Previous Article | Next Article 
Journal of Bacteriology, August 2004, p. 5189-5196, Vol. 186, No. 16
0021-9193/04/$08.00+0 DOI: 10.1128/JB.186.16.5189-5196.2004
Copyright © 2004, American Society for Microbiology. All Rights Reserved.
Biphenyl Dioxygenases: Functional Versatilities and Directed Evolution
Kensuke Furukawa,1* Hikaru Suenaga,2 and Masatoshi Goto1
Department of Bioscience and Biotechnology, Faculty of Agriculture, Kyushu University, Hakozaki, Fukuoka 812-8581,1
Institute for Biological Resources and Functions, National Institute of Advanced Industrial Science and Technology, Tsukuba, Ibaraki 305-8566, Japan2

INTRODUCTION
Biphenyl is a compound in which two benzene rings are connected
to each other. Polychlorinated biphenyls (PCBs) can be produced
by the direct chlorination of biphenyl, by which 209 different
compounds containing 1 to 10 chlorines can be produced. Because
PCBs have been widely used for a variety of industrial purposes,
these recalcitrant compounds are recognized to be some of the
most serious environmental pollutants worldwide. Biphenyl-utilizing
bacteria cometabolize PCBs into chlorobenzoic acids by using
biphenyl-catabolic enzymes via an oxidative route (Fig.
1).
Several biphenyl- and PCB-degrading bacteria, including both
gram-negative and gram-positive strains, have been isolated
to date (
1,
18,
19,
81). Using these bacteria, many workers
have studied the biochemical and genetic bases of PCB degradation
in detail.
Biphenyl dioxygenase (BphA) is a Resike-type, three-component
enzyme, composed of a terminal dioxygenase and an electron transfer
chain (Fig.
1) (
12,
49). The former consists of a large subunit
and a small subunit, associating as an
3ß
3 heterohexamer
(
11,
46). The latter consists of ferredoxin and its reductase
and is involved in electron transfer from NADH to reduce the
terminal dioxygenase. The terminal dioxygenase activates molecular
oxygen to introduce it into the biphenyl molecule at the 2,3
position to obtain a 2,3-dihydro-2,3-diol, which is then dehydrogenated
to 2,3-dihydroxybiphenyl by dihydrodiol dehydrogenase (BphB).
The second dioxygenase, 2,3-dihydroxybiphenyl dioxygenase (BphC),
does not require any external reductant and cleaves the 2,3-dihydroxylated
ring between carbon atoms 1 and 2 to produce 2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoic
acid (HOPD, the ring
meta-cleavage product), which is then hydrolyzed
to benzoic acid and 2-hydroxypenta-2,4-dienoate by a hydrolase
(BphD). These upper pathway enzymes in biphenyl metabolism are
encoded by the
bph gene clusters, in which
bphA1 and
bphA2 encode
a large and a small subunit of the terminal dioxygenase,
bphA3 encodes ferredoxin, and
bphA4 encodes ferredoxin reductase (Fig.
1) (
15,
20,
28,
36,
48,
79). The
bphB,
bphC, and
bphD genes
encode a dehydrogenase, a ring-cleavage dioxygenase, and a hydrolase,
respectively. Among these, the large subunit of terminal dioxygenase
is crucially involved in the substrate specificity of biphenyl
dioxygenase (
40,
42). Therefore, evolutionary molecular engineering
has been applied to large-subunit genes of different origins,
creating novel dioxygenases. Evolved biphenyl dioxygenases thus
obtained show enhanced and expanded degradation for not only
PCBs, but also other related compounds (
7,
8,
40,
42,
75-
77).
The use of evolved enzymes is also effective for the synthesis
of high-value organic molecules in the pharmaceutical industries
(
53,
72).
In this communication, we review recent advances in studies on the function, regulation, and engineering of bph genes, particularly focusing on the versatile characteristics of biphenyl dioxygenases.

STRUCTURAL VERSATILITIES OF BIPHENYL CATABOLIC bph GENES
Genes for catabolic functions are considered to have adaptively
evolved in nature by various genetic events, including mutation,
recombination, gene transfer, and assembly, resulting in a family
of diverse but highly related sequences. As a consequence, the
bph genes are present on bacterial chromosomes (
2,
3,
11,
20,
29,
35,
39,
54,
78), plasmids (
30,
65,
85), and transposons
(
45,
51,
59,
73). The chromosomal 90-kb element (termed the
bph-sal element) containing a
bph gene cluster in
Pseudomonas putida KF715 can be transferred to other
P. putida strains at
a high frequency (
59). This conjugative element is then inserted
into the chromosome of a new host. Tn
4371, a 55-kb transposable
element, displays a modular structure including a phage-like
integrase gene (
int), a
Pseudomonas-like
bph gene cluster, and
RP4- and Ti-plasmid-like transfer genes (
trb) (
52).
The typical bph gene cluster, composed of bphR1-bphA1A2(orf3)bphA3A4BCX0X1X2X3D, is seen in Pseudomonas pseudoalcaligenes KF707 (20, 79, 83, 84) and Burkholderia sp. strain LB400 (14, 28, 54, 68). The bph gene clusters identified to date demonstrate that some are very similar but some are very different in terms of gene organization and the structure of each gene (Fig. 2). Thus, it is obvious that certain bph gene clusters can move among soil bacteria and have evolved from a common ancestor. Some bph genes are significantly rearranged. For example, the bph genes in Pseudomonas sp. strain KKS102 are shuffled, in that the bphA4 gene is located downstream of bphD (36, 37). The bph cluster in P. putida KF715 lacks the 3.5-kb bphX region, the genes of which are involved in the lower pathway of biphenyl catabolism (26, 59). The organization of the bph operon of the gram-positive strain Rhodococcus globerulus P6 (62) is similar to that in KF707; however, the genetic uniqueness of this strain was first demonstrated by the presence of multiple bphC genes (5, 38). In Rhodococcus erythropolis TA421, three of the seven bphC genes are located on a linear plasmid (41). More detailed features of the bph genes of rhodococci were reported for Rhodococcus sp. strain RHA1 (17, 47, 48, 85). RHA1 harbors huge linear plasmids, including pRHL1 (1,100 kb), pRHL2 (450 kb), and pRHL3 (330 kb). The major bph gene cluster, consisting of bphA1A2A3A4-bphC-bphB, is located on pRHL1. The bphDEF genes are located on pRHL2 (47). In pRHL2, bphB2, bphDEF, bphC2, and bphC4 are also located in three separate regions (71). A total of seven (or possibly six) bphC-like genes are found in strain RHA1, of which four (or possibly three) are located on plasmids and three are on a chromosome (Fig. 2) (63). The 2-hydroxypenta-2,4-dienoate metabolic pathway genes (lower pathway genes) and the 2-hydroxypenta-2,4-dienoate hydratase (bphE1), 4-hydroxy-2-oxovalerate aldolase (bphF1), and acetaldehyde dehydrogenase (acylating) (bphG) genes are located on the chromosome, in contrast to most catabolic genes for the upper biphenyl pathway, which are located on linear plasmids. These bphGF1E1 genes are indicated to be indispensably responsible for biphenyl metabolism (64).

FUNCTIONAL VERSATILITIES OF BIPHENYL DIOXYGENASES
Aromatic ring-hydroxylating dioxygenases involved in initial
oxygenation are of particular importance because this reaction
destabilizes the aromatic ring and initiates the degradation
of aromatic compounds. These enzymes generally consist of a
terminal dioxygenase and the reductase chain (
12,
49). The terminal
dioxygenase activates molecular oxygen and introduces it to
the substrate. Some terminal dioxygenases are homomultimers,
while others are heteromultimers that comprise a large (

) and
a small (ß) subunit. The reductase chain transfers
electrons from NADH to the terminal dioxygenase (
11). The biphenyl
dioxygenase of
P. pseudoalcaligenes KF707 is a class IIB-type
three-component enzyme consisting of four subunits, including
a large subunit (BphA1) and a small subunit (BphA2) of terminal
dioxygenase, a ferredoxin (BphA3), and a ferredoxin reductase
(BphA4). BphA1 is an iron-sulfur protein containing the motif
Cys-X-His-X17-Cys-X2-His that forms a Rieske-type [2Fe-2S] cluster
involved in electron transfer from ferredoxin. BphA1 and BphA2
are associated as an
3ß
3 heterohexamer and require
Fe(II) for their activities (
46). Oxygen activation is supposed
to occur at the mononuclear iron center of BphA1.
The biphenyl dioxygenases of P. pseudoalcaligenes KF707 and Burkholderia sp. strain LB400 have been extensively studied with respect to the degradation of PCBs. These two enzymes show distinct differences in the ranges of PCBs used as substrates. The range of PCB congeners oxidized by the LB400 enzyme is much wider than that oxidized by the KF707 enzyme (16, 22). However, KF707 biphenyl dioxygenase has a higher activity for several di-para-substituted PCBs. The purified LB400 biphenyl dioxygenase has the remarkable ability to oxidize PCB congeners that contain up to four chlorines by introducing two hydroxyl groups at either the 2,3 or 3,4 positions. The specificity of the LB400 biphenyl dioxygenase for PCBs was correlated with the relative positions of the chlorine substituents on the aromatic rings rather than with the number of chlorine substituents on the rings (4). The attack by the biphenyl dioxygenase of Burkholderia sp. strain LB400 on several symmetrical ortho-substituted biphenyls or quasi ortho-substituted biphenyl analogues was investigated. 2,2'-Difluoro-, 2,2'-dibromo-, 2,2'-dinitro-, and 2,2'-dihydroxybiphenyl were accepted as substrates. Dioxygenation of all of these compounds shows a strong preference for the semisubstituted pair of vicinal ortho and meta carbons, leading to the formation of 2'-substituted 2,3-dihydroxybiphenyls by the subsequent elimination of HX (X = F, Br, NO2, or OH) (67). The absence of 3,4-dioxygenase activity in KF707 is another significant difference between the two dioxygenases.
The biphenyl dioxygenase from Comamonas testosteroni B-356 transforms dichlorobiphenyls in the following order of apparent specificities: 3,3'-CB > 2,2'-CB > 4,4'-CB. PCB congeners such as 2,2'-CB exact a high energetic cost, produce a cytotoxic compound (H2O2), and inhibit the degradation of other congeners (33). The biphenyl dioxygenase from R. globerulus P6 exhibits the following ring substitution preference for six mono- and dichlorinated PCB congeners: no substitution > meta > para > ortho substitution. This enzyme shows a strict specificity for attacking at nonhalogenated ortho or meta vicinal carbons, as in the case of KF707 biphenyl dioxygenase (50).
Despite the major difference in the PCB degradation capacities between P. pseudoalcaligenes KF707 and Burkholderia sp. strain LB400, it is particularly interesting that the biphenyl catabolic bph genes of these two strains are nearly identical in gene organization and nucleotide sequence. The identities of these components between KF707 and LB400 are as follows: BphA1 (KF707) and BphA (LB400), 95.6%; BphA2 (KF707) and BphE (LB400), 99.5%; BphA3 (KF707) and BphF (LB400), 100%; and BphA4 (KF707) and BphG (LB400), 100% (15, 79). The major discrepancy is seen in the large subunit, in which 20 amino acids (including 1 amino acid that is lacking in KF707 BphA1) are different among 460 total amino acids (15, 79). Several lines of evidence, as follows, revealed that the large subunit of terminal dioxygenase is responsible for the recognition and binding of substrates and thereby for substrate specificity (21, 27, 40), although there are reports that the small subunit is also involved in substrate recognition (13, 32). (i) A hybrid dioxygenase composed of TodC1 (F1) and BphA2A3A4 (KF707), which was constructed by the replacement of KF707 bphA1 with todC1 (encoding an iron-sulfur protein of toluene dioxygenase from P. putida F1), exhibits a substrate specificity similar to that of the original toluene dioxygenase (21, 27). (ii) A hybrid biphenyl dioxygenase composed of BphA1 (LB400) and BphA2A3A4 (KF707) exhibits a wide-ranging PCB degradation capability similar to that of the original LB400 biphenyl dioxygenase (40). Thus, only a 20-amino-acid difference in the large subunits leads to a major difference in the PCB degradation capabilities of these two biphenyl dioxygenases. The KF707 enzyme primarily recognizes the 4'-chlorinated ring structure (97%) of 2,5,4'-CB and introduces a molecular oxygen at the 2',3' position. On the other hand, the LB400 enzyme primarily binds (recognizes) the 2,5-dichlorinated ring structure (95%) of the same compound and introduces O2 at the 3,4 position. Kimura et al. constructed a variety of chimeric large-subunit genes by exchanging four common restriction fragments between the KF707 bphA1 and LB400 bphA1 genes (40). Upon expression in Escherichia coli cells, various chimeric biphenyl dioxygenases revealed that a relatively small number of amino acids in the carboxy-terminal half (among 20 different amino acids in total) are involved in the recognition of the chlorinated ring and the sites of dioxygenation. Further study revealed that the site-directed mutagenesis of Thr-376 (KF707) to Asn-376 (LB400) in the KF707 biphenyl dioxygenase resulted in the expansion of the range of biodegradable PCB congeners (40). Mondello et al. investigated the large-subunit proteins in more detail (55). A comparison of large-subunit protein sequences of KF707-type and LB400-type strains identified four regions (designated I, II, III, and IV) in which specific sequences were consistently associated with either a broad or narrow PCB substrate specificity. A combination of mutations between KF707-type BphA1 and LB400-type BphA in regions III and IV resulted in dramatic differences in the substrate specificity. Altering the regions in the LB400 BphA in order to correspond to those in the KF707 bphA1 sequence produced a narrow substrate specificity that was very similar to that of KF707. A stretch of seven amino acids, termed region III, is of particular interest. Some individual mutations within region III alone improved the PCB degradative activity, especially for di-para-substituted congeners. However, the highest improvements in activity were obtained from multiple amino acid modifications in region III, suggesting that the effects of these mutations are cooperative. Barriault et al. also constructed a biphenyl dioxygenase by using common restriction sites to exchange DNA fragments between Burkholderia sp. strain LB400 bphA and C. testosteroni B-356 bphA1, showing that modifications of the C-terminal portion of the LB400
subunit can change the catalytic properties of the enzyme (8).
Oxygenase components from C. testosteroni B-356 and Rhodococcus sp. strain RHA1 were crystallized, and X-ray diffraction was measured (33, 57). The crystal structures of a Rieske ferredoxin of Burkholderia sp. strain LB400 (14) and an NADH-dependent ferredoxin reductase of Pseudomonas sp. strain KKS102 (69) were solved. This structural information may provide more detailed insight into the substrate specificity and mode of oxygenation of various biphenyl dioxygenases.

VERSATILE REGULATION OF bph GENES
Despite detailed biochemical and genetic analyses of the
bph genes of various bacteria, our knowledge concerning regulation
has remained unclear for a long time. Recently, the regulatory
mechanisms of the
bph genes of several strains have been studied.
The regulation of the
bph gene cluster,
bphR1-bphA1A2(orf3)bphA3A4BCX0X1X2X3D,
in
P. pseudoalcaligenes KF707 was recently reported in some
detail by Watanabe et al. (
83,
84). In this system, two regulatory
genes,
bphR1 and
bphR2, were identified. The
bphR1 gene is located
just upstream of
bphA1, but
bphR2 is separated from the other
bph genes. The BphR1 protein belongs to the GntR family and
the BphR2 protein belongs to the LysR family, showing a high
similarity (81%) to NahR (the naphthalene and salicylate catabolic
regulator) (
66). Both regulatory proteins act as activators,
and at least six transcriptional start sites are mapped in this
gene cluster. Thus, there are two regulatory systems as follows:
(i)
bphR1-dependent transcription for
bphR1 itself,
bphX0X1X2X3,
and
bphD and (ii)
bphR2-dependent transcription for
bphA1A2(orf3)A3A4BC.
In this regulatory system, it is believed that the BphR2 protein
first activates the transcription of
bphA1A2(orf3)A3A4BC to
convert biphenyl to the
meta-cleavage compound (HOPD), which
binds to BphR1 to activate this protein. The activated BphR1
protein binds to the promoter-operator regions of
bphR1 itself
and to
bphX0,
bphX1, and
bphD to promote the transcription of
these genes (Fig.
3). The transcription of the
bph locus of
Burkholderia sp. strain LB400, whose
bph genes are very similar
to those of KF707, was investigated (
9). In this system, the
ORF0 protein (corresponding to KF707 BphR1) mediates the activation
of the
bphA1 promoter. The four major 5' ends were mapped between
25 and 70 bp upstream of the start codon of the
bphA1 gene.
Sequence elements between approximately positions 710 and 1080
upstream were required in
cis for full functioning of the respective
promoter(s). It should be noted that the regulatory mechanisms
of the
bph genes are totally different between
P. pseudoalcaligenes KF707 and
Burkholderia sp. strain LB400, despite the fact that
the
bph genes of these two strains are nearly identical. The
expression of the
bph genes of
Pseudomonas sp. strain KKS102
is also induced by the ring
meta-cleavage product (HOPD), as
in the case of
P. pseudoalcaligenes KF707 (
61). The
bph genes
[
bphEGF(orf4)A1A2A3BCD(orf1)A4R] of strain KKS102 constitute
an operon whose expression is strongly dependent on the
pE promoter
located upstream of the
bphE gene. A
bphS gene, whose deduced
amino acid sequence shows homology with the GntR family of transcriptional
repressors, was identified in the upstream region of the
bphE gene. Disruption of the
bphS gene resulted in constitutive expression
of the
bph genes, suggesting that BphS negatively regulates
the
pE promoter. Gel retardation and DNase footprinting analyses
demonstrated specific binding of BphS to the
pE promoter region
and identified four BphS binding sites. The binding of BphS
is abolished in the presence of HOPD (
60). Thus, the BphS protein
acts as a repressor in strain KKS102, unlike BphR1 of strain
KF707, which acts as an activator.
The
bphEGForf4A1A2A3BCD operon in Tn
4371 in
Ralstonia eutropha A5 is transcribed from a
70 promoter, and the
bphS gene product
(GntR-like regulator) negatively regulates the transcription
of the
bph gene cluster as a repressor (
56). The
bph operon
in gram-positive
Rhodococcus sp. strain M5,
bpdC1C2BADEF, is
suggested to be regulated by the two-component signal transduction
system of
bpdS and
bpdT (
43). In this system, BpdS and BpdT
seem to function as a sensor histidine kinase and a response
regulator, respectively. Recently, Takeda et al. (
80) reported
the regulatory system of
Rhodococcus sp. strain RHA1 in more
detail. The transcription of the
bphA1A2A3A4C1B operon, located
on the linear plasmid pRH1, is positively regulated by a set
of two-component regulatory genes (termed
bphS and
bphT). The
bphS and
bphT genes promote transcriptional induction by various
aromatic compounds, such as biphenyl, benzene, and substituted
benzenes. The possible induction mechanism by
bphST is presented
as follows. In the absence of biphenyl,
bphST genes are constitutively
transcribed from the adjacent
bphSp promoter at the basal level.
In the presence of biphenyl, biphenyl activates the
bphS product
(BphS), which then activates the
bphT product (BphT) by phosphorylation.
The activated BphT protein promotes transcription from
bphA1p and induces expression of the
bphA1A2A3A4C1B and
bphST genes.
Thus, it is interesting that GntR-like regulators appear to
be common in
bph clusters from gram-negative bacteria, whereas
gram-positive bacteria have two-component regulatory systems
to control
bph expression. It is also true that the regulation
of the
bph genes is very versatile from strain to strain. These
versatilities reflect the fact that certain
bph genes are foreign
genes derived from other strains and are regulated in different
fashions in the new host strains.

DIRECTED EVOLUTION OF BIPENYL DIOXYGENASES
Enzymes that comprise different catabolic pathways exhibit a
peculiar substrate specificity for different aromatic compounds
or catabolic intermediates. Sequence analyses of aromatic ring-degradative
enzymes revealed that they can be grouped into families that
are similar in size and amino acid sequence (
12,
23,
58). Enzymes
belonging to the same family have evolved from a common ancestor
to acquire a new catabolic function through various genetic
events, such as gene transfer, recombination, duplication, multiple
point mutation, deletion, and integration (
24,
25,
31). Thus,
we could learn how new degradation abilities appeared through
a long historical period. Gene manipulation techniques have
opened up a way to alter the function of aromatic ring dioxygenases.
Thus, mutant enzymes with an enhanced degradation ability for
biphenyl and its related compounds and also with a novel capability
to transform the heterocyclic aromatic compounds can be generated.
DNA shuffling is a method for random recombination of selected genes in vitro by fragmentation and PCR reassembly (74). This technique was applied to the bphA1 gene of P. pseudoalcaligenes KF707 and the bphA gene of Burkholderia sp. strain LB400 (42) because the large subunits of the biphenyl dioxygenases of these two strains are crucially responsible for substrate specificity in a different manner. E. coli cells expressing shuffled (evolved) bph genes were incubated with biphenyl, 4-chlorobiphenyl (4-CB), 2,2'-dichlorobiphenyl (2,2'-CB), 4,4'-dichlorobiphenyl (4,4'-CB), 2,5,4'-trichlorobiphenyl (2,5,4'-CB), 4-methylbiphenyl (4-MB), diphenylmethane (DM), and dibenzofuran (DF). E. coli cells expressing the original KF707 BphA1 enzyme and E. coli cells expressing the original LB400 BphA enzyme exhibited major differences in the formation of the ring meta-cleavage yellow products for many biphenyl compounds. Large amounts of yellow compounds were produced from 4,4'-CB, 2,5,4'-CB, and DM by the KF707 enzyme, but not by the LB400 enzyme. In contrast, large amounts of yellow compounds were produced from 2,2'-CB and DF by the LB400 enzyme, but not by the KF707 enzyme. Thus, major differences can be seen in these two parental enzymes that are used for shuffling evolution. E. coli cells expressing some evolved BphA1 proteins exhibited interesting features in the production of ring meta-cleavage yellow compounds. One such E. coli clone carrying pSHF1045 exhibited an enhanced production of yellow compounds from biphenyl, 4-CB, 4-MB, and 4,4'-CB relative to E. coli expressing the original KF707 enzyme. The same clone produced yellow compounds from DF and 2,2'-CB but no yellow compound from 2,5,4'-CB, from which a 3,4-dihydrodiol compound is produced as a dead-end product, as did E. coli expressing the LB400 enzyme. Another E. coli clone carrying pSHF1072 gained a novel degradation activity for toluene and benzene and produced indigo from indole. The same clone exhibited a much higher activity toward monocyclic aromatic compounds such as ethylbenzene, butylbenzene, and isopropylbenzene than did E. coli expressing the KF707 enzyme (76). The deduced amino acid sequences of such evolved large subunits showed only a few amino acid changes from the original enzymes. Barriault et al. also did family shuffling of a targeted region of the large-subunit genes from Burkholderia sp. strain LB400, C. testosteroni B-356, and R. globerulus P6. Some variants showed a high activity toward 2,2'-CB, 3,3'-CB, 4,4'-CB, and 2,6-CB (7).
A method of random-priming recombination (70) is also a powerful tool for evolutionary molecular engineering of an enzyme. The bphA1 gene of P. pseudoalcaligenes KF707 was subjected to this mutagenesis. One of the resultant biphenyl dioxygenases thus obtained exhibited novel multifunctional oxygenase activities (75). This evolved enzyme attacked at the angular position adjacent to the hetero atom of heterocyclic aromatic compounds such as dibenzofuran and dibenzo-p-dioxin (angular dioxygenation). The same enzyme also introduced two atoms of molecular oxygen into the aromatic ring of dibenzofuran and dibenzo-p-dioxin (lateral dioxygenation). Furthermore, the enzyme exhibited sulfoxidation for dibenzothiophene and monooxygenation for fluorene. Based on the structural information developed from crystallographic analyses of naphthalene dioxygenase (34), Suenaga et al. constructed 12 site-directed BphA1 mutants with changes in the amino acids that coordinate the catalytic nonheme iron center (77). The Ile335Phe, Thr376Asn, and Phe377Leu biphenyl dioxygenase mutants exhibited altered regiospecificities for various PCBs compared with the wild-type biphenyl dioxygenase. In particular, the Ile335Phe mutant acquired the ability to degrade 2,5,2',5'-CB by 3,4-dioxygenation and showed bifunctional 2,3-dioxygenase and 3,4-dioxygenase activities for 2,5,2'-CB and 2,5,4'-CB. Furthermore, two mutants, the Phe227Val and Phe377Ala mutants, introduced molecular oxygen at the 2,3 position, forming 3-chloro-2',3'-dihydroxybiphenyl with concomitant dechlorination.
Another successful application by modified biphenyl dioxygenases is the bioconversion of a variety of heterocyclic aromatic compounds, such as flavone, flavanone, and ionized aromatics. A recombinant E. coli strain expressing pSHF1072, carrying biphenyl dioxygenase, converted 1-methoxynaphthalene, dibenzothiophene, xanthene, 1-phenylpyrazole, 2-phenylpyridine, and 4-phenylpyrimidine into their corresponding cis-dihydrodiols (53). Recombinant Streptomyces lividans expressing the same enzyme converted flavone, 6-hydroxyflavone, 7-hydroxyisoflavone, and trans-chalone to the corresponding mono- or di-hydroxylated compounds (72). The same evolved enzyme could also transform the molecular structure of a variety of aromatic compounds, including carboxylic acids or amines such as 1-naphthoic acid, 2-(1-naphthyl) acetic acid, diphenylamine, and 1-benzyl-4-piperidone. These ionized aromatics were converted to the corresponding 1,2-dihydrodiol or mono- or trihydroxy forms. According to the three-dimensional structure model constructed based on the naphthalene dioxygenase (34), diphenylamine can be well accommodated within the active site of the evolved BphA1 (Fig. 4). The hydroxylation site of diphenylamine is located adjacent to the catalytic iron in evolved BphA1, while the location of the diphenylamine in the active site of the wild-type BphA1 enzyme is far from the iron molecule. These products that were converted by evolved biphenyl dioxygenase are potentially useful as versatile starting materials for the chemical synthesis of pharmaceuticals and biologically active organic molecules.

CONCLUSIONS
Biphenyl-utilizing bacteria are ubiquitously distributed in
nature. These bacteria are considered to be involved in the
final stage of plant lignin degradation as well as with other
aromatic degraders. Biochemical and genetic studies on PCB degradation
provide us knowledge about how microorganisms acquire new and
novel degradation capabilities for man-made xenobiotic compounds.
Biphenyl dioxygenase is an interesting enzyme that provides
a good model system for molecular evolutionary engineering.
One major advantage of this technology is that only minimal
prior information is required. It has been demonstrated that
evolved biphenyl dioxygenases can be used for the degradation
of PCBs and other environmental pollutants, including dioxins
and chlorinated ethenes. Moreover, the use of evolved biphenyl
dioxygenases is effective for the synthesis of high-value organic
molecules, because many of the products generated by these enzymes
are difficult to synthesize by existing methods of organic chemistry.
It should be feasible to complement the methods of combinatorial
chemistry with biotechnological methods.

ACKNOWLEDGMENTS
K.F. thanks Fumio Matsumura and Ananda M. Chakrabarty for their
kind and helpful discussions.
This work was supported in part by a grant-in-aid (Hazardous Chemicals) from the Ministry of Agriculture, Forestry, and Fisheries of Japan (HC-04-2321-1).

FOOTNOTES
* Corresponding author. Mailing address: Department of Bioscience and Biotechnology, Faculty of Agriculture, Kyushu University, Hakozaki, Fukuoka 812-8581, Japan. Phone: 81 (92) 642-2849. Fax: 81 (92) 642-2849. E-mail:
kfurukaw{at}agr.kyushu-u.ac.jp.


REFERENCES
1 - Abramowicz, D. A. 1990. Aerobic and anaerobic biodegradation of PCBs: a review. Crit. Rev. Biotechnol. 10:241-251.
2 - Ahmad, A. D., J. Fraser, M. Sylvestre, A. Larose, J. Bergeron, J. M. Juteau, and M. Sondossi. 1995. Sequence of the bphD gene encoding 2-hydroxy-6-oxo-(phenyl/chlorophenyl)hexa-2,4-dienoic acid (HOP/cPDA) hydrolase involved in the biphenyl/polychlorinated biphenyl degradation pathway in Comamonas testosteroni: evidence suggesting involvement of Ser112 in catalytic activity. Gene 156:69-74.[CrossRef][Medline]
3 - Ahmad, D., M. Sylvestre, and M. Sondossi. 1991. Subcloning of bph genes from Pseudomonas testosteroni B-356 in Pseudomonas putida and Escherichia coli: evidence for dehalogenation during initial attack in chlorobiphenyls. Appl. Environ. Microbiol. 57:2880-2887.[Abstract/Free Full Text]
4 - Arnett, C. M., J. V. Parales, and J. D. Haddock. 2000. Influence of chlorine substituents on rates of oxidation of chlorinated biphenyls by the biphenyl dioxygenase of Burkholderia sp. strain LB400. Appl. Environ. Microbiol. 66:2928-2933.[Abstract/Free Full Text]
5 - Asturia, J. A., J. D. Eltis, M. Prucha, and K. N. Timmis. 1994. Analysis of three 2,3-dihydroxybiphenyl 1,2-dioxygenase genes found in Rhodococcus globerulus P6. J. Biol. Chem. 269:7807-7815.[Abstract/Free Full Text]
6 - Asturias, J. A., and K. N. Timmis. 1993. Three different 2,3-dihydroxybiphenyl-1,2-dioxygenase genes in the gram-positive polychlorobiphenyl-degrading bacterium Rhodococcus globerulus P6. J. Bacteriol. 175:4631-4640.[Abstract/Free Full Text]
7 - Barriault, D., M. Plante, and M. Sylvestre. 2002. Family shuffling of targeted bphA region to engineer biphenyl dioxygenase. J. Bacteriol. 184:3794-3800.[Abstract/Free Full Text]
8 - Barriault, D., C. Simard, H. Chatel, and M. Sylvestre. 2001. Characterization of hybrid biphenyl dioxygenases obtained by recombining Burkholderia sp. strain LB400 bphA with the homologous gene of Comamonas testosteroni B-356. Can. J. Microbiol. 47:1025-1032.[CrossRef][Medline]
9 - Beltrametti, F., D. Reniero, S. Backhaus, and B. Hofer. 2001. Analysis of transcription of the bph locus of Burkholderia sp. strain LB400 and evidence that the ORF0 gene product acts as a regulator of the bphA1 promoter. Microbiology 147:2169-2182.[Abstract/Free Full Text]
10 - Bergeron, J., D. Ahmad, D. Barriault, A. Larose, M. Sylvestre, and J. Powlowski. 1994. Identification and mapping of the gene translation products involved in the first steps of the Comamonas testosteroni B-356 biphenyl/chlorobiphenyl biodegradation pathway. Can. J. Microbiol. 40:743-753.[Medline]
11 - Broadus, R. M., and J. D. Haddock. 1998. Purification and characterization of the NADH:ferredoxinBPH oxidoreductase component of biphenyl 2,3-dioxygenase from Pseudomonas sp. strain LB400. Arch. Microbiol. 170:106-112.[CrossRef][Medline]
12 - Bulter, C. S., and J. R. Mason. 1997. Structure-function analysis of the bacterial aromatic ring-hydroxylating dioxygenases. Adv. Microb. Physiol. 38:47-84.[Medline]
13 - Chebrou, H., Y. Hurtubise, D. Barriault, and M. Sylvestre. 1999. Heterologous expression and characterization of the purified oxygenase component of Rhodococcus globerulus P6 biphenyl dioxygenase and of chimeras derived from it. J. Bacteriol. 181:4805-4811.[Abstract/Free Full Text]
14 - Colbert, C. L., M. M. Couture, L. D. Eltis, and J. T. Bolin. 2000. A cluster exposed: structure of the Rieske ferredoxin from biphenyl dioxygenase and the redox properties of Rieske Fe-S proteins. Struct. Fold Des. 8:1267-1278.[Medline]
15 - Erickson, B. D., and F. J. Mondello. 1992. Nucleotide sequencing and transcriptional mapping of the genes encoding biphenyl dioxygenase, a multicomponent polychlorinated-biphenyl-degrading enzyme in Pseudomonas strain LB400. J. Bacteriol. 174:2903-2912.[Abstract/Free Full Text]
16 - Erickson, B. D., and F. J. Mondello. 1993. Enhanced biodegradation of polychlorinated biphenyls after site-directed mutagenesis of a biphenyl dioxygenase gene. Appl. Environ. Microbiol. 59:3858-3862.[Abstract/Free Full Text]
17 - Fukuda, M., S. Shimizu, N. Okita, M. Seto, and E. Masai. 1998. Structural alteration of linear plasmids encoding the genes for polychlorinated biphenyl degradation in Rhodococcus strain RHA1. Antonie Leeuwenhoek 74:169-173.
18 - Furukawa, K. 1982. Microbial degradation of polychlorinated biphenyls, p. 33-57. In A. M. Chakrabarty (ed.), Biodegradation and detoxification of environmental pollutants. CRC Press, Boca Raton, Fla.
19 - Furukawa, K. 1994. Molecular genetics and evolutionary relationship of PCB-degrading bacteria. Biodegradation 5:289-300.[CrossRef][Medline]
20 - Furukawa, K., and T. Miyazaki. 1986. Cloning of a gene cluster encoding biphenyl and chlorobiphenyl degradation in Pseudomonas pseudoalcaligenes. J. Bacteriol. 166:392-398.[Abstract/Free Full Text]
21 - Furukawa, K., J. Hirose, A. Suyama, T. Zaiki, and S. Hayashida. 1993. Gene components responsible for discrete substrate specificity in the metabolism of biphenyl (bph operon) and toluene (tod operon). J. Bacteriol. 175:5224-5232.[Abstract/Free Full Text]
22 - Gibson, D. T., D. L. Cruden, J. D. Haddock, G. J. Zylstra, and J. M. Brand. 1993. Oxidation of polychlorinated biphenyls by Pseudomonas sp. strain LB400 and Pseudomonas pseudoalcaligenes KF707. J. Bacteriol. 175:4561-4564.[Abstract/Free Full Text]
23 - Harayama, S., and M. Kok. 1992. Functional and evolutionary relationship among diverse oxygenases. Annu. Rev. Microbiol. 46:565-601.[CrossRef][Medline]
24 - Harayama, S., M. Rekik, A. Bairoch, E. Neidle, and L. N. Ornston. 1991. Potential DNA slippage structure acquired during evolutionary divergence of Acinetobacter calcoaceticus chromosomal benABC and Pseudomonas putida TOL pWW0 plasmid xylXYZ, genes encoding benzoate dioxygenases. J. Bacteriol. 173:7540-7548.[Abstract/Free Full Text]
25 - Hartnett, C., E. L. Neidle, K. Ngai, and L. N. Ornston. 1990. DNA sequence of genes encoding Acinetobacter calcoaceticus protocatechuate 3,4-dioxygenase: evidence indicating shuffling of genes and of DNA sequence within genes during their evolutionary divergence. J. Bacteriol. 172:956-966.[Abstract/Free Full Text]
26 - Hayase, N., K. Taira, and K. Furukawa. 1990. Pseudomonas putida KF715 bphABCD operon encoding biphenyl and polychlorinated biphenyl degradation: cloning, analysis, and expression in soil bacteria. J. Bacteriol. 172:1160-1164.[Abstract/Free Full Text]
27 - Hirose, J., A. Suyama, S. Hayashida, and K. Furukawa. 1994. Construction of hybrid biphenyl (bph) and toluene (tod) genes for functional analysis of aromatic ring dioxygenases. Gene 138:27-33.[CrossRef][Medline]
28 - Hofer, B., S. Backhaus, and K. N. Timmis. 1994. The biphenyl/polychlorinated biphenyl-degradation locus (bph) of Pseudomonas sp. LB400 encodes four additional metabolic enzymes. Gene 144:9-16.[CrossRef][Medline]
29 - Hofer, B., L. D. Eltis, D. N. Dowling, and K. N. Timmis. 1993. Genetic analysis of a Pseudomonas locus encoding a pathway for biphenyl/polychlorinated biphenyl degradation. Gene 130:47-55.[CrossRef][Medline]
30 - Hooper, S. W., T. C. Dockendorff, and G. S. Sayler. 1989. Characteristics and restriction analysis of the 4-chlorobiphenyl catabolic plasmid, pSS50. Appl. Environ. Microbiol. 55:1286-1288.[Abstract/Free Full Text]
31 - Horn, J. M., S. Harayama, and K. N. Timmis. 1991. DNA sequence determination of the TOL plasmid (pWW0) xylGFJ genes of Pseudomonas putida: implication for the evolution of aromatic catabolism. Mol. Microbiol. 5:2459-2474.[Medline]
32 - Hurtubise, Y., D. Barriault, and M. Sylvestre. 1998. Involvement of the terminal oxygenase ß subunit in the biphenyl dioxygenase reactivity pattern toward chlorobiphenyls. J. Bacteriol. 180:5828-5835.[Abstract/Free Full Text]
33 - Imbeault, N. Y., J. B. Powlowski, C. L. Colbert, J. T. Bolin, and L. D. Eltis. 2000. Steady-state kinetic characterization and crystallization of a polychlorinated biphenyl-transforming dioxygenase. J. Biol. Chem. 275:12430-12437.[Abstract/Free Full Text]
34 - Kauppi, B., K. Lee, E. Carredano, R. E. Parales, D. T. Gibson, H. Eklund, and S. Ramaswamy. 1998. Structure of an aromatic ring-hydroxylating dioxygenase-naphthalene 1,2-dioxygenase. Structure 6:571-586.[Medline]
35 - Khan, A. A., and S. K. Walia. 1989. Cloning of bacterial genes specifying degradation of 4-chlorobiphenyl from Pseudomonas putida OU83. Appl. Environ. Microbiol. 55:798-805.[Abstract/Free Full Text]
36 - Kikuchi, Y., Y. Nagata, M. Hinata, K. Kimbara, M. Fukuda, K. Yano, and M. Takagi. 1994. Identification of the bphA4 gene encoding ferredoxin reductase involved in biphenyl and polychlorinated biphenyl degradation in Pseudomonas sp. strain KKS102. J. Bacteriol. 176:1689-1694.[Abstract/Free Full Text]
37 - Kikuchi, Y., Y. Yasukochi, Y. Nagata, M. Fukuda, and M. Takagi. 1994. Nucleotide sequence and functional analysis of the meta-cleavage pathway involved in biphenyl and polychlorinated biphenyl degradation in Pseudomonas sp. strain KKS102. J. Bacteriol. 176:4269-4276.[Abstract/Free Full Text]
38 - Kim, C. K., E. Kim, J. C. Chae, and Y. Kim. 1996. Structure of the pcbC gene encoding 2,3-dihydroxybiphenyl dioxygenase of Pseudomonas sp. P20. Biochem. Biophys. Res. Commun. 226:15-20.[CrossRef]
39 - Kimbara, K., T. Hashimoto, M. Fukuda, T. Koana, M. Takagi, M. Oishi, and K. Yano. 1989. Cloning and sequencing of two tandem genes involved in degradation of 2,3-dihydroxybiphenyl to benzoic acid in the polychlorinated biphenyl-degrading soil bacterium Pseudomonas sp. strain KKS102. J. Bacteriol. 171:2740-2747.[Abstract/Free Full Text]
40 - Kimura, N., A. Nishi, M. Goto, and K. Furukawa. 1998. Functional analyses of a variety of chimeric dioxygenases constructed from two biphenyl dioxygenases that are similar structurally but different functionally. J. Bacteriol. 179:3936-3943.
41 - Kosono, S., M. Maeda, F. Fuji, H. Arai, and T. Kudo. 1997. Three of the seven bphC genes of Rhodococcus erythropolis TA421, isolated from a termite ecosystem, are located on an indigenous plasmid associated with biphenyl degradation. Appl. Environ. Microbiol. 63:3282-3285.[Abstract]
42 - Kumamaru, T., H. Suenaga, M. Mitsuoka, T. Watanabe, and K. Furukawa. 1998. Enhanced degradation of polychlorinated biphenyls by directed evolution of biphenyl dioxygenase. Nat. Biotechnol. 16:663-666.[CrossRef][Medline]
43 - Labbe, D., J. Garnon, and P. C. Lau. 1997. Characterization of the genes encoding a receptor-like histidine kinase and a cognate response regulator from a biphenyl/polychlorobiphenyl-degrading bacterium, Rhodococcus sp. strain M5. J. Bacteriol. 179:2772-2776.[Abstract/Free Full Text]
44 - Lau, P. C., J. Garnon, D. Labbe, and Y. Wang. 1996. Location and sequence analysis of a 2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoate hydrolase-encoding gene (bpdF) of the biphenyl/polychlorinated biphenyl degradation pathway in Rhodococcus sp. M5. Gene 171:53-57.
45 - Lloyd-Jones, G., C. De Jong, R. C. Ogden, W. A. Duetz, and P. A. Williams. 1994. Recombination of the bph (biphenyl) genes from pWW100 and their deletion during growth on benzoate. Appl. Environ. Microbiol. 60:691-696.[Abstract/Free Full Text]
46 - Maeda, T., Y. Takahashi, H. Suenaga, A. Suyama, M. Goto, and K. Furukawa. 2001. Functional analyses of Bph-Tod hybrid dioxygenase, which exhibits high degradation activity toward trichloroethylene. J. Biol. Chem. 276:29833-29838.[Abstract/Free Full Text]
47 - Masai, E., K. Sugiyama, N. Iwashita, S. Shimizu, J. E. Hauschild, T. Hatta, K. Kimbara, K. Yano, and M. Fukuda. 1997. The bphDEF meta-cleavage pathway genes involved in biphenyl/polychlorinated biphenyl degradation are located on a linear plasmid and separated from the initial bphACB genes in Rhodococcus sp. strain RHA1. Gene 187:141-149.[CrossRef][Medline]
48 - Masai, E., A. Yamada, J. M. Healy, T. Hatta, K. Kimbara, M. Fukuda, and K. Yano. 1995. Characterization of biphenyl catabolic genes of gram-positive polychlorinated biphenyl degrader Rhodococcus sp. strain RHA1. Appl. Environ. Microbiol. 61:2079-2085.[Abstract]
49 - Mason, J. R., and R. Cammack. 1992. The electron-transport proteins of hydroxylating bacterial dioxygenases. Annu. Rev. Microbiol. 46:277-305.[CrossRef][Medline]
50 - McKay, D. B., M. Seeger, M. Zielinski, B. Hofer, and K. N. Timmis. 1997. Heterologous expression of biphenyl dioxygenase-encoding genes from a gram-positive broad-spectrum polychlorinated biphenyl degrader and characterization of chlorobiphenyl oxidation by the gene products. J. Bacteriol. 179:1924-1930.[Abstract/Free Full Text]
51 - Merlin, C., D. Springael, M. Mergeay, and A. Toussaint. 1997. Organisation of the bph gene cluster of transposon Tn4371, encoding enzymes for the degradation of biphenyl and 4-chlorobiphenyl compounds. Mol. Gen. Genet. 253:499-506.[CrossRef][Medline]
52 - Merlin, C., D. Springael, and A. Toussaint. 1999. Tn4371: a modular structure encoding a phage-like integrase, a Pseudomonas-like catabolic pathway, and RP4/Ti-like transfer functions. Plasmid 41:40-54.[CrossRef][Medline]
53 - Misawa, N., K. Shindo, H. Takahashi, H. Suenaga, K. Iguchi, H. Okazaki, S. Harayama, and K. Furukawa. 2002. Hydroxylation of various molecules including heterocyclic aromatics using recombinant Escherichia coli cells expressing modified biphenyl dioxygenase genes. Tetrahedron 58:9605-9612.[CrossRef]
54 - Mondello, F. J. 1989. Cloning and expression in Escherichia coli of Pseudomonas strain LB400 genes encoding polychlorinated biphenyl degradation. J. Bacteriol. 171:1725-1732.[Abstract/Free Full Text]
55 - Mondello, F. J., M. P. Turcich, J. H. Lobos, and B. D. Erickson. 1997. Identification and modification of biphenyl dioxygenase sequences that determine the specificity of polychlorinated biphenyl degradation. Appl. Environ. Microbiol. 63:3096-3103.[Abstract]
56 - Mouz, S., C. Merlin, D. Springael, and A. Toussaint. 1999. A GntR-like negative regulator of the biphenyl degradation genes of the transposon Tn4371. Mol. Gen. Genet. 262:790-799.[CrossRef][Medline]
57 - Nagarajan, V., N. Sakurai, M. Kubota, T. Nonaka, H. Nagumo, H. Takeda, T. Nishizaki, E. Masai, M. Fukuda, Y. Mitsui, and T. Senda. 2003. Crystallization of the terminal oxygenase component of biphenyl dioxygenase derived from Rhodococcus sp. strain RHA1. Protein Pept. Lett. 10:412-417.[CrossRef][Medline]
58 - Neidle, E. L., C. Hartnett, L. N. Ornston, A. Bairoch, M. Rekik, and S. Harayama. 1991. Nucleotide sequence of the Acinetobacter calcoaceticus benABC genes for benzoate 1,2-dioxygenase reveal evolutionary relationships among multicomponent oxygenases. J. Bacteriol. 173:5385-5395.[Abstract/Free Full Text]
59 - Nishi, A., K. Tominaga, and K. Furukawa. 2000. A 90-kilobase conjugative chromosomal element coding for biphenyl and salicylate catabolism in Pseudomonas putida KF715. J. Bacteriol. 182:1949-1955.[Abstract/Free Full Text]
60 - Ohtsubo, Y., M. Delawary, K. Kimbara, M. Takagi, A. Ohta, and Y. Nagata. 2001. BphS, a key transcriptional regulator of bph genes involved in PCB/biphenyl degradation in Pseudomonas sp. KKS102. J. Biol. Chem. 276:36146-36154.[Abstract/Free Full Text]
61 - Ohtsubo, Y., Y. Nagata, K. Kimbara, M. Takagi, and A. Ohta. 2000. Expression of the bph genes involved in biphenyl/PCB degradation in Pseudomonas sp. KKS102 induced by the biphenyl degradation intermediate, 2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoic acid. Gene 256:223-228.[CrossRef][Medline]
62 - Peloquin, L., and C. W. Greer. 1993. Cloning and expression of the polychlorinated biphenyl-degradation gene cluster from Arthrobacter M5 and comparison to analogous genes from gram-negative bacteria. Gene 125:35-40.[CrossRef][Medline]
63 - Sakai, M., E. Masai, H. Asami, K. Sugiyama, K. Kimbara, and M. Fukuda. 2002. Diversity of 2,3-dihydroxybiphenyl dioxygenase genes in a strong PCB degrader, Rhodococcus sp. strain RHA1. J. Biosci. Bioeng. 93:421-427.
64 - Sakai, M., K. Miyauchi, N. Kato, E. Masai, and M. Fukuda. 2003. 2-Hydroxypenta-2,4-dienoate metabolic pathway genes in a strong polychlorinated biphenyl degrader, Rhodococcus sp. strain RHA1. Appl. Environ. Microbiol. 69:427-433.[Abstract/Free Full Text]
65 - Sayler, G. S., H. L. Kong, and M. S. Shields. 1984. Plasmid-mediated biodegradative fate of monohalogenated biphenyls in facultatively anaerobic sediments. Basic Life Sci. 28:117-135.[Medline]
66 - Schell, N. A. 1993. Molecular biology of the LysR family of transcriptional regulators. Annu. Rev. Microbiol. 47:597-626.[CrossRef][Medline]
67 - Seeger, M., B. Camara, and B. Hofer. 2001. Dehalogenation, denitration, dehydroxylation, and angular attack on substituted biphenyls and related compounds by a biphenyl dioxygenase. J. Bacteriol. 183:3548-3555.[Abstract/Free Full Text]
68 - Seeger, M., K. N. Timmis, and B. Hofer. 1995. Conversion of chlorobiphenyls into phenylhexadienoates and benzoates by the enzymes of the upper pathway for polychlorobiphenyl degradation encoded by the bph locus of Pseudomonas sp. strain LB400. Appl. Environ. Microbiol. 61:2654-2658.[Abstract]
69 - Senda, T., T. Yamada, N. Sakurai, M. Kubota, T. Nishizaki, E. Masai, M. Fukuda, and Y. Mitsui. 2000. Crystal structure of NADH-dependent ferredoxin reductase component in biphenyl dioxygenase. J. Mol. Biol. 304:397-410.[CrossRef][Medline]
70 - Shao, Z., H. Zhao, L. Giver, and F. H. Arnold. 1998. Random-priming in vitro recombination: an effective tool for directed evolution. Nucleic Acids Res. 26:681-683.[Abstract/Free Full Text]
71 - Shimizu, S., H. Kobayashi, E. Masai, and M. Fukuda. 2001. Characterization of the 450-kb linear plasmid in a polychlorinated biphenyl degrader, Rhodococcus sp. strain RHA1. Appl. Environ. Microbiol. 67:2021-2028.[Abstract/Free Full Text]
72 - Shindo, K., R. Nakamura, I. Chinda, Y. Ohnishi, S. Horinouchi, H. Takahashi, K. Iguchi, S. Harayama, K. Furukawa, and N. Misawa. 2003. Hydroxylation of ionized aromatics including carboxylic acid or amine using recombinant Streptomyces lividans cells expressing modified biphenyl dioxygenase genes. Tetrahedron 59:1895-1900.[CrossRef]
73 - Springael, D., S. Kreps, and M. Mergeay. 1993. Identification of a catabolic transposon, Tn4371, carrying biphenyl and 4-chlorobiphenyl degradation genes in Alcaligenes eutrophus A5. J. Bacteriol. 175:1674-1681.[Abstract/Free Full Text]
74 - Stemmer, W. P. C. 1994. Rapid evolution of a protein in vitro by DNA shuffling. Nature 370:389-391.[CrossRef][Medline]
75 - Suenaga, H., M. Goto, and K. Furukawa. 2001. Emergence of multifunctional oxygenase activities by random priming recombination. J. Biol. Chem. 276:22500-22506.[Abstract/Free Full Text]
76 - Suenaga, H., M. Mitsuoka, Y. Ura, T. Watanabe, and K. Furukawa. 2001. Directed evolution of biphenyl dioxygenase: emergence of enhanced degradation capacity for benzene, toluene, and alkylbenzene. J. Bacteriol. 183:5441-5444.[Abstract/Free Full Text]
77 - Suenaga, H., T. Watanabe, M. Sato, Ngadiman, and K. Furukawa. 2002. Alteration of regiospecificity in biphenyl dioxygenase by active-site engineering. J. Bacteriol. 184:3682-3688.[Abstract/Free Full Text]
78 - Sylvestre, M., M. Sirois, Y. Hurtubise, J. Bergeron, D. Ahmad, F. Shareck, D. Barriault, I. Guillemette, and J. M. Juteau. 1996. Sequencing of Comamonas testosteroni strain B-356-biphenyl/chlorobiphenyl dioxygenase genes: evolutionary relationships among gram-negative bacterial biphenyl dioxygenases. Gene 174:195-202.[CrossRef][Medline]
79 - Taira, K., J. Hirose, S. Hayashida, and K. Furukawa. 1992. Analysis of bph operon from the polychlorinated biphenyl-degrading strain of Pseudomonas pseudoalcaligenes KF707. J. Biol. Chem. 267:4844-4853.[Abstract/Free Full Text]
80 - Takeda, H., A. Yamada, K. Miyauchi, E. Masai, and M. Fukuda. 2004. Characterization of transcriptional regulatory genes for biphenyl degradation in Rhodococcus sp. strain RHA1. J. Bacteriol. 186:2134-2146.[Abstract/Free Full Text]
81 - Unterman, R. 1996. A history of PCB biodegradation, p. 209-253. In R. L. Crawford and D. L. Crawford (ed.), Bioremediation: principles and applications. Cambridge University Press, New York, N.Y.
82 - Wang, Y., J. Garnon, D. Labbe, H. Bergeron, and P. C. Lau. 1995. Sequence and expression of the bpdC1C2BADE genes involved in the initial steps of biphenyl/chlorobiphenyl degradation by Rhodococcus sp. M5. Gene 164:117-122.
83 - Watanabe, T., H. Fujihara, and K. Furukawa. 2003. Characterization of the second LysR-type regulator in the biphenyl-catabolic gene cluster of Pseudomonas pseudoalcaligenes KF707. J. Bacteriol. 185:3575-3582.[Abstract/Free Full Text]
84 - Watanabe, T., R. Inoue, N. Kimura, and K. Furukawa. 2000. Versatile transcription of biphenyl catabolic bph operon in Pseudomonas pseudoalcaligenes KF707. J. Biol. Chem. 275:31016-31023.[Abstract/Free Full Text]
85 - Yamada, A., H. Kishi, K. Sugiyama, T. Hatta, K. Nakamura, E. Masai, and M. Fukuda. 1998. Two nearly identical aromatic compound hydrolase genes in a strong polychlorinated biphenyl degrader, Rhodococcus sp. strain RHA1. Appl. Environ. Microbiol. 64:2006-2012.[Abstract/Free Full Text]
Journal of Bacteriology, August 2004, p. 5189-5196, Vol. 186, No. 16
0021-9193/04/$08.00+0 DOI: 10.1128/JB.186.16.5189-5196.2004
Copyright © 2004, American Society for Microbiology. All Rights Reserved.
This article has been cited by other articles:
-
Uhlik, O., Jecna, K., Mackova, M., Vlcek, C., Hroudova, M., Demnerova, K., Paces, V., Macek, T.
(2009). Biphenyl-Metabolizing Bacteria in the Rhizosphere of Horseradish and Bulk Soil Contaminated by Polychlorinated Biphenyls as Revealed by Stable Isotope Probing. Appl. Environ. Microbiol.
75: 6471-6477
[Abstract]
[Full Text]
-
Sul, W. J., Park, J., Quensen, J. F. III, Rodrigues, J. L. M., Seliger, L., Tsoi, T. V., Zylstra, G. J., Tiedje, J. M.
(2009). DNA-Stable Isotope Probing Integrated with Metagenomics for Retrieval of Biphenyl Dioxygenase Genes from Polychlorinated Biphenyl-Contaminated River Sediment. Appl. Environ. Microbiol.
75: 5501-5506
[Abstract]
[Full Text]
-
Shin, K. A., Spain, J. C.
(2009). Pathway and Evolutionary Implications of Diphenylamine Biodegradation by Burkholderia sp. Strain JS667. Appl. Environ. Microbiol.
75: 2694-2704
[Abstract]
[Full Text]
-
Camara, B., Seeger, M., Gonzalez, M., Standfuss-Gabisch, C., Kahl, S., Hofer, B.
(2007). Generation by a Widely Applicable Approach of a Hybrid Dioxygenase Showing Improved Oxidation of Polychlorobiphenyls. Appl. Environ. Microbiol.
73: 2682-2689
[Abstract]
[Full Text]
-
Vezina, J., Barriault, D., Sylvestre, M.
(2007). Family Shuffling of Soil DNA To Change the Regiospecificity of Burkholderia xenovorans LB400 Biphenyl Dioxygenase. J. Bacteriol.
189: 779-788
[Abstract]
[Full Text]
-
Ferraro, D. J., Okerlund, A. L., Mowers, J. C., Ramaswamy, S.
(2006). Structural basis for regioselectivity and stereoselectivity of product formation by naphthalene 1,2-dioxygenase.. J. Bacteriol.
188: 6986-6994
[Abstract]
[Full Text]
-
Fujihara, H., Yoshida, H., Matsunaga, T., Goto, M., Furukawa, K.
(2006). Cross-Regulation of Biphenyl- and Salicylate-Catabolic Genes by Two Regulatory Systems in Pseudomonas pseudoalcaligenes KF707. J. Bacteriol.
188: 4690-4697
[Abstract]
[Full Text]
-
Witzig, R., Junca, H., Hecht, H.-J., Pieper, D. H.
(2006). Assessment of Toluene/Biphenyl Dioxygenase Gene Diversity in Benzene-Polluted Soils: Links between Benzene Biodegradation and Genes Similar to Those Encoding Isopropylbenzene Dioxygenases.. Appl. Environ. Microbiol.
72: 3504-3514
[Abstract]
[Full Text]
-
Fortin, P. D., MacPherson, I., Neau, D. B., Bolin, J. T., Eltis, L. D.
(2005). Directed Evolution of a Ring-cleaving Dioxygenase for Polychlorinated Biphenyl Degradation. J. Biol. Chem.
280: 42307-42314
[Abstract]
[Full Text]
-
Suenaga, H., Liu, R., Shiramasa, Y., Kanagawa, T.
(2005). Novel Approach to Quantitative Detection of Specific rRNA in a Microbial Community, Using Catalytic DNA. Appl. Environ. Microbiol.
71: 4879-4884
[Abstract]
[Full Text]
-
Patrauchan, M. A., Florizone, C., Dosanjh, M., Mohn, W. W., Davies, J., Eltis, L. D.
(2005). Catabolism of Benzoate and Phthalate in Rhodococcus sp. Strain RHA1: Redundancies and Convergence. J. Bacteriol.
187: 4050-4063
[Abstract]
[Full Text]
-
Fortin, P. D., Lo, A. T.-F., Haro, M.-A., Kaschabek, S. R., Reineke, W., Eltis, L. D.
(2005). Evolutionarily Divergent Extradiol Dioxygenases Possess Higher Specificities for Polychlorinated Biphenyl Metabolites. J. Bacteriol.
187: 415-421
[Abstract]
[Full Text]