FEMS Microbiology Letters 130 (1995) 75-80 Phylogenetic analysis of polycyclic aromatic hydrocarbon degrading mycobacteria by 16s rRNA sequencing Rong-Fu Wang, Wei-Wen Cao, Carl E. Cerniglia * Microbiology Dtrmision.National Centerfor To.uicologicalResearch.FDA, Jefferson,AR 72079-950,USA Received 24 January 1995;revised 8 May 1995;accepted8 May 1995 Abstract Mycobacterium sp. PYR-1 was previously isolated in our laboratory and was shown to be able to mineralize high molecular mass polycyclic aromatic hydrocarbons (PAHs) [Heitkamp and Cemiglia, (1988) Appl. Environ. Microbial. 54, 1612-16141. In this research, the 16s rRNA gene (rDNA) of this strain was amplified by polymerase chain reaction (PCR) and directly sequenced by cycle sequencing method. We compared this sequence with all known mycobacterial 16s rDNA sequences available from GenBank and found that Mycobacterium sp. PYR-1 16s rDNA differs from the other mycobacteria, especially in the region of nucleotides 168-200 (in the Escherichia co/i numbering system). Using the 16s rDNA sequences of the mycobacteria, a phylogenetic tree was constructed. The data from the phylogenetic tree and similarity values suggest that Mycobacterium sp. PYR-1 is closer to M. aurum and M. uaccue. Using the same approach, we also determined the 16s rDNA from an another PAH-degrading Mycobacterium sp. PAH135, isolated by Grosser and colleagues (1991) (Appl. Environ. Microbial. 57, 3462-3469). Mycobacterium sp. PAH135 was found to be closer to M. aichiense, and different from our MJ>cobacterium sp. PYR-1. Keywords: PAH-degrading mycobacteria; 16s rRNA; Polymerasechain reaction: Phylogeny 1. Introduction Bioremediation of polycyclic aromatic hydrocarbons (PAHs) contaminated environments has been considered as an attractive technology for restoration of polluted sites to an innocuous state. Generally, the biodegradation of low molecular mass PAHs such as naphthalene, phenanthrene and anthracene in pure culture or in environmental samples were reported to be performed by Pseudomonas strains [1,2]. Recently, strains from the genus Mycobacterium have * Corresponding author. Tel: + I (501) 543 7341: Fax: + I (501) 543 7307; e-mail: [email protected]. been shown to degrade the more recalcitrant and genotoxic higher molecular mass PAHs to polar metabolites and carbon dioxide [1,3-S]. Mycobacterium sp. PYR-1 was previously isolated in our laboratory from an oil-contaminated sediment and is efficient in the metabolism of high molecular mass PAHs, such as pyrene, fluoranthene and phenanthrene [5-81. This organism was identified as a rapidly-growing Mycobacterium sp. [5,6]. Confirmation that strain PYR-1 was a Mycobacterium sp. was determined by comparing its mycolic acid, cellular proteins, and nucleic acids with those of known species [91. The 16s ribosomal RNA sequences have proved useful in establishing phylogenetic relationships be- 037%1097/95/$09.50 6 1995 Federationof EuropeanMicrobiological Societies.All rights reserved SSDI 0378-1097(95)00186-7 76 R.-F. Wang et al. / FEMS Microbiology cause of their high information content, conservative nature, and universal distribution [lo,1 11. The 16s rRNA sequence analysis is a standard method for the investigation of their phylogenetic relationships [12]. Even though some closely related species may have only a few bases differences in their 16s rRNA gene sequences, a phylogenetic tree can be established to give them an exact taxonomic position [13]. Recently, more reports have been published for the identification of bacterial species and phylogenetic relationship analysis by the 16s rRNA sequencing [12-171. The taxonomic position of mycobacteria which degrade PAHs has not been described. Establishing the phylogenetic placement of Mycobacferium sp. PYR-1 could be helpful for further application of this organism, particularly if this strain is identified as a new species. In addition, determining the 16s rRNA sequence of Mycobacterium sp. PYR-1 can result in developing DNA probes or PCR methods to detect this organism from indigenous soil samples or inoculated soil samples when this organism is used as an inoculant in bioremediation of PAHs contaminated sediments. In this article, we report the amplification and sequencing of the 16s rRNA gene (rDNA) of Mycobacterium sp. PYR-1. Using this sequence data, a phylogenetic tree was constructed and its phylogenetic placement was established. 2. Materials and methods 2.1. Microorganism and culture conditions Mycobacterium sp. PYR-1 was originally isolated from oil-contaminated sediments [5,6]. Mycobacterium sp. PAH 135 was received from R.J. Grosser, University of Cincinnati, Cincinnati, OH. Axenic cultures of Mycobacterium sp. PYR-1 and Mycobacterium sp. PAH 135 were maintained on minimal basal salts medium (MBS) supplemented with pyrene and nutrients as described previously [5,6]. 2.2. Amplification of the 16s rRNA gene The amplification and sequencing primers were located at the highly conserved regions of the 16s Letters 130 (1995) 75-80 rRNA gene. The 5’-end amplification primer is GCTGGCGGCGTGCTTAACA, which is located at R036-R056 (E. coli numbering system, [IS]). For the Mycobacterium sp. PYR-1 amplification, the 3’-end amplification primers is AAGGAGGTGATCCARCCGCA, which is located at R1535-R1516. For the Mycobacterium sp. PAH135 amplification, the 3’-end primers is CGGCTACC’ITGTTACGACTC, which is located at R1509-R1489 (E. coli numbering system). Mycobacterial cells were collected from colonies or broth culture in MBS containing organic nutrients as described previously. The cells were washed twice with PBS (0.05 M NaH,PO,-Na,HPO,, 0.8% NaCl, pH 7.4) and once with autoclaved distilled water (dH,O), then resuspended in 0.1 ml dH,O. The cell suspensions (10 ~1) were diluted 1:lO using 90 ~1 of 1% Triton X-100, heated at 100°C for 5 min, immediately cooled in ice water, then subjected to the PCR amplification without isolation of the DNA. 2.3. Sequencing the PCR products by 35S-cycle sequencing method The DNA bands were visualized with a long wave UV lamp and excised from agarose gel. Glassmilk method (The Geneclean II kit, Bio 101 Inc., La Jolla, CA) was used to recover the DNA following the manufacturer’s instructions. Direct sequencing of the PCR products was conducted using the SequiTherm Cycle Sequencing Kit (Epicentre Technologies, Madison, WI) with 35S-dATP following the manufacturer’s instructions. 2.4. Phylogenetic analysis A computer program ‘ALIGN’ (Scientific and Educational Software, State Line, PA) was used for alignment and homology analysis of the rDNA sequences. Computer programs PHYLIP version 3.5~ were provided by Dr. Joe Felsenstein (University of Washington, Seattle, WA) and used for producing the phylogenetic tree. The sequences were also sent to Ribosomal Database Project (RDP) at the University of Illinois for phylogenetic analysis [19]. 2.5. Nucleotide sequence accession numbers The sequences of the 16s rRNA gene for Mycobacterium sp. PYR-1 and Mycobacterium sp. R.-F. Wang et al. / FEMS Microbiology PAH135 have been deposited in the EMBL GenBank data library with accession numbers X84977 and X84978, respectively. 3. Results and Discussion The 16s rRNA gene sequence of Mycobacterium sp. PYR-1 was determined. Phylogenetic analysis was conducted by comparing the 16s rDNA sequences for this species with other Mycobacterium species and some closely related High G + C Grampositive bacterial species available from GenBank. The sequences exhibited very high levels of similarity with other mycobacteria. For example, the similarity values for the 16s rRNA gene sequence of M.sp.PYRm1 M.sp.PAH135 M.aichiense M.asiaticum M.aurum M.avium M.bovis M.celatum M.chitae M.chlorophenoll M.chubuense M.cookii M.diernhoferi M.fallax M.farcinogenes M.flavescens M.fortuitum M.gadium cus M.gastr1 M.gWleVeUSe M.gilvum M.gordonae M.haemophilum M.interiection M.intermedium M.lntracellulare M.kansasii M.komossense M.lepraemurium M.malmoense M.marinum M.obuense M.paratuberculosis M.scrofulaceum M.simiae M.smeamatis M.sphagni M.szulgai M. terrae M.thermoresistibile........M.tuberculosis M.lllCfZrXE M.VaCCae Letters 130 11995) 75-80 77 Mycobacterium sp. PYR-1 is 99% with M. aurum, 98% with M. aaccae, 94-97% with other mycobac- terial species except for a few species in which incomplete 16s rDNA sequences available from GenBank were compared. These high similarity values confirmed that Mycobacterium sp. PYR-1 is a mycobacterial species. However, an alignment of this sequence with the 16s rRNA sequences of 41 other mycobacterial species available from the GenBank demonstrated that this species is different from all other known mycobacterial species tested, the most notable variation at the V2 region of 16s rRNA gene, positions 168-200, (in the E. coli numbering system, 18). Fig. 1 shows the alignment result of the variable region (V2) of 16s rDNA for 43 species of Mycobacterium. Mycobacterium sp. PYR-1 has a CCGAATAC-ACCCTTCTGGCTGCATGGTCTGGKTGGGGAAAGC--TTTT....... T-GAT.A.-G.C........mG.T.TG.T.......-.. ......... G-GAT.A./G.C..T.....mG.T.TG.T.......-.. ..... G...G-GA..-A.G..A.....-...CT.TG.T.......-.. ..m --GGA..A.GC.A.....-...GT.TG.T.......-....... .. ..... G...G-GA..-..AA.AC....-....TCTG.T.......-.. ..... G...G-GA.:A.G..A.....-....T.TG.TN......GC...A ... G...G-GA..A.~G..A.....-....T.TG.T.......-.. ......... T-GAT.A.~G.C..T.....-G.T.TG.T.......-... . ....... G-GA..-A.G."........~A.T.TG.T.......-... . ... G...G-GA..~A.G.CA......TG..-.TG.T.......-... . .G...--GGA..A.G.A..N...N....-.TG.T.......-..... ....... T-GA..-G.GCT..T.....GG.-.TG.T.......-.. ..m ... G...T-GAT.A.GC.C../......G.-.TG.T.......-.. ....G...--GGA..A.GC..........G.-.TA.T.......-. .. ......... T-T....NN...TC......C....TA.........-.. ........ T-GA../G.GCA..T.C....G./.TG.T.......-.. ... ..G...--GGA..A.GC.A.....~...GT.TG.T.......-.. ... ..G...G-GA..ACT....~....-.C..T.TG.T.......-.. ....G...T-GA..~A.G.AAC....-..T.T.TG.T.......-. ..... ....... G-GA..-G.AT...T...A..G.-.TG.T.......-..... G-GA.:A.A..ACA. -...CT.TG.T. :-___ G...G-GA...CAA.../.. CCT.T.TG.T. .--... G...G-GA...CGA...m.. :.C..T.TG.T. .--___ G...G-GA.:...C.GC.. CCTA..AG.T. _--... . . ..TTAG.T. r G...G-GA....TA...-.. _--... G...G-GA..ACT...:.. .-.C..T.TG.T. .--.__ . ..G...T-GA..A.-G.A..T. C..:.T.TG.T. .--.__ G..:-GGA....AA.GC.. . . ..T.TG.T. .T G-GA..CCGA.../.. .-.C..T.GG.T. _--_., .G...G-GA.:A.G..A.". -...CT.TG.T. _--... G...G-GA.:A.G.CA.T. TG..-.TG.T. _--... . ..G...G-GA..-..AA.AC....-....TCTG.T.......--....G...G-GA..ACT..../....-.C..T.TG.T.......--....... G...G-GA..ACT....-....-.C..T.TG.T.......-.. ........ G....TC......C....TA.........-..- ..... .. ..m ....... TG...A.G.:-..T.....GG./.TG.T.......-... . ... G...G-GA..CCGA.../....-.C..T.GG.T.......-.. ..m ... G...G-GA..A.-G..A......T...~.TG.T.......-... . .... .G..A.TC......C..A.TG.........--G . ..... G...GmGA..-A.G..A.....-....T.TG.T.......GC...A ... G...G-GA..-A.G..A.T.../...CT.TG.T.......-.. ..m ...... .................. T......GA.........-.. ..- ( ( ( ( i ( ( ( ( ( ( ( ( ( ( ( ( c ( c ( ( c c 1 1 t ( t ( ( ( ( ( ( ( ( ( ( ( ( ( ( 173) 171) 172) 172) 172) 1741 176) 161) 171) 172) 172) 173) 172) 170) 172) 174) 171) 173) 174) 174) 172) 172) 175) 1741 1751 163) 174) 174) 188) 1741 1681 172) 1741 173) 173) 1761 1711 1731 174) 175) 176) 168) 174) Fig. 1. Alignment result of one variable region (V2) of 16s rDNA for 43 species of Mycobacterium. The sequences of Mycobacterium sp. PYR-1 and Mycobacterium sp. PAH135 were determind by us. The other sequences were available from the GenBank. ” shows the same bases with the first line bases; ” shows lacking bases the letters showed different bases, K represents T or G. The base numbers shown on the right should be added 38 each to give the numbers in the E. co/i numbering system [18]. R.-F. W’ang ef ul. / FEMS MI< 78 different sequence in the V2 region from all other Mycobacterium species examined. A phylogenetic tree was constructed based on a comparison of the 16s rDNA sequences of mycobacteria from positions 39 to 1460 (E. coli numbering system) because of incompleteness of the 16s rDNA sequences of a number of the reference strains in the GenBank. The tree is shown in Fig. 2. Placement in the tree and similarity values both suggest that the Mycobacterium sp. PYR-1 is most similar to Mycobacterium aurum and Mycobacterium uaccae. The sequences were also sent to Ribosomal Database Project (RDP) at the University of Illinois for phylogenetic analysis. A large unrooted tree including many other common bacterial species was M. M. M. M. ulcerans marinum tuberculosis bovis M. paratuberculosis M. intracellulare M. gaslri M. kansasii M. malmoense M. haemophilum TM. smegmatis FM. aeneveuse M. flavescens A -M. terrae \ -M. komossense r M. aichiense f-M. diernhoferi M. thermoresistibile M. chlorophenolicus --M. sphagni M. obuense pl. vaccae Corynebacterium Fig. 2. Phylogenetic tree for the two mycobacterial species with other 41 mycobacterial species and 5 high G + C Gram-positive bacterial species. The tree is based on a comparison of 16s rDNA sequence on positions 38 to 1460 in the E. coli numbering system [18]. R.-F. Wang et al. / FEMS Microbiology produced by maximum likelihood method, which also indicated that the strain PYR-1 is in the genus Mycobacterium (data not shown). A small unrooted tree including only mycobacterial species was also generated by RDP with maximum likelihood method (data not shown). The phylogenetic position of Mycobacterium PYR-1 in these trees is identical to the results in the parsimony tree, i.e., Mycobacterium sp. PYR-1 is closest to M. aurum and M. rlaccae. Previously we found that the polypeptide pattern of Mycobacterium sp. PYR-1 most closely resembled that of M. austroufiicanum. However, restriction enzyme analysis and Southern blot hybridization revealed differences between the chromosomal DNA of our isolate and that of M. austroufiicanum [9]. We did not include M. austroafiicanum in the phylogenetic tree since to our knowledge the 16s rRNA sequence has not been published or available from GenBank. Grosser et al. [4] reported the isolation of a Mycobacterium sp. PAH135 which was also PAH degrading, rapid-growing Mycobacterium similar to Mycobacterium sp. PYR-1. Genetic differences between the two PAH-degrading mycobacteria were studied and reported in an abstract [20]. They reported that ‘the Mycobacterium sp. PAH135 (Grosser strain) is closest to that of M. fullax by 16s rDNA sequence comparison; The same approach on the PYR-1 (H-C strain) has yielded a sequence which verifies that organism as a Mycobacterium; Completion of this approach will allow construction of a phylogenetic tree...‘. However, sequence data for the 16s rRNA gene for either species was not presented in the abstract or any subsequent publication, and these sequences have not been deposited in GenBank. Therefore, we also determined the 16s rDNA sequence and did the phylogenetic analysis for Mycobacterium sp. PAH135. The similarity values for the 16s rRNA gene sequence of Mycobacterium sp. PAH135 is 99% with M. aichiense, 98% with 12 of other mycobacterial species, 97% with Mycobacterium sp. PYR-1. Placement in phylogenetic tree and similarity values for this species indicated that Mycobacterium sp. PAH135 is most similar to M. aichiense, and distinct from Mycobacterium sp. PYR-1. In conclusion, the 16s rDNA of Mycobacterium sp. PYR-1 and PAH135 were sequenced and the Letters 130 (1995) 75-80 79 phylogenetic placements for these two species were established. The sequences will be used to develop DNA probes or PCR primers to determine the genetic diversity of PAH degrading strains. The research results will also be helpful for further applications of these organisms as inoculants in bioremediation of PAH contaminated sediments. Acknowledgements This research was supported in part by appointments (for W.W.C.) to the Postgraduate Research Program at the National Center for Toxicological Research administered by the Oak Ridge Institute for Science and Education through an interagency agreement between the U.S. Department of Energy and the U.S. Food and Drug Administration. We thank Robert J. Grosser and David Warshawsky for kindly providing the Mycobacterium sp. PAH135. We appreciate Dr. Joe Felsenstein at University of Washington for providing the computer programs PHYLIP version 3.5~ and helping us use it for producing the phylogenetic tree. We also appreciate Mike McCaughey at RDP for the helping in constructing an alternative phylogenetic tree using our sequence data. References 111Cerniglia, C.E. (1993) Biodegradation of polycyclic aromatic hydrocarbons. Curr. Opin. Biotechnol. 4, 331-338. La Yang. Y., Chen, R.F. and Shiaris, M.P. (19941 Metabolism of naphthalene, fluorene and phenanthrene: preliminary characterization of a cloned gene cluster from Pseudomonas putida NCIB 9816. J. Bacterial. 176, 2158-2164. [31 Boldrin, B., Tiehm, A. and Fritzsche, C. (1993) Degradation of phenanthrene, fluorene, fluoranthene and pyrene by a Mycobacterium sp. Appl. Environ. Microbial. 59, 19271930. ]41 Grosser, R.J., Warshawsky. D. and Vestal, J.R. (1991) Indigenous and enhanced mineralization of pyrene, benzo [alpyrene and carbazole in soils. Appl. Environ. Microbial. 57, 3462-3469. [51 Heitkamp, M.A., Franklin, W. and Cerniglia, C.E. (1988) Microbial metabolism of polycyclic aromatic hydrocarbons: Isolation and characterization of a pyrene-degrading bacterium. Appl. Environ. Microbial. 54, 2549-55. 161Heitkamp, M.A. and Cerniglia, C.E. (1988) Mineralization of polycyclic aromatic hydrocarbons by a bacterium isolated from sediment below an oil field. Appl. Environ. Microbial. 54, 1612-1614. 80 R.-F. Wang Edal. / FEMS Microbiology [7] Heitkamp, M.A. and Cerniglia, C.E. (19891 Polycyclic aromatic hydrocarbon degradation by a Mycobacterium sp. in microcosms containing sediment and water from a pristine ecosystem. Appl. Environ. Microbial. 55, 1968-1973. [8] Kelley, I., Freeman, J.P., Evans. F.E. and Cerniglia, C.E. (19911 Identification of a carboxylic acid metabolite from the catabolism of fluoranthene by a Mycobacterium sp. Appl. Environ. Microbial. 57, 636-641. [9] Rafii, F., Butler, W.R. and Ccrniglia, C.E. (1992) Diffcrentiation of a rapidly growing, scotochromogenic, polycyclicaromatic-hydrocarbon metabolizing strain of Mycobncterium sp. from other known Mycobacrerium species. Arch Microbiol. 157, 512-520. [lo] Lane, D.J, Pace, B., Olsen, G.J., Stahl, D.A., Sogin, M.L. and Pace, N.R. (19851 Rapid determination of 16s ribosomal RNA sequences for phylogenetic analysis. Proc. Natl. Acad. Sci. USA 82, 6955-6959. [ll] Woese, CR. (19871 Bacterial evolution. Microbial. Rev. 51. 221-271. [12] Yamamoto, S. and Harayama, S. (1995) PCR amplification and direct sequencing of gyrB genes with universal primers and their application to the detection and taxonomic analysis of Pseudomonas putida strains. Appl. Environ, Microbial. 61, 1104-1109. [13] Collins, M.D., Wallbanks, S., Lane, D.J., Shah, J., Nietupski. R., Smida, J., Dorsch, M. and Stackebrandt, E. (1991) Phylogenetic analysis of the genus Listeria based on reverse transcriptase sequencing of 16s rRNA. Int. J. Syst. Bacterial. 41, 240-246. Letters 130 (19951 75-80 [14] Canard, B., Gamier, T., Lafay, B., Christen, R. and Cole, ST. (1992) Phylogenetic analysis of the pathogenic anaerobc Clostridium perfringens using the 16s rRNA nucleotide sequence. Int. J. Syst. Bacterial. 42, 312-314. [ 151 Duncan, A.J., Carman, R.J., Olsen, G.J. and Wilson, K.H. (1993) Assignment of the agent of Tyzzer’s disease to Clostridium pififorme comb. nav. on the bases of 16s rRNA sequence analysis. Int. J. Syst. Bacterial. 43, 314-318. [ 161 Lawson, P.A., Llop-Perez, P., Hutson, R.A., Hippe, H. and Collins, M.D. (1993) Towards a phylogeny of theclostridia based on 16s rRNA sequences. FEMS Microbial. Lett. 113, 87-92. [17] Van Kuppeveld, F.J.M., Van Der Logt, J.T.M., Angulo, A.F., Van Zoest, M.J., Quint, W.G.V., Niesters, H.G.M., Galama, J.M.D. and Melchers, W.J.D. (1992) Genus-and species-specific identification of Mycoplasmas by 16s rRNA amplification. Appl. Environ. Microbial. 58, 2606-2615. [18] Brosius, J., Palmer, J.L., Kennedy, J.P. and Noller, H.F. (1978) Complete nucleotide sequence of a 16s ribosomal RNA gene from Escherichia coli. Proc. Natl. Acad. Sci. USA 75, 4801-4805. [19] Larson, N., Olsen, G.J., Maidak, B.L., McCaughey, M.J., Overbeek, R., Macke, T.J., Marsh, T.L. and Woese, CR. (1993) The ribosomal database project. Nucleic Acids Res. 21 (SuppI.), 3021-3023. [20] Govindaswami, M., Feldhake, D.J. and Loper, J.C. (1994) Genetic differences between two polycyclic aromatic hydrocarbon (PAH) -degrading soil mycobacteria. Abstr. 94th Gen. Meet. Am. Sot. Microbial. Q-142, p. 413.
© Copyright 2025 Paperzz