g l-1, KH2PO4 -150 g l-1, NaCl - 2.0 g l-1), 200 μl of 1 M MgSO4 and 4 ml of 1 M Cacl2. The inoculum from the reactor sample was enriched in New Mineral Media (NMM) containing (per liter) 1 ml of 10%CaCl2, 2 ml of 10% MgSO4, 2.5 ml of 10% NH4Cl, 40 ml of 50 mM Phosphate buffer (Na2HPO4- 131 g l-1 and KH2PO4-67.5 g l-1).

Enrichment and culturing steps

The MRL sludge was initially fed into bioreactor containing 0.1X M9 Media along with 250-ppm of crude oil as a substrate for about a month. One ml of treated sludge from the bioreactor was pelleted and washed twice with double distilled water. This pellet was then inoculated in NMM containing 100 ppm camphor, as the sole carbon source. The culture flask was enriched after five days by transferring the pellet into fresh NMM media along with camphor. Enrichment was done twice and was followed by serial dilution and spread plating on NMM plates containing camphor in order to isolate bacteria selectively utilizing camphor for their growth. The concentration of camphor in all enrichment steps was constantly maintained at 100 ppm.

Template preparation for PCR amplification

Morphologically distinct bacterial colonies from the NMM plates were chosen for further molecular studies. They were picked up carefully on the tip of a sterile platinum inoculating needle and were inoculated in PCR tube containing 10 μl of PCR grade water. The cells were lysed by heating to 95°C for 5 minutes in PTC-200 thermal cycler (MJ Research) as described earlier by Park et al. (2002). About 5 μl of the denatured cells were taken for the PCR amplification of desired gene.

PCR Amplification of 16S r DNA & Amplified Ribosomal DNA Restriction Analysis (ARDRA)

The PCR amplification of 16S rDNA gene for all the morphologically distinct camphor isolates was carried out as done earlier (Bhuvaneswari et al., 2005), using the eubacterial primer set- 27 F(5-AGAGTTTGATCMTGGCTCAG-3) and 1492 R (5-TACGGYTACCTTGTTACGACTT-3) as reported by Backermans and Madsen (2002). 5 μl of denatured cells of different isolates were used as a template in the PCR. The forward and reverse primers were used at a concentration of 50 pmol and the annealing temperature was set at 55°C. The resulting 16S rDNA PCR amplicons were confirmed by analyzing PCR them on 1.2% agarose gels containing 0.5 μg/ml of ethidium bromide in 1X TAE running buffer. The PCR products were concentrated by ethanol precipitation and were subjected to ARDRA using the restriction enzyme Hae III as per manufacturer’s protocol. The restriction band patterns were viewed in 1.8% agarose gel stained with ethidium bromide. Isolates with entirely discrete restriction pattern were chosen for further studies targeting the cam C gene.

PCR amplification of cam C gene

PCR amplification for cam C gene was performed in a total volume of 50 μl. The reaction mixtures contained 2 μl of 10X-reaction buffer, 1.2 μl of 25 mM Mgcl2, 2 μl of 2 mM d NTPs, 0. 5 μl of each primer viz., FP 5-CGT GAG GCC TAT GAA GAT TAC CG-3 and RP 5-GCC ACA CAT CCT CTT GGC TTC G-3 (GENBANK AC# M12546), 2U of Taq DNA Polymerase. About 5 μl of the denatured cells were used as template in the PCR. A cycling regime with initial denaturation at 94°C for 5 min (1 cycle), followed by 94°C for 1 min, 65°C for 1.5 min, 72°C for 2 min (35 cycles) and final extension at 72°C for 7 min (1 cycle) was employed. The successful amplification of cam C gene was confirmed by analyzing PCR products on 1.2% agarose gels as described above.

Restriction analysis of cam C gene PCR amplicons

The cam C gene amplicons were concentrated using ethanol precipitation before carrying out restriction digestion. In ethanol precipitation the cam C PCR product were mixed gently with one-tenth volume of 3 m M sodium acetate (pH-5.2) and 2.5 volumes of absolute ethanol. This mix was incubated at minus 80°C for an hour and then centrifuged at 14,000 rpm for half an hour. The pellets obtained were dissolved in PCR grade water and were digested with 15U of Eco RV. The restriction digestion was carried out for 3 h at 37°C and the fragmentation pattern was viewed in 2% agarose gel stained with ethidium bromide.

DNA Dot-blot

All the 15 isolates were recultured in NMM broth containing 100 ppm of camphor and were used for Plasmid DNA extraction using the conventional method (Sambrook et al. 1989). The Plasmid DNA of 15 camphor isolates along with one positive control was spotted onto the N-Bond nylon membrane using the Dot-Blot apparatus. The DNA spots on the membrane were denatured with 0.5 N NaOH and 1 M Tris for 5–6 min, one after the other. The membrane was then exposed for UV cross-link for 3 min followed by Pre-hybridization at 65°C for 1 hr. Hybridization was done at 60°C for 18 hrs after the addition of 50 ng of biotinylated cam C probe that was made using the BioPrime DNA Labelling System following the kit protocol. Blot washing steps included preliminary wash with 5X SSC and 0.5% SDS at 65°C followed by wash with 0.1X SSC and 1% SDS at 50°C. Brief washes with 2X SSC and TBS-Tween20 were done at room temperature. Blocking of the membrane was done with prewarmed (65°C) blocking solution (3 gm BSA/100 ml of TBS-Tween20) for 1 hr. The membrane was treated with 2000 fold diluted SA-AP (Streptavidin alkaline phosphatase) in TBS-tween 20 for 10 min at room temperature. Finally the membrane was washed for an hour at room temperature with final wash buffer composed of 100 mM Tris (pH-9.5), 100 mM NaCl and 50 mM of magnesium chloride. For chemiluminescent detection process, the dye namely 2-amino-2-methyl-1 propanol or Lumiphos was used at a concentration of 10 μl / square cm. The photographic film was developed after 15 min of exposure.

Cloning and sequencing of 16S rDNA PCR amplicons of camphor isolates

The 16S-rDNA PCR product of 15 distinct camphor-utilizing bacteria was ligated into pCR 2.1-TOPO (TOPO TA-Cloning Kit; Invitrogen), following the manufacturer’s recommended protocol. Selection of clones was based on the conventional blue white screening using IPTG and X-Gal. The plasmids from all positive clones were extracted according to the standard protocol (Sambrook et al. 1989) and checked for the presence of right insert by viewing them in 1% Agarose gel. The positive recombinant plasmids carrying the 16S r DNA insert were column purified and sequenced.

Phylogenetic analysis of the camphor isolates based on partial 16 S rDNA sequences

The partial 16S rDNA gene sequences for all the 15 camphor isolates were analyzed by matching them with the available sequence data in the NCBI database using BLAST and were later submitted in GenBank. The 16S rDNA nucleotide sequences of the 15 isolates were aligned using the CLUSTAL MUSCLE program as described earlier by Edgar 2004, and was used to generate the phylogenetic tree based on Molecular evolutionary genetic analysis (MEGA-5) software using the Neighbor joining method (Tamura et al. 2011).

Declarations

Acknowledgements

I am deeply indebted to Dr. H.J. Purohit, Chief Scientist and Head, EGU, NEERI, Dr. P. Padmanabhan, New Medical School, Singapore and Dr. Atya Kapley, Principal Scientist, EGU, NEERI, for their valuable guidance and prime support in carrying out this brief study. I also thank my fellow colleague Wazid Hassan, SRF, Seribiotech research laboratory, Bangalore, for helping me with Phylogenetic tree construction. My sincere thanks to Department of Science and Technology (DST), Government of India, for funding and supporting this work. I also thank the Director, NEERI, for providing me an opportunity to carry out this research work in their esteemed Environmental Genomics Unit of NEERI, Nagpur.

Authors’ Affiliations

(1)
Environmental Genomics Unit, National Environmental Engineering Research Institute, Nehru Marg
(2)
Seribiotech Research Laboratory, Carmelaram Post

References

  1. Ahn Y, Sanseverino J, Sayler GS: Analyses of polycyclic aromatic hydrocarbon-degrading bacteria isolated from contaminated soils. Biodegradation 1999, 10: 149-157. 10.1023/A:1008369905161View ArticleGoogle Scholar
  2. Backermans C, Madsen EL: Diversity of 16S r DNA and naphthalene dioxygenase genes from coal-Tar-waste-contaminated aquifer waters. Microb Ecol 2002, 44(2):95-106.Google Scholar
  3. Bhuvaneswari G, Padmanabhan P, Kapley A, Purohit HJ: Study on Staphylococcus aureus strain HPC-250 for associated antibacterial property. Curr Microbiol 2005, 51: 287-291. 10.1007/s00284-005-4471-3View ArticleGoogle Scholar
  4. Chakrabarty AM: Plasmids in Pseudomonas . Ann Rev Genet 1976, 10: 7-30. 10.1146/annurev.ge.10.120176.000255View ArticleGoogle Scholar
  5. Diamandis EP, Christopoulos RK: The biotin-(strept) avidin system: principles and applications in biotechnology. Clin Chem 1991, 37: 625-637.Google Scholar
  6. Edgar RC: MUSCLE: multiple sequence alignment with high accuracy and high throughput. Nucl Acid Res 2004, 32(5):1792-1797. 10.1093/nar/gkh340View ArticleGoogle Scholar
  7. Goyal AK, Zylstra GJ: Molecular cloning of novel genes for polycyclic aromatic hydrocarbon degradation from Comamonas testosteroni GZ39. Appl Environ Microbiol 1996, 62: 230-236.Google Scholar
  8. Gurtler V, Wilson VA, Mayall BC: Classification of medically important Clostridia using restriction endonuclease site differences of PCR-amplified 16S rDNA. J Gen Microbiol 1991, 137: 2673-2679. 10.1099/00221287-137-11-2673View ArticleGoogle Scholar
  9. Hamann C, Hagemann J, Hilderbrandt A: Detection of polycyclic aromatic hydrocarbon degradation genes in different soil bacteria by polymerase chain reaction and DNA hybridization. FEMS Microbiol Lett 1999, 173: 255-263. 10.1111/j.1574-6968.1999.tb13510.xView ArticleGoogle Scholar
  10. Harford-Cross CF, Carmichael AB, Allan FK, England PA, Rouch DA: Protein engineering of cytochrome P450-cam (CYP101) for the oxidation of polycyclic aromatic hydrocarbons. Protein Eng 2000, 13: 121-128. 10.1093/protein/13.2.121View ArticleGoogle Scholar
  11. Hedlund BP, Geiselbrecht AD, Bair TJ, Staley JT: Polycyclic aromatic hydrocarbon degradation by a new marine bacterium, Neptunomonas naphthovorans gen. nov. sp. nov. Appl Environ Microbiol 1999, 65: 251-259.Google Scholar
  12. Kafilzadeh F, Rafiee S, Tahery Y: Evaluation of Bioremediation of naphthalene using native bacteria isolated from oil contaminated soils in Iran. Ann Biol Res 2011, 2(6):610-616.Google Scholar
  13. Kim YD, Todoroki H, Oyama T, Isse T, Matsumoto A: Identification of cytochrome P450 isoforms involved in l-hydroxylation of pyrene. Environ Res 2004, 94: 262-266. 10.1016/S0013-9351(03)00134-8View ArticleGoogle Scholar
  14. Kumar M, Khanna S: Diversity of 16S r RNA and dioxygenase genes detected in coal-tar contaminated site undergoing active bioremediation. J Appl Microbiol 2010, 108: 1252-1262. 10.1111/j.1365-2672.2009.04523.xView ArticleGoogle Scholar
  15. Kutty R, Purohit HJ, Khanna P: Isolation and characterization of a Pseudomonas sp. strain PH1 utilizing meta-aminophenol. Can J Microbiol 2000, 46: 211-217.View ArticleGoogle Scholar
  16. Kutty R, Kapley A, Purohit HJ: Pseudomonas sp. Strain RM2: strain with diverse physiology for aniline and chlorophenol utilization. Asian J Microbiol Biotechnol Environ 2001, 3: 117-121.Google Scholar
  17. Ludwig W, Amann R, Martinez-Romero E, Schonhuber W, Bauer S, Neef A, Schleifer H: r RNA base identification and detection systems for Rhizobia and other bacteria. Plant Soil 1998, 204: 1-19. 10.1023/A:1004350708767View ArticleGoogle Scholar
  18. Mallick S, Chatterjee S, Dutta TK: A novel degradation pathway in the assimilation of phenanthrene by Staphylococcus sp. strain PN/Y via meta -cleavage of 2-hydroxy-1-naphthoic acid: formation of trans -2, 3-dioxo-5-(2hydroxyphenyl)-pent-4-enoic acid. Microbiology 2007, 153: 2104-2115. 10.1099/mic.0.2006/004218-0View ArticleGoogle Scholar
  19. Masih A, Taneja A: Polycyclic aromatic hydrocarbon (PAHs) concentration and related carcinogenic potential in soil at a semi arid region of India. Chemosphere 2006, 65: 449-456. 10.1016/j.chemosphere.2006.01.062View ArticleGoogle Scholar
  20. Meyer S, Moser R, Neef A, Stahl U, Kampfer P: Differential detection of key enzymes of polyaromatic hydrocarbon degrading bacteria using PCR and gene probes. Microbiology 1999, 145: 1731-1741. 10.1099/13500872-145-7-1731View ArticleGoogle Scholar
  21. Mueller JG, Devereux R, Santavy DL, Lantz SE, Willis SG, Pritchard PH: Phylogenetic and physiological comparisons of PAH-degrading bacteria from geographically diverse soils. Antonie Leeuwenhoek 1997, 71: 329-343. 10.1023/A:1000277008064View ArticleGoogle Scholar
  22. Narde G, Kapley A, Purohit HJ: Isolation and characterization of Citrobacter strain HPC255 for broad-range substrate specificity for chlorophenols. Curr Microbiol 2004, 48: 419-23.View ArticleGoogle Scholar
  23. Obayori OS, Salam LB: Degradation of polycyclic aromatic hydrocarbons: Role of plasmids. Sci Res Essays 2010, 5(25):4093-4106.Google Scholar
  24. Park W, Padmanabhan P, Padmanabhan S, Zylstra GJ, Madsen EL: nahR, encoding a LysR-type transcriptional regulator, is highly conserved among naphthalene-degrading bacteria isolated from a coal tar waste-contaminated site and in extracted community DNA. Microbiology 2002, 148: 2319-2329.View ArticleGoogle Scholar
  25. Purohit HJ, Raje DV, Kapley A, Padmanabhan P, Singh RN: Genomic tools in environmental impact assessment. Featured article in Environ Sci Technol 2003, 37(19):356A-363A. 10.1021/es032594mView ArticleGoogle Scholar
  26. Qureshi A, Purohit HJ: Isolation of bacterial consortium for degradation of p-nitrophenol from agricultural soil. Ann Appl Biol 2002, 140: 159-162. 10.1111/j.1744-7348.2002.tb00168.xView ArticleGoogle Scholar
  27. Qureshi A, Prabu SK, Purohit HJ: Isolation and characterization of Pseudomonas strain for utilization of 4-nitrophenol. Microbes Environ 2001, 16: 49-52. 10.1264/jsme2.2001.49View ArticleGoogle Scholar
  28. Rawat MK, Sharma M: Investigations on polycyclic aromatic hydrocarbons (PAHs) in waste oil at Mathura-Agra, National Highway No.2. J Indian Chem Soc 2008, 85: 539-554.Google Scholar
  29. Rodon MR, Goodman RM, Handelsman J: The earth’s bounty: assessing and assessing soil microbial diversity. Trends Biotechnol 1999, 17: 403-409. 10.1016/S0167-7799(99)01352-9View ArticleGoogle Scholar
  30. Saito A, Iwabuchi T, Harayama S: Characterization of genes for enzymes involved in the phenanthrene degradation in Nocardioides sp. KP7. Chemosphere 1999, 38: 1331-1337. 10.1016/S0045-6535(98)00534-7View ArticleGoogle Scholar
  31. Sambrook J, Fritsch EF, Maniatis T: Molecular cloning: a laboratory manual. 2nd edition. Cold Spring Harbor, N.Y.: Cold Spring Harbour Laboratory Press; 1989.Google Scholar
  32. Shaham M, Chakrabarty AM, Gunsalus IC: Camphor plasmid-mediated chromosomal transfer in Pseudomonas putida . J Bacteriol 1973, 116(2):944-949.Google Scholar
  33. Shimada T: Xenobiotic-metabolizing enzymes involved in activation and detoxification of carcinogenic polycyclic aromatic hydrocarbons. Drug Metabo Pharmacokinet 2006, 21: 257-276. 10.2133/dmpk.21.257View ArticleGoogle Scholar
  34. Stapleton RD, Sayler GS: Assessment of the microbiological potential for the natural attenuation of petroleum hydrocarbons in a shallow aquifer system. Microb Ecol 1998, 36: 349-361. 10.1007/s002489900121View ArticleGoogle Scholar
  35. Survery S, Ahmad S, Subhan SA, Ajaz M, Rasool SA: Hydrocarbon degrading bacteria from Pakistani soil: isolation, identification, screening and genetical studies. Pak J Biol Sci 2004, 7(9):1518-1522.View ArticleGoogle Scholar
  36. Susanna LK, Valere L, Rebecca WC: How do substrates enter and products exit the buried active site of cytochrome P450 cam? 1. Random expulsion molecular dynamics investigation of ligand access channels and mechanisms. J Mol Biol 2000, 303: 797-811.Google Scholar
  37. Tamura K, Peterson D, Peterson N, Stecher G, Nei M, Kumar S: MEGA5: molecular evolutionary genetics analysis using maximum likelihood, evolutionary distance, and maximum parsimony methods. Mol Biol Evol 2011, 28(10):2731-2739. 10.1093/molbev/msr121View ArticleGoogle Scholar
  38. Unger BP, Gunsalus C, Sligar SG: Nucleotide sequence of the Pseudomonas putida Cytochrome P-450 cam gene and its expression in Escherichia coli . J Biol Chem 1986, 261(3):1158-1163.Google Scholar
  39. Urlacher VB, Girhard M: Cytochrome P450 monooxygenases: an update on perspectives for synthetic application. Trends Biotechnol 2012, 30(1):26-36. 10.1016/j.tibtech.2011.06.012View ArticleGoogle Scholar
  40. Weisburg W, Barn S, Pelletier D, Lane D: 16S Ribosomal DNA amplification for phylogenetic study. J Bacteriol 1991, 173: 697-703.Google Scholar
  41. Zylstra GJ, Kim E, Goyal AK: Comparative molecular analysis of genes for polycyclic aromatic hydrocarbon degradation. Genet Eng 1997, 19: 257-269.View ArticleGoogle Scholar

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