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Biphenyl-Degrading Enzyme in Pseudomonas StrainLB400

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JOURNAL OF BACTERIOLOGY, May 1992, P. 2903-2912 0021-9193/92/092903-10$02.00/0 Copyright © 1992, American Society for Microbiology Vol. 174, No. 9 Nucleotide Sequencing and Transcriptional Mapping of the Genes Encoding Biphenyl Dioxygenase, a Multicomponent Polychlorinated- Biphenyl-Degrading Enzyme in Pseudomonas Strain LB400 BRUCE D. ERICKSON AND FRANK J. MONDELLO* Bioremediation Laboratory, Corporate Research and Development, General Electric Co., Schenectady, New York 12301 Received 11 October 1991/Accepted 10 February 1992 The DNA region encoding biphenyl dioxygenase, the first enzyme in the biphenyl-polychlorinated biphenyl degradation pathway of Pseudomonas species strain LB400, was sequenced. Six open reading frames were identified, four of which are homologous to the components of toluene dioxygenase from Pseudomonas putida Fl and have been named bphA, bphE, bphF, and bphG. From this comparison, biphenyl dioxygenase was found to be a multicomponent enzyme containing a two-subunit iron-sulfur protein, a ferredoxin, and a reductase. Comparison of the large subunit of the iron-sulfur protein and the ferredoxin with other multicomponent dioxygenases identified amino acid sequences similar to Rieske iron-sulfur proteins for binding a [2Fe-2S] cluster. Sequences have also been identified in the reductase component that match the consensus sequence for FAD or NAD binding. Transcription of the biphenyl dioxygenase region was examined, and three transcription initiation sites were identified. Transcription initiating at the site furthest upstream is greatly increased when the LB400 cells are grown on biphenyl as the sole carbon source. Polychlorinated biphenyls (PCBs) are a group of man- made compounds composed of biphenyl molecules contain- ing from 1 to 10 chlorines. Depending on the number and position of the chlorines, it is possible to produce 209 different PCB congeners. The vast majority of PCBs in the environment are derived from commercial mixtures (e.g., Aroclors) which contain 60 to 80 different congeners (24). Bacteria able to degrade PCBs are relatively common; however, in most cases, these organisms have a narrow substrate specificity which allows them to degrade only a small number of lightly chlorinated PCBs (1, 3, 7, 10, 16, 26, 28). Such strains are of limited usefulness for bioremediation as they are unable to degrade many of the congeners found in commercial PCB mixtures. Pseudomonas sp. strain LB400 is a potentially valuable organism as it is able to oxidize a wide variety of PCB congeners up to and including hexachlorobiphenyls (4). The major pathway for PCB and biphenyl degradation by strain LB400 is a four-step process initiated by the insertion of two atoms of oxygen at carbon positions 2 and 3 by biphenyl dioxygenase (a 2,3-dioxygenase). The resulting 2,3-dihydrodiol is then converted by dihydrodiol dehydroge- nase to 2,3-dihydroxybiphenyl, which is transformed by 2,3-dihydroxybiphenyl dioxygenase to 2-hydroxy-6-oxo-6- phenylhexa-2,4-dienoic acid via a meta-cleavage reaction. A hydrase reaction converts this compound to the correspond- ing benzoic acid (20). Unlike nearly all other PCB-degrading bacteria, LB400 also has a 3,4-dioxygenase activity resulting in the insertion of oxygen atoms at the 3 and 4 carbon positions. Thus far, this ability has only been demonstrated against 2,5,2',5'- tetrachlorobiphenyl, a congener with no unchlorinated 2,3 sites (20). Since mutations which inactivate the 2,3-dioxy- genase also eliminate 3,4-dioxygenase activity, it is possible that both originate from a single enzyme. Alternatively, it * Corresponding author. may be that these activities are due to different enzymes which are coregulated or that share subunits. It has been demonstrated that differences in PCB congener specificity among bacteria reflect differences in the genes encoding their PCB-degrading enzymes (the bph genes). In a previous report, we have described the cloning and charac- terization of the bph genes from strain LB400 (19). Southern hybridization experiments were used to test a variety of PCB-degrading bacteria for the presence of DNA sequences similar to any of the LB400 bph genes. No significant hybridization was detected to strains exhibiting congener specificity different from that of LB400 (30). This suggests the existence of at least two analogous 2,3-dioxygenase pathways encoded by significantly different gene sets. A bacterium (Alcaligenes eutrophus H850) with PCB-degrad- ing ability very similar to that of LB400 contained bph genes which hybridized strongly to those of LB400 (30). Biphenyl/PCB dioxygenase plays a critical role in PCB degradation by catalyzing the first step in the oxidative pathway and hence determining congener specificity. The exceptional activity of the biphenyl dioxygenase of strain LB400 has led us to study the structure and function of the genes encoding this enzyme. In this report, we describe the nucleotide sequence of these genes and their relationship to those of other dioxygenases. In addition, we used S1 nucle- ase mapping to examine the transcription of the biphenyl dioxygenase genes under a variety of conditions. MATERUILS AND METHODS Nucleotide sequencing. Two adjacent DNA fragments en- compassing the biphenyl-PCB dioxygenase genes were sub- mitted to LARK Sequencing Technologies, Dallas, Tex., for nucleotide sequencing. These were the 2.85-kb EcoRI frag- ment from pGEM453.1 and the 2.7-kb XmaI fragment of pGEM454 (19). The additional sequencing beyond the XmaI (SmaI) site was obtained by using a Sequenase kit (U.S. Biochemical Corp.) and a- 5S-dATP (Du Pont, NEN Re- 2903
Transcript

JOURNAL OF BACTERIOLOGY, May 1992, P. 2903-29120021-9193/92/092903-10$02.00/0Copyright © 1992, American Society for Microbiology

Vol. 174, No. 9

Nucleotide Sequencing and Transcriptional Mapping of the GenesEncoding Biphenyl Dioxygenase, a Multicomponent Polychlorinated-

Biphenyl-Degrading Enzyme in Pseudomonas Strain LB400BRUCE D. ERICKSON AND FRANK J. MONDELLO*

Bioremediation Laboratory, Corporate Research and Development,General Electric Co., Schenectady, New York 12301

Received 11 October 1991/Accepted 10 February 1992

The DNA region encoding biphenyl dioxygenase, the first enzyme in the biphenyl-polychlorinated biphenyldegradation pathway of Pseudomonas species strain LB400, was sequenced. Six open reading frames wereidentified, four of which are homologous to the components of toluene dioxygenase from Pseudomonas putidaFl and have been named bphA, bphE, bphF, and bphG. From this comparison, biphenyl dioxygenase was foundto be a multicomponent enzyme containing a two-subunit iron-sulfur protein, a ferredoxin, and a reductase.Comparison of the large subunit of the iron-sulfur protein and the ferredoxin with other multicomponentdioxygenases identified amino acid sequences similar to Rieske iron-sulfur proteins for binding a [2Fe-2S]cluster. Sequences have also been identified in the reductase component that match the consensus sequence forFAD or NAD binding. Transcription of the biphenyl dioxygenase region was examined, and three transcriptioninitiation sites were identified. Transcription initiating at the site furthest upstream is greatly increased whenthe LB400 cells are grown on biphenyl as the sole carbon source.

Polychlorinated biphenyls (PCBs) are a group of man-made compounds composed of biphenyl molecules contain-ing from 1 to 10 chlorines. Depending on the number andposition of the chlorines, it is possible to produce 209different PCB congeners. The vast majority of PCBs in theenvironment are derived from commercial mixtures (e.g.,Aroclors) which contain 60 to 80 different congeners (24).Bacteria able to degrade PCBs are relatively common;however, in most cases, these organisms have a narrowsubstrate specificity which allows them to degrade only asmall number of lightly chlorinated PCBs (1, 3, 7, 10, 16, 26,28). Such strains are of limited usefulness for bioremediationas they are unable to degrade many of the congeners foundin commercial PCB mixtures. Pseudomonas sp. strainLB400 is a potentially valuable organism as it is able tooxidize a wide variety of PCB congeners up to and includinghexachlorobiphenyls (4).The major pathway for PCB and biphenyl degradation by

strain LB400 is a four-step process initiated by the insertionof two atoms of oxygen at carbon positions 2 and 3 bybiphenyl dioxygenase (a 2,3-dioxygenase). The resulting2,3-dihydrodiol is then converted by dihydrodiol dehydroge-nase to 2,3-dihydroxybiphenyl, which is transformed by2,3-dihydroxybiphenyl dioxygenase to 2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoic acid via a meta-cleavage reaction. Ahydrase reaction converts this compound to the correspond-ing benzoic acid (20).

Unlike nearly all other PCB-degrading bacteria, LB400also has a 3,4-dioxygenase activity resulting in the insertionof oxygen atoms at the 3 and 4 carbon positions. Thus far,this ability has only been demonstrated against 2,5,2',5'-tetrachlorobiphenyl, a congener with no unchlorinated 2,3sites (20). Since mutations which inactivate the 2,3-dioxy-genase also eliminate 3,4-dioxygenase activity, it is possiblethat both originate from a single enzyme. Alternatively, it

* Corresponding author.

may be that these activities are due to different enzymeswhich are coregulated or that share subunits.

It has been demonstrated that differences in PCB congenerspecificity among bacteria reflect differences in the genesencoding their PCB-degrading enzymes (the bph genes). In aprevious report, we have described the cloning and charac-terization of the bph genes from strain LB400 (19). Southernhybridization experiments were used to test a variety ofPCB-degrading bacteria for the presence of DNA sequencessimilar to any of the LB400 bph genes. No significanthybridization was detected to strains exhibiting congenerspecificity different from that of LB400 (30). This suggeststhe existence of at least two analogous 2,3-dioxygenasepathways encoded by significantly different gene sets. Abacterium (Alcaligenes eutrophus H850) with PCB-degrad-ing ability very similar to that of LB400 contained bph geneswhich hybridized strongly to those of LB400 (30).Biphenyl/PCB dioxygenase plays a critical role in PCB

degradation by catalyzing the first step in the oxidativepathway and hence determining congener specificity. Theexceptional activity of the biphenyl dioxygenase of strainLB400 has led us to study the structure and function of thegenes encoding this enzyme. In this report, we describe thenucleotide sequence of these genes and their relationship tothose of other dioxygenases. In addition, we used S1 nucle-ase mapping to examine the transcription of the biphenyldioxygenase genes under a variety of conditions.

MATERUILS AND METHODS

Nucleotide sequencing. Two adjacent DNA fragments en-compassing the biphenyl-PCB dioxygenase genes were sub-mitted to LARK Sequencing Technologies, Dallas, Tex., fornucleotide sequencing. These were the 2.85-kb EcoRI frag-ment from pGEM453.1 and the 2.7-kb XmaI fragment ofpGEM454 (19). The additional sequencing beyond the XmaI(SmaI) site was obtained by using a Sequenase kit (U.S.Biochemical Corp.) and a- 5S-dATP (Du Pont, NEN Re-

2903

2904 ERICKSON AND MONDELLO

1 GAATTCCGCGAAGAA1C0GTTGGCCGTGC0CGTGGCCGCCGCACCTTCGTCCQGCGQCGTGCATGCGCCCGCCQGCGTGTCQCGATCTGCGGC100101 TGGACGGGCTCATGGCCTGCCCTTGGACGCGCCGCCAGCGCCTTGCGTCTTGCTTCACCCATCGGGTGAGTGTGCCAAACCGCGCAAAGCCGCAACTGG 200

201 ACTGGCTCAGCGCCCGATCCGTCGAGCACTGCCGGATTTAGGATC A GATGTGGGAGCGGCTGEACCCGT6GATCGCCCGAACCGC 300

301 AAGTCGTGTCAAGTTCCACCTGTACCTGATCCTGGATTTGTACAGCCGCAAGATCGTGGGTGCCGAGGTGC&CGACAGCGACGAATCTGTGCATGCCGTG 400

401 CATCTGGTGCGGCGCACCGCACTGGCCGAGGGCATCGCQGCGATGG&CACCAAACCCGTACTAAGACCTTTCCTAGGGTTTTCACTCAGGTATGGATGTC 500

501 GAATGTCGATAATAATAT6ACATTATGACGAGCCACTTGCTATCGAAGCCTGATTCAGTCCGCGCTGAAATGTGGGG0AATTCTGTAATGACCGGT600.orfO . . . .

601 Q&GAAATGCAATGAATGCGAGAACTCCAAACAGCCTCACCATGGGAGGCGACAAGTCATTTGCGGATGCGTCGCCGGTGCCCATCGCGAACGTGCGCAGC 700M N A R T P N S L T M G G D R S F A D A S P V P I A N V R S

701 cTGwimAcGmCAGnG GGC GGAGGGGCGACTCGCTGCT CACTCGCCATTGAAGATCTCAAGTCGCGCTATG 800L I E A T F Q R L R A D I" V E G R L A A G S R L A I E D L K S R Y E

801 AGGTTAGCGGCGGGACCGTGCGGGAGGCGCTTTCCCTGCTGGTGGCCAATAACCTGGTGCAGACACAGGCCCAGCGTGGATTTCATGTGACCCCCATGTC 900V S G G T V R E A L S L L V A N N L V Q T Q A Q R G F H V T P M SVSGGTVREALSLLVANNLVQTQAQRGFHvTPMs~0

901 TCTGGATGACATGCGTGATCTGGCCGCCGCGGATCGCGCTTGAGTGCGAAGCGCTGCGCCAAAGTGTGCTGAATGGCGACGCCGAATGGGAGGCGCGG 1000L D D M R D L A A T R I A L E C E A L R Q S V L N G D A E W E A R

1001 GTTGTCAGTTCGTATCACCGGCTCTCGCTCCTCGACGAGCGCACGATGCGCGATCCGGTTCACTTGTTCAATCAGTGGGAGCAAGCCAACCGCGACTTTC 1100V V S S Y H R L S L L D E R T N R D P V H L F N Q W E Q A N R D F H

1101 ACGAAGCCCTGATCTCA TCCGCCTGGACCCGCGGTTCCTGTCTATCCTGTATTTGCAAATGGAGCGCTACCGCCGATTGACGGCGATGCA 1200E A L I S A C S S A W T Q R F L S I L Y L Q M E R Y R R L T A -M H

* . * .bp . .h.1401 CCGCCCTGCQAAGGGCAATGCAACGGAGACGTTAAATCATGAGTTCAGCAATCAAAGTGCAGGGAGCCCCTGTGAAGTGGGTTACCAATTGGACGCC 1500

N~~~~~ ~RP A IN KE V Q GA P VD W V T N W T P

1501 16A00GTQCGGGTTCGACAAAAAGGGCTGTTGATCCAC CATCGCCGATCA TTTTATGATGGAGGAGCGGTTTTT 1600

IE A IR S V D R E F G L L D P*

1601 17CGCTCTGGGCTGTTACGGAGAC AGT TCCGATTCCTGGCACTTACCTGGGAAGTGG GTCATGGTCGAC 1700

GR~~~ ~ ~ S SL L LGEVP EGAT Y M G W V V M V R Q

17011GAGGC8ATCAAGGTGTTCCTGAACCAGTGCCGGACCGCGCATCTACGCCGCTCGGACGCCGG8AACGCCGGCTTTACCGCG1600E D } R I K V FD Q C R H R G MR I C RD D A G N AL A F T Cv

1801 19TCGCTTGGCTACZATTCGCGAGAGCTGGTGTGCCGGGGACGGCCACTTTTGGGCAAGATCCGGCGATGGTTTGAC 1900

Y H G N A Y D I A G S L V N V P F E K E A F C D K K E G D C G F D

1901 AAGGCCGAATGGGGCCCGCTCCAGGCACGCGTGGCAACCTACAAGGGCCTGCGTCTTTGCCACTGGGATGTGCAGGCGCaGACCTGGAGACCTACCTCG 2000

K A E W G P L QA RV A T Y K G L V F AN NAP D L F T Y LS

2001 2T10ACG0CTGGCCTACGACGTCGCCGGC CGGGAGTGGCC TTTTGCGCAGAAGGTGACCGGCTTTGA 100

D A R P Y M D V M L D R T P A G T V A I G G M Q K W V I P C N W D

2101 GTTTGCCGCAGAGCAGTTCTGCAGTGACAGGTACCACGCCGGCACCACG&CGCACCTGTCCGGCATCCTGGCGGGCATTCCGCCGGAAAGGACCTCTCG 2200

F A A E G F C Q A M Y H A G T T T H L A G I L A G I P P E M D L G

2201 CGCCGTCCCAGGATATCGGCCTGGCGCCGTGGTGATCAGCGGCCCCTGGGi 2300

2301 TGGGCCCCA&GGTCACCCAGTACTGG&CCGAGGGTCCGGCTGCCGAGCTTGCGGAACAGCGCCTGGGGCACACCGGCATGCCGGTTCGACGCATGGTCGG 2400

G P R V T Q Y V T E G P AA E L AE Q G G H T G MW V R R M V G

2401 250GC0CGCGATCTTCAGTGAQTGTACCGCCCACCQCGACGQCCTTCCGGAT CTG GCGGGTCCCCGGAAATGGTGTGCTCC 2500

Q H M T I F P T C M F L P TF N N I R IW H A G IP N E I E V WS

250126CATCGACGGCCCCGGC TTCA GGCGG CACGGCACAACTGGCATTCTCCGAGGCGGGTGTTTGGCGGTG 2600

F T L V D A D A P A E I A E E Y RG H N I R N FV A G G V F E A D D

2601 ATGGCGAGAGCTGGGTGG&ATCCAGAAGGGGCTACGTGGGTACAAGGCCAGAGCCAGCCGCTCAATGCCCAGATGGGCCTGGGTCGGTCGCAGACCGG 2700

G E N V E IY W K G L R G Y L A E Q P L N A T G L G R R Q T G

2701 TCCCGiTCTGACTGCAGCAGCAGACGGGGTTTTACCGAGGAGTTCACCGTG 2800

2801 GCCACGCTCGCCTGATC AAGACGCAATCGTTAGATCTGTCAACCGGAAGAATTCAACATGGTGGGCTGGACGTGCATGTGCAGACGGCGCGCCGAGG 2900A T L K P *

FIG. 1. Nucleotide sequence of the biphenyl dioxygenase region from Pseudomonas species strain LB400 and predicted amino acidsequences of the ORFs. The gene names are indicated above the initiation codons. Potential ribosome-binding sequences are indicated byhorizontal lines above the nucleotide sequence.

search Products), according to the manufacturer's instruc-tions.

Sequence analysis. The nucleotide sequence was analyzedby using the GCG Sequence Analysis Software Package (6).

The programs used were SEQED for sequence loading,MAP and MAPSORT for restriction site identification, MAPfor open reading frame identification, TRANSLATE foramino acid sequence determination, WORDSEARCH and

J. BACTERIOL.

VOL. 174, 1992 NUCLEOTIDE SEQUENCE OF BIPHENYL DIOXYGENASE GENES 2905

* * - * bphE. . . . .2901 TTCCGTCCCCTGATATTTACTTGGAGTAACTGTTATGACAAATCCATCCCCGCATTTTTTCAAAACATTTGAATGGCCAAGCAAGGCGGCTGGCCTTGA 3000

M T N P S P H F F K T F E W P S K A A G L E

3001 GTTGCAGACAGATCGACAGTTCTACTiCCGCGCGCAGTTGCTTGACQCCGGGCCTACGAGGCCTGGTTTGCCCTGCTGGACAAAGATATCCAC 3100L Q N E I E Q F Y Y R E A Q L L D H R A Y E A W F A L L D K D I H

3101 TACTTCATGCCGCTGCGCACCAATCGCATGATCCGGGAGGGCGAGCTGGAATATTCCGGCGACCAGGATTTAGCCCATTTCGATGAAACCCATGAAACCA 3200Y F M P L R T N R M I R E G E L E Y S G D Q D L A H F D E T H E T M

3201 TGTAC330C0TCCGCAGTGACCTCGGACGTGGCTGGG.a;AGCCGCCTTCCCGCACCGCCCCTGGTCTCCAACGTCATCGTCAAGCAGAC 3300Y G R I R K V T S D V G W A E N P P S R T R H L V S N V I V K E T

3301 GGCACGCCGGATACCTTCGAGGTCAATTCCGCATTCATCCTGTACCGCAATCGGCTTGAGCGCCAGGTCGACATCTTCGCGGGCGAACGCCGGGACGTG 3400A T P D T F E V N S A F I L Y R N R L E R Q V D I F A G E R R D V

3401 CTGCGCCGCGCCGACAACAACCTTGGTTTCACATCGCCAAGCGCACCATCCTGTCGACGCCAGTACCTTGCTGTCGAACAACCTGAGCATGTTCTTCT 3500L R R A D N N L G F S I A K R T I L L D A S T L L S N N L S M F F**- orfl * * * &

3501 AGCCCAGCACGCTGAACCGGCCTCAATGAGGATGCTGCCATGAAAAATGCAAGACTGTTTTTGATCGCCATCGGCGTCTTCTACATCATCAACCTCATTG 3600M K N A R L F L I A I G V F Y I I N L I G

3601 G30CGCTTC0CTTCACGTTGGGCTTGTTTGGCAGGATGTATCCAGGCGTAGACTGCACGTGGGTCGCCGATTTTCACCCTGCTCAGATGCCTG3700T L P F S T L G L F G R M Y P G V E L H V G A P I F T L L Q D A W

3701 30GCGGT0TCGTCTCCAGTTGCGCCATCGGGGCCGTCGCTTTGTGGGGCGCCCGCGATCCGGGCCGTTATCGGGCCGTTATTCQGTGGTQTCGCA3800A V V G L Q L G A I G A V A L W G A R D P G R Y R A V I P V V I A

3801 ACGGAAGTG3TCGATGGCCTCTGGGATTTTTACAGCATCGTGTGGAGCQCGAAGCCTTGTGGTTCGGGCTTGTCACGCTGGTCATCCATGTGCTGTGGA3900T E V V D G L W D F Y S I V W S H E A L W F G L V T L V I H V L W I

3901 TTGGCTGGG4CCTGCATGCCTGGCGTGCCCTGGCGTCGAAATCGCTGAGGACACTTTGATTACTCTTCAGCCACCMCAGTGACTGTTCGCCCCAGGCG4000G W G L H A W R A L A S K S L R T L

_ _-- bphF . * * **4001 ATTTAACCCTTTTAACTAATTACMGAAGCGTTATGAAATTTACCAGAGTTTGTGATCGAAGAGATGTGCCCGAAGGCGAAGCCCTGAAGGTCGAAAGTG 4100

M K F T R V C D R R D V P E G E A L K V E S G

4101 GAGGCACCT4CGTCGCGATTTTCATGTGGATGGCGAGCTGTTCGCMCACAGGACCGCTGCACCCACGGCGACTGGTCCCTGCTCGATGGCGGCTATCT4200G T S V A I F N V D G E L F A T Q D R C T H G D W S L L D G G Y L

4201 TGAAGGTGACGTGGTGGAATGCTCACTGCACATGGGGAAGTTTTGCGTTCGCACGGGCAAGGTCAAATCACCGCCGCCCTGTGAGGCACTGAAGATATTT 4300E G D V V E C S L H M G K F C V R T G K V K S P P P C E A L K I F

. . _- _ . bphG4301 CCGATCCGC4TCGAGACAATGACGTGCTGGTCGACTTCGAAGCCGGGTATCTGGCGCCATGATCGACACCATCGCCATCATCGGCGCCGGCCTGGCCGG4400

P I R I E D N D V L V D F E A G Y L A P *M I D T I A I I G A G L A G

4401 TTCGACGGC4GCGCGCGCACTGCGCGCCCAGGGATACGAGGGGCGCATCCACCTGCTCGGGGATGAGTCGCATCAGGCCTATGACCGGACCACGCTGTCC4500S T A A R A L R A Q G Y E G R I H L L G D E S H Q A Y D R T T L S

4501 0GACGGTG0TGGCGGGCGAGCAGCCCGAGCCGCCTGCMTCCTGGACAGCGCCTGGTACGCATCGGCCCATGTGGATGTCCAGCTCGGGCGACGGGTGA4600K T V L A G E Q P E P P A I L D S A W Y A S A H V D V Q L G R R V S

4601 GTTGCCTG40TCTGGCCAA0CGCQGATTCAGTTTGAATCGGGCGCCCCGCTGGCCTACGACCGGCTGCTGCTGGCCACCGGCGCGCGCGCCCGGCGCAT4700C L D L A N R Q I Q F E S G A P L A Y D R L L L A T G A R A R R M

4701 GGCGATTCGGGGTGGCGACCTGGCAGGCATCCATACCTTGCGAGACCTCGCCGACAGCCAGGCGCTGCGGCAGGCGCTGCMCCGGGCCAGTCGCTGGTC 4800A I R G G D L A G I H T L R D L A D S Q A L R Q A L Q P G Q S L V

4801 ATCGTCGGC4GAGGCCTGATCGGTTGCGAGGTGGCGACCACCGCCCGCAAGCTGAGTGTCCATGTCACGATTCTGGAAGCCGGCGACGAGTTGCTGGTGC4900I V G G G L I G C E V A T T A R K L S V H V T I L E A G D E L L V R

4901 GCGTGCTGGGTCACCGGACCGGGGCATGGTGTCGGGCCGAACTGGAACGCATGGGTGTCCGCGTGGAGCGCAATGCACAGGCCGCGCGCTTCGAAGGCCA 5000V L G H R T G A W C R A E L E R M G V R V E R N A Q A A R F E G Q

5001 GGGGCAGGT5CGCGCCGTGATCTGCGCCGACGGGCGCCGGGTGCCCGCCGATGTGGTCTTGGTCAGCATTGGCGCCGAGCCGGCGGACGAGCTGGCCCGTS100G Q V R A V I C A D G R R V P A D V V L V S I G A E P A D E L A R

5101 GCC5CTGGCATCGCCTGCGCGCGCGGCGTGCTGGTCGACGCCACCGGCGCCACCTCGTGTCCAGAGGTGTTCGCCGCCGGTGACGTCGCCGCCTGGCCGC5200A A G I A C A R G V L V D A T G A T S C P E V F A A G D V A A W P L

5201 TGCGTCAAG5GGGCCAGCGCTCGCTGGAGACCTACCTGAACAGCCAGATGGAGGCCGAAATCGCGGCCAGCGCCATGTTGAGTCAGCCCGTGCCGGCGCC5300R Q G G Q R S L E T Y L N S Q M E A E I A A S A M L S Q P V P A P

5301 CCAGGTGCC5ACCTGCTGGACGGAGATTGCAGGCCACCGCATCCAGATGATTGGCGATGCCGAAGGGCCCGGCGAGATCGTCGTACGCGGCGACGCCCAG5400Q V P T C W T E I A G H R I Q M I G D A E G P G E I V V R G D A Q

5401 AGCGGCCAGCCAATCGTGTTGCTCAGGCTGCTTGATGGCTGCGTCGAGGCCGCGACGGCGATCAATGCCACCAGGGAATTTTCTGTGGCGACCCGACTGG 5500S G Q P I V L L R L L D G C V E A A T A I N A T R E F S V A T R L V

5501 TCGGCACCCGGGTTTCTGTTTCCGCCGAGCAACTGCGGACGTCGGCTCGAACCTGCGGGATTTACTCAAAGCCAAACCGAATTGATGCGCATGACCGGC 5600G T R V S V S A E Q L Q D V G S N L R D L L K A K P N* - . * bphB . ..

5601 GAATCGCTTTAACAATAAAGGGGATTGGAAAAATGAAACTGAAAGGTGAAGCGGTACTGATCACGGGGGGCGCCTCCGGATTAGGGCGCGCGCTCGTGGA 5700M K L K G E A V L I T G G A S G L G R A L V

FIG. 1-Continued.

STRINGS for data base searching, GAP and BESTFIT for prepared by the hot-phenol extraction method of Salser et al.sequence alignments, and PRETTY and PUBLISH for se- (25). Cultures for the inoculum were grown to high density atquence presentation. 30°C in pseudomonas minimal medium (18), with biphenyl as

Si nuclease mapping. Whole-cell RNA for S1 mapping was the carbon source. Fresh cultures containing the appropriate

2906 ERICKSON AND MONDELLO

TABLE 1. Characteristics and comparisons of biphenyl and toluene dioxygenase components

Protein component Gene Nucleotides Amino acids Mol wt Charge pJ iducleot ide% noididentity identity

Iron-sulfur protein bphA 1,380 459 51,513 -8 6.4large subunit todCl 1,353 450 50,930 -17 5.2 67.6 65.6

Iron-sulfur protein bphE 567 188 22,085 -5 6.0small subunit todC2 564 187 22,013 -5 5.5 61.7 57.2

Ferredoxin bphF 330 109 11,981 -7 4.5 58.9todB 324 107 11,900 -8 4.5 55.1

Reductase bphG 1,227 408 42,970 -5 6.2todA 1,233 410 42,942 -9 5.0 52.

carbon source were inoculated to a starting optical density at600 nm of 0.05 and were grown at 30°C until harvesting at anoptical density at 600 nm of 0.5 to 0.8. RNA preparationsfrom 200 ml of culture medium yielded 1 to 3 mg of RNA.

Si nuclease mapping was performed essentially as previ-ously described (2, 5). Analysis was performed on 20 to 40,ug of RNA with the addition of yeast tRNA to a finalconcentration of 100 jig of RNA per reaction. Probes wereprepared by digesting pGEM453.1 (pUC18 containing the2.85-kb EcoRI fragment) with the indicated restriction en-zyme and then treating with calf intestinal alkaline phos-phatase (Boehringer Mannheim) and labeling with T4 poly-nucleotide kinase (New England BioLabs) and crude[y-32P]ATP (Du Pont, NEN Research Products). The probeswere then purified by electrophoresis on a 6% nondenaturingacrylamide gel and eluted by using a UEA electroeluter(International Biotechnologies, Inc.). Hybridizations weredone at 45 to 48°C for 3 to 4 h. Samples were then incubatedwith 200 U of S1 nuclease (Boehringer Mannheim) for 30 minat 37°C; this was followed by ethanol precipitation. Afterprecipitation, the samples were electrophoresed on a 5%acrylamide-bisacrylamide (19:1)4 M urea sequencing geland visualized by autoradiography.

Nucleotide sequence accession number. The nucleotidesequence of a 5,700-bp region ofPseudomonas species strainLB400 DNA containing the genes for biphenyl dioxygenasehas been deposited in GenBank under the accession numberM86348.

RESULTS

Nucleotide sequencing and sequence analysis of biphenyldioxygenase. The nucleotide sequence of a 5,700-bp region ofDNA encoding the LB400 biphenyl dioxygenase was deter-mined. Computer analysis identified six complete open read-ing frames (ORFs), whose nucleotide and predicted aminoacid sequences are shown in Fig. 1. The initiation codon ofeach ORF was preceded by a putative ribosome-binding site,suggesting that translation of these regions was possible. TheTGA stop and ATG start codons for ORFs 5 and 6 overlap,which may indicate that these regions are translationallycoupled. Similar arrangements have been observed for othermulticomponent catabolic enzymes such as benzoate 1,2-dioxygenase from Acinetobacter calcoaceticus (21) and thetoluene dioxygenase from Pseudomonas putida Fl (34).A partial ORF preceded by a ribosome-binding site is

located 43 bp downstream of the termination codon of ORF6. The partial nucleotide sequence of this region is virtuallyidentical to that of the bphB gene (encoding biphenyl 2,3-dihydrodiol dehydrogenase) from Pseudomonas pseudoal-caligenes KE707 (8). These data suggest that the 3' end ofthe biphenyl dioxygenase sequence is complete and that the

sequence presented extends into the LB400 gene for dihy-drodiol dehydrogenase. In addition, a sequence fragmentfrom the biphenyl dioxygenase region of KF707 (9) matchesthe beginning of ORF 2 of LB400, with 58 of 60 nucleotidesand 19 of 20 amino acids identical.The GenBank and EMBL sequence data banks were

searched for sequences similar to those of the biphenyldioxygenase ORFs. This search identified the sequences fortoluene dioxygenase from P. putida Fl (34) and benzenedioxygenase from a P. putida isolate (14). The reportedtoluene and benzene dioxygenase sequences are essentiallyidentical, with the exception of several frameshifts that maybe the result of sequencing errors. Four of the OREs fromthe biphenyl dioxygenase region showed striking similarityto the genes encoding toluene dioxygenase subunits whenthe nucleotide and amino acid sequences were compared.Characteristics of the genes and gene products and thepercent identities of the amino acid and nucleotide compar-isons of the biphenyl and toluene dioxygenase componentsare shown in Table 1. Toluene dioxygenase in P. putida Flhas a relatively broad substrate specificity and is able tooxidize a wide variety of aromatic hydrocarbons (11, 33).The enzyme has been well characterized and consists of areductase, a ferredoxin, and a tetrameric iron-sulfur proteinwith two large and two small subunits (o2f2) (27, 31). Thecoding regions of LB400 that correspond with the toluenedioxygenase components have been named bphA, bphE,bphF, and bphG. On the strength of the sequence compari-sons, we propose that bphA and bphE are homologous totodCI and todC2 and encode the large and small subunits ofthe iron-sulfur component of biphenyl dioxygenase, respec-tively. bphF encodes the ferredoxin and bphG encodes thereductase, and they are homologous to todB and todA,respectively. The amino acid identities vary from 65.5% forthe large iron-sulfur subunits to 52.1% for the reductases.Most of the predicted characteristics for these two enzymesare very similar, except for the charge and pl of the largeiron-sulfur protein subunits and the reductases.The alignment and comparison of the bph and tod amino

acid sequences are shown in Fig. 2. The amino acid identitiesare not distributed randomly throughout the sequence butshow distinct clustering. For the BphA-TodCl comparison,the first 35 residues at the amino terminus and severalintemal regions show little sequence conservation. In con-trast, there are highly conserved regions at residues 100 to128 (28 of 29), 212 to 246 (34 of 35), and 378 to 396 (19 of 19).The BphE-TodC2 comparison again shows poor sequenceconservation in the amino terminus, while several clusters atresidues 46 to 59 (12 of 14), 97 to 177 (18 of 21), and 132 to158 (24 of 27) are more highly conserved. BphF and TodBshow little sequence identity in the amino or carboxyltermini, but the middle of the protein from residues 31 to 78

J. BAcTERIOL.

NUCLEOTIDE SEQUENCE OF BIPHENYL DIOXYGENASE GENES 2907

BphA - TodCl

BphA MSSAIKEVQGVKI PAIRGLVDQBGLWD2RIYADQSLYELELI I II I I I I 1 II

TodCl ....HNNQTDTSPIRLRRSVNTSEIEALFDVAGRIDPRIYTDEDLYQLEL

51 ERVFGRSWLLLGHESIVPETGDFLATYGEDPVVWVRtDKSIKVFLN0CII111 I IIITTIIIII IIIII

IIII IIIIRRVwkDAwTTL1GHnTuXRPGDYIT¶TYwnP1VVVRCaDASATVu'LUNC

101 RHRGNRICRSDAGNAAFCSYHGWAYDIAGKLVNVPFJA KCDKKS

RHRGNRICRADAGNAKAFTCSYHGWAYDTAGNLVP Y SF.......

151 CGFDKAEWGPLQORVATYXGLVFANWDYQAPDLETYLGDARPYMDVLDRI11 11 III Hll 111 1111 I III l ill

ACLNKKENSPLKARVETYKGLIFANIIDENAVDLDTYLGEAKCFYMDHNDR

201

BphE-TodC2

SphE I4TPSPHFFTFEIIPSKAAGLELQNEIEQF.YYREAQLLDHRAYEAWFALLIII H i1ll Hill1

TodC2 .MIDSANRADVFLRKPAPVAPEIQHEVEOFYYEMLLNDRRFEEWFALL

51 DicDIHYFwLRTNNEIREGELEYSGDQDLAHDETHETMiYGRIRIVTSDV111 I H ill I 11 11 1111

AEDIHYFNPIRTTRINRDSRLEYSGSREYAHFDDDATPWRLRXITSDV

101 G0UANPPSRTRHLVSNVIVKETATPDTFVSAFILYRNRLERQVDIFAGIII lIllIlllll I lIII 11111111 11111

SMSENPASRTRHLVSKVNIVGEAEGEYEISSAFIVYRNRLERQLDIFAG

151 EZRDVLRRADJILGFSIAltRTILLDASTLLSNNLSMFFIIIIIII ii lIii111I1MI11ERRDTLaPNTSEAGFEIVNRTILIDQSTILANNLSFFF

IIIIII IPIIXFAAIQFCSDMI 11 AGW1 DTEAGTEAIPGVOCWVIPCNWKAAEQFCSDKYHAGTTSHLSGILAGL2ED

251 HDLSQAQIPTKGNQFRAAGGHGSGWDEPGSLLAVMGPKVTQYWTE(DL I IAGPGA GS VD

1L

I 11 111111 11111LEaMADLAPPrTVGKQYRASWGGHGSGFYVGDPNLMLAI4GPKVTSYWTEt

II I III I II II111 IIII I 11111111

ASEKAAERLGSVERGSKULV.EHMTVFPTCSFLPGINTVRTWHPRGPNE

351 EVWAFTLVDADAPAEIKEEYRRHNIRNFSAGGVFEQDDGENIUVEIQKGI111111 111111 1111 ll I 1111111111111111111 IEVWAFTVVDADAPDDIKEEFRRQTLRTFSAGGVFEQDDGENWVEIQHII

401 GYKAKSQPLNAQMGLGRSQTGHPDFPGNVG.YVYAEEAARGt4YHHWMI 11 I 11 11 11 111111 III 11GHKARSRPFNAEMSMnVDNDPVYPGRISNNVYSEEAARGLYAHNLRI

BphG - TodA3P

3P lBphG MIDTIAIIGAGLAGSTAARAIRAQGYEGRIHLLGDESHQAYDRTTLSKTVI I I I I IIII I 11 I III IIII III I

TodA MhTHVAIIGNGVGGFTTAQALRAEGFEGRISLIGDEPHLPYDRPSLSKAV

EV 51 IAGEQPEPPAILDSAVYASAHVDVQLGRRVSCLDLANRQIQFESGAPLAYI I l I I lI l II I

LDGSLERPPILAEADWYGEARIDMLTGPEVTALDVQTRTISLDDGTTLSA

'4I'4 151

450 SEPSWATLKP..I 11

TSPDWDALKATR 201

III1111 1 11 111 I 11 I IIIDAIVIATGSRARTMALPGSQLPGVVTLRTYGDVQVLRDSVTSATRLLIVG

GGLIGCEVATTARKLSVHVTILEAGDELLVRVLGHRTGAWCRAELERNGV111111111111111 11111111111111II1 1 I IIGGLIGCEVATTARKLGLSVTILEAGDELLVRVLGRRIGAWLRGLLTELGV

RVERNAQAARFEGQGQVRAVICADGRAVPADVVLVSIGAEPADELMAAGii 11 III II 111111 III 11

QVELGTGVVGFSGEGQLEQVHASDGRSFVADSALICVGAEPADQLARQAG

251 IACARGVLVDATGATSCPEVFAAGDVAAIPLRQGGQRSLETYLNSQMEAEBphF-TodB ACDIIRV IIL IIIV illFIVGD WVIAG Li I IOIACDRGVIVDHCGATIAItGVFAVGDVASlPLRAGGRRSLETYIINAQROA

MKFTRVCDRRDVPEGEALKVESGGTSVAIFNVDGELFATQDRCTHGDNSLII 11111 II II 111111

301

51 LDGGYLEGDVVECSLHMGtFCVRTGtICVSPPPCEALKIFPIRIEDNDVLVIII 11111 11 I11IlI1111 I I lI II I

SD.GYLDGDIVECTLHFGKFCVRTGKVKALPACKPIKVFPIKVEGDEVHV

IAASAMLSQPVPAPQVPTCWTEIAGHRIOQIGDAEGPGEIWRGDAQSGQI I I III IAAILKP LP 11

S GW GR GI

G G FSAVAAAILGIUNVSAPQLPVSIITEIAGHUU8WAGDIEGPGDFVSRGMPGSGA

351 PIVLLRLLDGCVEMATAINATREFSVATRLVGTRVSVSAEQLQDVGSNLRII I I H ll1 I

A.LLFRLQERRIQAWAVDAPRDFALATRLVEARAAIEPARLADLSNSMR

401 DLLKAKPN...

DFVRANEGDLT

FIG. 2. Comparison of the proposed components of Pseudomonas species strain LB400 biphenyl dioxygenase with the components oftoluene dioxygenase from Pseudomonas putida Fl (34). Program parameters were adjusted to suppress the labeling of similar amino acidresidues. Identical residues are indicated by vertical bars.

has 38 of 48 (47 in TodB) residues conserved. Sequenceconservation is lowest for BphG and TodA, and the aminoacid identities are spread more evenly across the sequences.The most conserved region is from amino acids 148 to 184,with stretches of 18 and 16 identical residues separated bythree nonidentical residues.

Figure 3 is a representation of the similarities in thebiphenyl and toluene dioxygenase DNA regions, with theshaded areas connecting homologous coding areas. Thearrangements of the genes encoding the subunits of bothdioxygenases are identical except for the presence of orf

upstream of bphA and orfl between bphE and bphF. The

nucleotide sequences of orfO and orfl do not correspondwith other toluene dioxygenase sequences, although theseregions are transcribed (see below). It is possible that one or

both of these reading frames encode additional componentsof biphenyl dioxygenase, but this has yet to be demon-strated.

Transcription of biphenyl dioxygenase genes. S1 nucleasemapping studies were used to determine which ORFs weretranscribed, to locate the RNA initiation sites, and to exam-ine the effect of growth substrates on transcription. TheRNA used in these experiments was extracted from LB400cultures that had been grown on biphenyl or succinate as the

VOL. 174, 1992

301

BphF

TodS MTITY

101 DFEAGYLAPII

DLDNGELK.

2908 ERICKSON AND MONDELLO

P _udawnw p. L840 bph Gene

ny Dl

A WMFI

Tolue Dioxygene

P*.udomonpgtfkb Fl tod Gene

FIG. 3. Comparison of the DNA regions that contain the genesfor biphenyl and toluene degradation. Open boxes indicate the genesand are labeled with the gene letter. Shaded regions connecthomologous sequences. Dark shading represents comparisons of thetod sequences with LB400 bph sequences, while light shadingrepresents comparisons with P. pseudoalcaligenes KF707 bphBC.Restriction sites relevant to the fragments for sequencing are

labeled.

sole carbon source or on a medium containing both biphenyland succinate.DNA upstream of the bphA coding region was probed with

a series of 5'-radiolabeled fragments. The highest-resolutionresults were obtained with Hinfl and MspI fragments of 263and 295 bp, respectively. These fragments overlap and coverthe region from within the 5' end of the bphA structural geneup to 150 to 250 bp upstream of the initiation codon. Sinuclease mapping with the Hinfl probe produced severalsignals (Fig. 4). Two major clusters of shortened protectedfragments of approximately 175 and 200 nucleotides wereseen. This suggests the existence of two potential transcrip-tion start sites located approximately 45 bp (pl) and 70 bp(p2) upstream of the bphiA initiation codon. In addition,full-length protection of the Hinfl probe was seen, indicatingtranscription coming from a third location (p3) further up-stream. Experiments with the MspI probe showed corre-

sponding bands. The protected bands in the Hinfl experi-ment that are slightly shorter than full length are probablyartifactual, as the corresponding bands in the MspI experi-ment were barely visible.

Previous work indicated that PCB degradation by LB400was enhanced when the cells were grown with biphenyl asthe sole carbon source (19). This may be the result ofincreased transcription of the bph genes under these condi-tions. Transcription from p3 was significantly reduced inLB400 cells grown with succinate, as shown by the reducedintensity of the band representing full-length protection ofthe probe. No decrease was observed in the intensity of thebands corresponding to shortened protected fragments,demonstrating that these conditions did not significantlyreduce transcription from the two sites proximal to the bphAstart codon. RNA obtained from the culture grown on

succinate and biphenyl gave an intermediate level of full-length signal (Fig. 4).To determine the location of the transcription start site p3,

we probed RNA preparations with radiolabeled DdeI andBglII-EcoRI fragnents of 629 and 778 bp, respectively. Anintense band corresponding to a protected fragment of

approximately 600 nucleotides was obtained when the DdeIprobe was hybridized with RNA extracted from biphenyl-grown LB400 cells. A much weaker band of the same sizewas observed with RNA from LB400 grown on succinate.Similar results were obtained with the BglII-EcoRI probe.The band intensity for a 260-nucleotide protected fragmentwas much greater when using RNA from biphenyl-grownversus succinate-grown cells. These data suggest that p3 islocated approximately 95 bp upstream of the orfO initiationcodon. Transcription from this promoter is induced (orderepressed) in the presence of biphenyl, since significanttranscription from this site occurs only when LB400 is grownunder these conditions.

In addition to the signal from p3, Fig. 4 shows apparentfull-length protection of the DdeI and BglII-EcoRI probes,suggesting RNA transcripts originating outside of the se-quenced region. The difference in relative intensity of thefull-length and cut-down signals for the two probes suggeststhat this is an artifact of the Si mapping technique. One suchartifact, the formation of triplex structures (5), involves therehybridization of the displaced probe strand to the RNA-DNA hybrid molecule, causing full-length protection. In-creasing the hybridization temperature to 500C greatly de-creased this full-length protection. In addition, Si mappingexperiments with a 255-bp DdeI probe fragment locatedwithin the sequenced region upstream of the 629-bp DdeIfragment showed no protection of the probe (data notshown). This indicates that there is no transcription cominginto the bph region from upstream of the sequenced DNA.Si nuclease mapping with 5'-labeled probes identifies the

5' ends of RNA molecules. These ends generally are theresult of transcription initiation but can arise from posttran-scriptional processing. To confirm that the RNA 5' ends atpl and p2 (bphA proximal) were due to promoter activity, wecloned the 263-bp Hinfl fragment and the 295-bp MspIfragment into a promoter-probe vector. The vector used wasa modified pKOl plasmid (17) which contains the promoter-less galK gene encoding galactokinase. Both fragnentsshowed promoter activity when cloned into the promoter-probe vector by complementing a galK mutation in theEscherichia coli host (data not shown). To confirm that thefragments have promoter activity in Pseudomonas species,they will be cloned into broad-host-range promoter probevectors and tested in strain LB400.

DISCUSSION

The nucleotide sequence of the DNA region encoding thebiphenyl dioxygenase ofPseudomonas species strain LB400was determined. Six ORFs were identified, four of whichwere very similar to those encoding the components oftoluene dioxygenase ofP. putida Fl. The corresponding bphand tod subunits showed amino acid identities ranging from52.1 to 65.5% and nucleotide identities ranging from 57.3 to67.6%. These data suggest that, like toluene dioxygenase,the LB400 biphenyl-PCB dioxygenase is a multicomponentenzyme made up of at least four different proteins. Based onthe sequence comparison, the genes for these proteins havebeen designated bphA and bphE (large and small subunits ofthe iron-sulfur protein, respectively), bphF (ferredoxin), andbphG (reductase).The enzymatic pathway for toluene and benzene degrada-

tion in P. putida Fl is similar to that for biphenyl and PCBsin LB400 (Fig. 5). Additional similarities in other bph and todgenes suggest that these degradation pathways are evolu-tionarily related. Dihydrodiol dehydrogenase and catechol

J. BACTERIOL.

NUCLEOTIDE SEQUENCE OF BIPHENYL DIOXYGENASE GENES 2909

A.

263

211

197

170

Hinfl 263+ 0

D. < e e

0

.8

Ddel 629

2512 < la2 z .D

527

404

309

242238

0

8C

BgII-EcoRI 778

2z

778

622527

404

309

242238

B

RNABiphenyl or.Succinate

.Biphenyl

Si nuclase probes.

778

Protected fragments

e O : I MS IIII I pip I I

off h

.~~~~~~I

* . . . .263 .

*..

. M .- 295 17

*~~~~~~~~~~~M175

-.-

778260

FIG. 4. S1 nuclease mapping of the transcription start sites in the bph region of LB400. (A) Autoradiograms of S1 nuclease reactions. Theprobe used in each reaction is listed at the top of each frame. Probe and tRNA control lanes are labeled appropriately. The remaining lanesare experimental reactions and are identified by the carbon source used to grow the LB400 prior to the RNA preparation. Protected fragmentsrepresenting transcription start sites are indicated by arrows. Size marker positions are labeled (in base pairs). (B) Schematic diagram of theS1 mapping experiments. The locations of promoters and relevant restriction sites are indicated above the diagram of the DNA region. Thearrows represent RNA transcripts and are identified with the carbon source(s) present when the transcripts are visible. DNA fragments usedas S1 nuclease probes as described in the text or used in panel A are shown. Asterisks represent the radiolabeled termini of the probefragments. Bands protected from Si nuclease digestion in panel A are indicated at the bottom.

dioxygenase in LB400 are encoded by the bphB and bphCgenes. Portions of these genes have been sequenced (Fig. 1;data not shown) and found to be nearly identical to the bphBand bphC genes in P. pseudoalcaligenes KF707 (8). KF707BphB and BphC show 58.1 and 54.6% amino acid identitywith the corresponding TodD and TodE proteins. The struc-tural homologies between bph and tod gene products arereflected in a limited functional similarity, as the toluenedegradation enzymes are capable of degrading biphenyl andsome mono- and dichlorobiphenyls to the correspondingdihydrodiols and catechols (11, 33). It has yet to be deter-mined whether the biphenyl/PCB degradation pathway isactive against toluene or chlorotoluenes.Homologous proteins generally show sequence conserva-

tion in regions necessary for structure or function. Sincetoluene dioxygenase is a well-characterized enzyme, it maybe possible to identify areas involved in substrate oxidation.

Several regions with likely structure-function roles areshown in Fig. 6. Recently, Neidle et al. (21) have reportedthe conservation of two cysteine-histidine pairs in TodCland the large iron-sulfur protein subunits from a variety ofother multicomponent dioxygenases. These cysteine-histi-dine pairs are also conserved in the BphA subunit and maybind a [2Fe-2S] center similar to the Rieske iron-sulfurproteins (12, 21, 23). A similar cysteine-histidine arrange-ment, conserved in the ferredoxin components of TodB,NdoA, and the proposed ferredoxin component of toluene-4-monooxygenase, TmoC (32), was also found in BphF.The reductase component of toluene dioxygenase is a

flavoprotein whose function is to catalyze the transfer ofelectrons from NADH to the ferredoxin. The binding ofNAD and FAD involves protein sequences capable of fold-ing into a 13t4 structure. Wierenga et al. (29) have identifiedan 11-amino-acid fingerprint sequence for regions forming

VOL. 174, 1992

2910 ERICKSON AND MONDELLO

HOOCAi(H

H

R-H be-msR Co% Tdom

FIG. 5. Degradation pathways of biphenyl-PCBs in Pseudomonas species strain LB400 and toluene-benzene in P. putida Fl. The genenames for each step are listed beneath the arrows.

these structures, and Hanukoglu and Gutfinger (13) havealigned multiple sequences to a proposed consensus se-quence for NAD-FAD binding. The reductase subunits ofbiphenyl and toluene dioxygenase (BphG and TodA, respec-tively), as well as putidaredoxin reductase (CamA) (22), eachcontain two regions matching the consensus sequence (Fig.

Slf Prtin Lag Subuniw

DKSIKVFLNQ C R H R GI C SY H GEDASIAVFLN C R H RRQI C SY H GEDGSIRAFLNV C R H R6KTLVVEEAG C SY H Gil

NGELNANNA C S HR C PF H GEDGELNAFNA C S H RGATWEFHuaTHT C SF H Gi---N-C - RG--a---- - C -H GM

VDGELFATQDR C T H GDWSLWGYLIWVVE C SL H M RTGKVDGEFFAVQDT C T H.GULSD.GWIVE C TLIHFGHWCVRTVEGEIYATDNL C T H G.SASDGYIEGRIE C PL H QGFDV-GE--A--- C T H G------GL-G---E C -L H -G-F-V-TGK

**** * * * * * * * *

BphG (1-4 0) MIDTIAII G A G LA STA A RALRAQGYEGRIHLLGDESHOQBphG (142-181) PGQSLVIV G G G LI G CV A TTARKLSVHVTILEAGDELLVRTodA(1-40) 1ATHVAII G N G VG G FTT A QAAEGFEGRISLIGDEPHLPTodA(142-181) SATRLLIV G G G LI G CV TTARKGLSVTILEAGDELLVRCamA(3-42) ANDNVVIV G T G

LG VEV A FGLRASGWEIRLVGDATVIPCamA(148-187) ADNRLVVI G G G YI G LV A ATAIKANMHVTLTAARVIR

NW/FAD Consens. +-e-* G G a G . +. . G + .

FIG. 6. Comparison of specific regions of multicomponent diox-ygenase subunits. The sequences are separated by dioxygenasecomponent and identified by name and amino acid range shown. Inthe Iron-Sulfur Protein and Ferredoxins sections, highly conservedC and H residues thought to be involved in the interaction of thepeptide chain with the [2Fe-2S] center are boxed. The lines labeledConsensus show the residues conserved in all the sequences listed.In the Reductases section, the NAD-FAD consensus binding se-quence (13) is given with the conserved amino acid residues indi-cated as follows: +, positively charged residue; *, hydrophobicresidue; ±, charged residue. The most highly conserved residues inthe known NAD-FAD-binding proteins are boxed. Asterisks indi-cate locations where both ranges of the BphG sequence match theconsensus sequence. The proteins used for the comparisons areBphA, BphF, and BphG (this study); TodCl, TodB, and TodA (34);NdoB and NdoA (15); BenA and XyIX (21); and CamA (22).

6). These may represent the site of interaction of both theflavin moiety and the NADH electron donor.

Si nuclease mapping was used to identify transcriptionstart sites in the region encoding biphenyl dioxygenase.Three such sites were identified, suggesting that biphenyldioxygenase is transcribed from multiple promoters. Two ofthe sites, pl and p2, are located approximately 45 and 70nucleotides upstream of the bphA4 start codon, respectively.The third 5' RNA end maps to approximately 95 bp upstreamof the orf start codon at a site designated p3. While none ofthese sites strongly match the consensus sequences for E.coli promoters, the pl-p2 region shows promoter activity inE. coli.

It has previously been reported that PCB degradation bystrain LB400 is greatest when the cells are grown withbiphenyl as the sole source of carbon and energy. Growth ofLB400 on succinate or a combination of succinate andbiphenyl reduces PCB-degrading ability in general and com-pletely eliminates activity against double-para-substitutedcongeners (19). Our data indicate that transcription site p3 ismuch more active in biphenyl-grown cells than in thosegrown on succinate. The increased transcription of the bphgenes from this site may account for the greater PCB-degrading ability of biphenyl-grown cells. Another possibil-ity is that in the absence of biphenyl, little or no or0 geneproduct is formed because of a lack of transcription from p3.This product may affect the activity or congener specificityof biphenyl dioxygenase, allowing the enzyme to attackdouble-para-substituted PCBs.We have no clear indication of a specific function for the

orfi gene product, although the location of this gene withinthe bph cluster suggests that it is involved in PCB degrada-tion. This is also supported by evidence that orfi is presentin the bph cluster ofA. eutrophus H850, an organism whichis similar to LB400 in PCB-degrading ability. Previousstudies with DNA-DNA hybridization showed a strongconservation of restriction sites (16 of 16) between the bphregions ofLB400 and H850 (30). One of these corresponds toa PstI site located within orfi, showing that this region hasbeen retained by both strains and may therefore have afunction. Future studies will be directed toward examiningthe roles of OrfO and Orfl in the degradation of PCBs.DNA sequence analysis clearly shows that the LB400

biphenyl dioxygenase is one of a family of homologousmulticomponent oxygenases. This family includes systems

BphA(90-125)TodC (86-121NdoB (71-106)Ben (85-120)Xy1X (80-115)Consensus

Frdox

BphF (32-76)TodB (32-75)NdoA(34-77)Consensus

J. BACTERIOL.

NUCLEOTIDE SEQUENCE OF BIPHENYL DIOXYGENASE GENES 2911

+ 02

FIG. 7. Proposed electron transport chain for the LB400 biphenyl dioxygenase. The enzyme components in the chain are indicated, as arethe genes encoding each protein. The redox state of each component is labeled (ox., oxidized; red., reduced).

with three components such as toluene, benzene, and naph-thalene dioxygenase and those with two components such asthe benzoate and toluate 1,2-dioxygenases. In the three-component systems, reducing equivalents are transportedfrom NAD(P)H through a reductase and a ferredoxin to theterminal oxygenase, while in two-component enzymes, thereductase and ferredoxin activities are contained within asingle polypeptide. It is apparent from the sequence compar-isons that biphenyl dioxygenase is a three-component en-zyme system, and we propose that its electron transportproceeds as shown in Fig. 7. The high degree of sequenceidentity between the genes involved in biphenyl and toluenedegradation shows that these pathways are closely relatedand illustrates how bacteria are developing systems capableof degrading xenobiotic compounds such as PCBs throughmodification of existing degradative pathways.

ACKNOWLEDGMENITS

This work was supported by grant CR816352 from the HazardousWaste Engineering Research Laboratory, Office of Research andDevelopment, U.S. Environmental Protection Agency, Cincinnati,Ohio.We thank P. R. Sferra, U.S. Environmental Protection Agency

project officer, for his interest and support.

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2. Barry, G., C. Squires, and C. L. Squires. 1980. Attenuation andprocessing of RNA from the rplJL-rpoBC transcription unit ofEscherichia coli. Proc. Natl. Acad. Sci. USA 77:3331-3335.

3. Bedard, D. L., R. Unterman, L. H. Bopp, M. J. Brennan, M. L.Haberl, and C. Johnson. 1986. Rapid assay for screening andcharacterizing microorganisms for the ability to degrade poly-chlorinated biphenyls. Appl. Environ. Microbiol. 51:761-768.

4. Bopp, L. H. 1986. Degradation of highly chlorinated PCBs byPseudomonas strain LB400. J. Ind. Microbiol. 1:23-29.

5. Burton, Z. F., C. A. Gross, K. K. Watanabe, and R. R. Burgess.1983. The operon that encodes the sigma subunit of RNApolymerase also encodes ribosomal protein S21 and DNAprimase in E. coli K12. Cell 32:335-349.

6. Devereux, J., P. Haeberli, and 0. Smithies. 1984. A comprehen-sive set of sequence analysis programs for the VAX. NucleicAcids Res. 12:387-395.

7. Furukawa, K. 1982. Microbial degradation of polychlorinatedbiphenyls, p. 33-57. In A. M. Chakrabarty (ed.), Biodegradationand detoxification of environmental pollutants. CRC Press,

Inc., Boca Raton, Fla.8. Furukawa, K., N. Arimura, and T. Miyazaki. 1989. Nucleotide

sequence of the 2,3-dihydroxybiphenyl dioxygenase gene ofPseudomonas pseudoalcaligenes. J. Bacteriol. 169:427-429.

9. Furukawa, K., N. Hayase, and K. Taira. 1990. Biphenyl/poly-chlorinated biphenyl catabolic gene (bph operon): organization,function, and molecular relationships in various pseudomonads,p. 111-120. In A. M. Chakrabarty, B. Iglewski, S. Kaplan, andS. Silver (ed.), Pseudomonas: biotransformations, pathogene-sis, and evolving biotechnology. American Society for Micro-biology, Washington, D.C.

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11. Gibson, D. T., G. J. Zylstra, and S. Chauhan. 1990. Biotrans-formations catalyzed by toluene dioxygenase from Pseudomo-nas putida Fl, p. 121-132. In A. M. Chakrabarty, B. Iglewski,S. Kaplan, and S. Silver (ed.), Pseudomonas: biotransforma-tions, pathogenesis, and evolving biotechnology. American So-ciety for Microbiology, Washington, D.C.

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30. Yates, J. R., and F. J. Mondello. 1989. Sequence similarities inthe genes encoding polychlorinated biphenyl degradation byPseudomonas strain LB400 andAlcaligenes eutrophus H850. J.Bacteriol. 171:1733-1735.

31. Yeh, W.-K., D. T. Gibson, and T.-N. Iu. 1977. Toluenedioxygenase: a multicomponent enzyme system. Biochem.Biophys. Res. Commun. 78:401-410.

32. Yen, K.-M., M. R Karl, L. M. Blatt, M. J. Simon, R B. Winter,P. RK Fausset, H. S. Lu, A. A. Harcourt, and K. L Chen. 1991.Cloning and characterization of a Pseudomonas mendocinaKR1 gene cluster encoding toluene-4-monooxygenase. J. Bac-teriol. 173:5315-5327.

33. Zylstra, G. J, S. Chauhan, and D. T. Gibson. 1990. Degradationof chlorinated biphenyls by Escherichia coli containing clonedgenes of the Pseudomonasputida Fl toluene catabolic pathway,p. 290-302. In Proceedings of the Sixteenth Annual HazardousWaste Research Symposium. Remedial action, treatment, anddisposal of hazardous waste. EPA/600/9-90 037. U.S. Environ-mental Protection Agency, Cincinnati, Ohio.

34. Zylstra, G. J., and D. T. Gibson. 1989. Toluene degradation byPseudomonas putida Fl: nucleotide sequence of thetodCIC2BADE genes and their expression in Escheflchia coli.J. Biol. Chem. 264:14940-14948.

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