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R E S E A R C H L E T T E R
Enzyme^substrate interactionand characterizationofa2,3-dihydroxybiphenyl1,2-dioxygenasefromDyellaginsengisoli LA-4Ang Li1, Yuanyuan Qu1, Jiti Zhou1 & Fang Ma2
1Key Laboratory of Industrial Ecology and Environmental Engineering, School of Environmental and Biological Science and Technology, MOE, Dalian
University of Technology, Dalian, China; and 2School of Municipal and Environmental Engineering, Harbin Institute of Technology, Harbin, China
Correspondence: Yuanyuan Qu, Key
Laboratory of Industrial Ecology and
Environmental Engineering, School of
Environmental and Biological Science and
Technology, MOE, Dalian University of
Technology, Dalian 116024, China.
Tel.: 186 411 8470 6251; fax: 186 411 8470
6252; e-mail: [email protected]
Received 9 July 2008; accepted 16 December
2008.
First published online 29 January 2009.
DOI:10.1111/j.1574-6968.2009.01487.x
Editor: Hans-Peter Kohler
Keywords
Dyella ginsengisoli ; 2,3-dihydroxybiphenyl
1,2-dioxygenase; kinetic parameters;
enzyme–substrate complex.
Abstract
A bphC gene (915 bp) encoding 2,3-dihydroxybiphenyl 1,2-dioxygenase (BphC)
was amplified by PCR from Dyella ginsengisoli LA-4, which was heterologously
expressed in Escherichia coli. The purified His-Tag BphC was able to catalyze
the meta-cleavage reaction of the dihydroxylated aromatic rings. According to
the specificity constant (Kcat/Km) of BphC_LA-4, the specificity of BphC_LA-4
was determined in the following order: 2,3-dihydroxybiphenyl4 3-methyl-
catechol4 catechol4 4-chlorocatechol4 4-methylcatechol. The experimental
data were consistent with the prediction of enzyme–substrate complexes.
The highest specific activity of BphC_LA-4 was 118.3 U mg�1 for 2,3-dihydrox-
ybiphenyl.
Introduction
Polychlorinated biphenyls (PCBs) have been of public and
scientific concern for several decades because of their
persistence in the environment, their bioaccumulation and
their potential carcinogenicity (McKay et al., 2003). Nowa-
days, a number of PCB-degrading microorganisms have
been isolated and characterized, and the major biodegrada-
tion pathway of biphenyl has been reported (Furukawa et al.,
2004; Pieper, 2005). Most biphenyl-degrading bacteria can
metabolize biphenyl to benzoate and 2-hydroxy-penta-2,4-
dienoate via the so-called upper pathway, which consists of
four enzymes: biphenyl 2,3-dioxygenase (BphA), dihydro-
diol dehydrogenase (BphB), 2,3-dihydroxybiphenyl dioxy-
genase (BphC) and 2-hydroxyl-6-oxo-6-phenylhexa-2,4-
dienoic acid hydrolase (BphD).
Among the enzymes mentioned above, BphCs catalyze
the meta-cleavage reaction of 2,3-dihydroxybiphenyl, which
belongs to a class of extradiol dioxygenases (Eltis & Bolin,
1996). Ring cleavage is an important step during the
degradation of aromatic compounds including biphenyl.
These extradiol dioxygenases can catalyze the meta-cleavage
of the dihydroxylated aromatic rings; therefore, they play a
key role in biphenyl mineralization or biodegradation of
other aromatic compounds (Vaillancourt et al., 2002a, b; Lee
et al., 2003).
Up to now, many bphC genes have been cloned and
heterologously expressed in the metabolic pathways for
biphenyl/PCBs (Eltis & Bolin, 1996; Kim et al., 1996; Hatta
et al., 2003; Lee et al., 2003; McKay et al., 2003). Most reports
on BphCs mainly focused on functional characterization, but
research on structural properties has been limited, especially
on the enzyme–substrate complexes (Han et al., 1995; Senda
et al., 1996). Recently, the complete 12.1-kb bph gene cluster
(GenBank accession no. EU258607) was amplified from
strain LA-4 by the genome walking method. The deduced
amino acid sequence of BphC_LA-4 shared the highest
similarity with BphC of Burkholderia xenovorans LB400 with
only 74% identity. This is the first report that the bphC gene
is amplified from the genus Dyella and expressed in
FEMS Microbiol Lett 292 (2009) 231–239 c� 2009 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
Escherichia coli. Meanwhile, the specificity of BphC_LA-4 for
dihydroxylated substrates was predicted according to the
enzyme–substrate complexes. Also, the characterization of
purified BphC_LA-4 was investigated in detail.
Materials and methods
Bacterial strains, plasmids and growthconditions
A novel biphenyl-degrading bacterium, Dyella ginsengisoli LA-
4, was grown at 30 1C on defined basal salts medium (Qu
et al., 2005) containing 0.5 g L�1 biphenyl and 2 g L�1 bacto-
tryptone. Escherichia coli JM109 (TaKaRa, Dalian, China) and
E. coli BL21 (DE3) (Novagen) were used for plasmid con-
struction and gene expression, respectively. Escherichia coli
were grown on Luria–Bertani (LB) media at 37 1C with
100mg mL�1 ampicillin or 30mg mL�1 kanamycin. The plas-
mids used in this study were pMD18-T simple vector (cloning
vector, Ampr) and pET28(a) (expression vector, Kmr).
Construction of plasmids and overexpression
DNA was manipulated using standard protocols (Ausubel
et al., 2000). Genome DNA was extracted from strain LA-4
using a Bacterial Genomic DNA Extraction Kit (TaKaRa).
According to the ORF of bphC gene (EU258607), the
primers were designated: bphC-F, 50-GAATTCATGAGCGT
CAAGAACTTGGG-30; bphC-R, 50-AAGCTTTCATGCGG
TCTCTCTTGTAG-30, where the EcoRI and HindIII sites are
underlined, respectively. The entire bphC gene was amplified
by PCR using PrimeSTAR HS DNA Polymerase (TaKaRa).
The PCR was run for 30 cycles with an annealing tempera-
ture of 55 1C. The PCR product was ligated into pMD18-T
simple vector before sequencing. DNA sequence was deter-
mined by TaKaRa Biotechnology. Then the gene was sub-
cloned into the pET28(a) vector, yielding pET-bphC.
Subsequently, the resulting plasmids (pET-bphC) were in-
troduced into E. coli BL21 (DE3) for overexpression.
For overexpression, E. coli BL21 (DE3) harboring pET-
bphC was cultured in 3 mL LB medium containing
30mg mL�1 kanamycin at 37 1C for 8 h, and then 100mL
was inoculated into 100 mL LB with 30mg mL�1 kanamycin.
After cells were allowed to grow at 37 1C to an OD600 nm of
0.6, the cultures were induced with 1 mM IPTG and
reincubated at 37 1C for 3 h. Escherichia coli was harvested
by centrifugation at 9820 g for 5 min, and then washed twice
with cold 20 mM sodium phosphate buffer (pH 7.4). Finally,
the pellets were frozen at � 80 1C until use.
Sequence analysis and molecular modeling
Sequence analysis, database searches and sequence compar-
ison were performed using the programs from NCBI. Amino
acid sequences of BphCs were aligned using CLUSTAL W, and
the aligned sequences were used to construct a phylogenetic
tree using the neighbor-joining method (Saitou & Nei,
1987).
The automated protein structure homology-modeling
server, SWISS-MODEL, was used to generate the three-dimen-
sional (3D) model (Schwede et al., 2003). In addition,
PYMOL (version 0.99; DeLano Scientific, San Carlos, CA)
was used to view the graphic. The enzyme–substrate com-
plexes were generated by superposition using DEEPVIEW, and
the substrates used in this study were drawn from the
template model [Protein Data Bank (PDB) code 1kndA,
BphC_LB400 complexed with catechol] to replace catechol.
Preparation of the crude extracts
Escherichia coli (pET-bphC) was suspended in 20 mM so-
dium phosphate buffer (pH 7.4) and lysed by freezing and
thawing followed by sonication (225 W at 4 1C for 30 min,
Ultrasonic processor CPX 750). After centrifugation
(58 545 g, 20 min, 4 1C), the supernatants were used as the
crude extracts.
Purification of His-Tag BphC
Protein was purified at room temperature by AKTA Explorer
100 (Amersham Biosciences, Montreal, QC, Canada). The
crude extracts were loaded onto a HisTrap FF crude column
(1 mL, Amersham Biosciences) equilibrated with buffer A
(20 mM sodium phosphate, 500 mM NaCl, 20 mM imida-
zole, pH 7.4). The column was operated at the flow rate of
1.0 mL min�1, and the enzyme was eluted with a 20-mL
linear gradient from 0% to 100% buffer B (20 mM sodium
phosphate, 500 mM NaCl, 500 mM imidazole, pH 7.4).
Active fractions were applied to a Hitrip Desalting column
(Amersham Biosciences) with buffer C (50 mM Tris-HCl,
pH 8.0) for desalting. Finally, the purified BphC was
obtained and concentrated to about 0.6 mg mL�1.
Purified enzymes were analysed by sodium dodecyl
sulfate-polyacrylamide gel electrophoresis (SDS-PAGE) as
described by Laemmli (1970). The acrylamide concentra-
tions for the concentrating and separating gels were 5% and
15%, respectively. The gel was stained with Coomassie
brilliant blue R250. Protein concentrations were determined
using the Bradford (1976) method.
Determination of enzyme activity with thepurified enzyme
2,3-Dihydroxybiphenyl 1,2-dioxygenase activity was mea-
sured by monitoring the reaction products HOPDA at
434 nm with a scanning spectrophotometer (V-560, JASCO,
Tokyo, Japan). Activity assays were performed in 50 mM
Tris-HCl (pH 8.0) containing 125mM 2,3-dihydroxybiphenyl
FEMS Microbiol Lett 292 (2009) 231–239c� 2009 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
232 A. Li et al.
at 20 1C. The total volume of the reaction mixture was
2.0 mL. One unit of enzyme activity was defined as the
amount of enzyme that catalyzed the formation of 1 mmol of
product per minute at 20 1C. The molar extinction coeffi-
cient of the product was e434 = 17.9 cm�1 mM�1 at pH 8.0
(Eltis et al., 1993). Specific activities were expressed as
micromoles of product formed per minute per milligram of
protein at 20 1C. The other substrates used in this study had
the following ring fission product absorbances and molar
extinction coefficients at pH 8.0: catechol, e375 = 67.8 cm�1
mM�1; 4-chlorocatechol, e379 = 40 cm�1 mM�1; 3-methylca-
techol, e388 = 73.6 cm�1 mM�1; 4-methylcatechol, e382 =
73.9 cm�1 mM�1 (Eltis et al., 1993; Hatta et al., 2003).
Apparent kinetic parameters were determined at substrate
ranges from 50 to 500 mM 2,3-dihyroxybiphenyl, 125 to
600 mM catechol, 125 to 500 mM 3-methylcatechol and 4-
methylcatechol, and 25 to 175mM 4-chlorocatechol. Kinetic
data were calculated from the initial velocities with the
Michaelis–Menten equation by ORIGIN 7.5. All the experi-
ments were carried out at least three times.
Effects of pH and temperature on enzymeactivity
The optimal pH of enzymatic cleavage was determined at
different pH values ranging from 6.0 to 9.0 using 50 mM
K2HPO4/NaOH buffer (pH 6.0–7.0) and Tris-HCl buffer
(pH 7.0–9.0). The molar extinction coefficients of the
products were: e434 = 8.0 cm�1 mM�1 at pH 7.0;
e434 = 13.2 cm�1 mM�1 at pH 7.5; e434 = 17.9 cm�1 mM�1 at
pH 8.0; e434 = 20.6 cm�1 mM�1 at pH 8.5; e434 =
22.0 cm�1 mM�1 at pH 9.0 (Eltis et al., 1993). The optimal
temperature for the enzyme activity was determined by
measuring the reactions at different temperatures ranging
from 20 to 80 1C.
Effects of metal ions and chemical compoundson enzyme activity
The effects of different metal ions on the enzyme activity
were tested by incubating 12 mg of purified BphC in 50 mM
Tris-HCl buffer (pH 8.0) for 15 min at 20 1C in the presence
of 1 mM different metal ions before initiating the reaction.
The effects of various compounds were investigated by
incubating 12 mg purified BphC with the different concen-
trations of chemical compounds.
Results
Cloning of the bphC gene and sequence analysis
The complete 927 bp EcoRI–HindIII fragment containing
the bphC gene was amplified from strain LA-4 by PCR,
which contained an initiation codon ATG at nucleotides 7–9
and a stop codon at nucleotides 922–927. The deduced
amino acid sequence shared the highest similarity with
BphCs of B. xenovorans LB400 and Pseudomonas pseudoal-
caligenes KF707 (both only 74% identity) (Furukawa et al.,
1987; Hofer et al., 1993). The phylogenetic relationship of
related enzymes is shown in Fig. 1a. The phylogenetic
analysis of the type I extradiol dioxygenases indicated that
they were all derived from the same ancestral origin. The
branch with BphC_LA-4 was obviously distinct from other
known BphCs.
Comparing the amino acid sequences of BphC_LA-4,
BphC_KKS102 and BphC_LB400 (Fig. 1b), it was suggested
that BphC_LA-4 was divided into two domains, N-terminal
(residues 1–134) and C-terminal (residues 135–304) (Eltis &
Bolin, 1996; Senda et al., 1996). According to previous
reports, the BphC_LA-4 was a two-domain type I extradiol
dioxygenase in which the C-terminal domain binds iron (II)
and was catalytically active (Lee et al., 2003; Vaillancourt
et al., 2006). Eltis & Bolin (1996) found a fingerprint region
and nine strictly conserved residues by aligning 23 extradiol
dioxygenases. Therefore, the fingerprint region spanned
residues 238–259 in the BphC_LA-4 sequence with the
pattern (GRHSNDHMVSFYAVTPSGFDVE). Three of the
strictly conserved residues, His-145, His-209 and Glu-259 in
BphC_LA-4, were the metal ligands. Three additional active
site residues, His-194, His-240 and Tyr-249, were also
strictly conserved in BphC_LA-4, which played potential
catalytic roles. The other conserved residues, Gly-28, Leu-
164 and Pro-253, played structural or folding roles in
BphC_LA-4.
Structural prediction and modeling
The 3D structure of BphC_LB400 was used as a template to
generate the BphC_LA-4 model. As shown in Fig. 2a, the
modeled structure of BphC_LA-4 suggested that the N- and
C-terminal domains were structurally similar, and each
domain of BphC_LA-4 contained two repetitions of the
babbb motif. Comparing the 3D structures between the
constructed model and the template model, the relative
mean square deviation of C-a on superposition was 3.0 A.
This suggested that the constructed model of BphC_LA-4
was reliable with a perfect quality.
In BphC_KKS102, three less well-conserved residues, Ile-
174, Phe-201 and Thr-280, interacted with the benzene ring
moiety of 2,3-dihydroxybiphenyl, which determined varied
substrate specificities among the related enzymes (Senda
et al., 1996). Comparing the amino acid sequences and 3D
structures of BphC_LA-4 and BphC_KKS102 (PDB code
1kw9), only Thr-280 was replaced by Ile-279 in BphC_LA-4,
as shown in Figs 1b and 2b.
To investigate the specificity of BphC_LA-4, the enzy-
me–substrate complexes were constructed (Fig. 3). As in
FEMS Microbiol Lett 292 (2009) 231–239 c� 2009 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
233Enzyme–substrate complexes and characterization of BphC_LA-4
Vaillancourt’s report (Vaillancourt et al., 2005), the active
site of BphC was poorly complementary to catechol because
the volume in the active site occupied by the second ring of
biphenyl was excess ‘free’ volume when catechol binds.
Therefore, the specificity of BphC for bicyclic substrate was
higher than that for monocyclic substrate. According to the
enzyme–substrate complexes (Fig. 3a–e), the volume of the
second ring of biphenyl was completely free in the cate-
chol:BphC complex, but the volume was partially occupied
by the methyl group of 3-methylcatechol. The chlorine
substitution or methyl group at position C4 of catechol
could partially occupy the free volume, but the residue Ile-
279 was close to these substitutions. This indicated that the
substitution at position C4 was sterically hindered because
of lack of space to accommodate the chlorine atom or
methyl group. The specificity of BphC_LA-4 for 4-methyl-
catechol should be lower than that for 4-chlorocatechol
because the methyl group occupied a larger space than the
chlorine atom. The prediction of specificity for BphC_LA-4
was in the following order: 2,3-dihydroxybiphenyl43-methylcatechol4 catechol4 4-chlorocatechol4 4-methyl-
catechol.
Purification and characterization of BphC_LA-4
The His-Tag BphC in E. coli BL21 (pET-bphC) was purified
at room temperature using an AKTA Explorer. The protein
was estimated to be 4 95% pure by SDS-PAGE. The
subunit molecular mass is shown in Fig. 4. The result was
Fig. 2. 3D structure of BphC_LA-4 constructed
with SWISS-MODEL (a) and a superposition of
BphC_LA-4 active site structure with that of
BphC_KKS102. (b) BphC_LA-4 and
BphC_KKS102 are shown in green and purple,
respectively.
(b)(a)
BphC LB400
BphC KF707
BphC Cam-1
BphC OU83
BphC KF715
BphC B-356
BphC SMN4
BphC KKS102
BphC TK102
BphC LA-4
BphC RHA1
TodE DOT-T1
Edo2 RW1
BphC R04
BphC B1
NahC pPG7
XylE pWW0
100
86100
55
99
66
95
99
92
100
889782
0.00.20.40.60.8
Fig. 1. Sequence analysis of BphC_LA-4. (a) Phylogenetic relationships of type I extradiol dioxygenases. Sequences used were as follows: Pseudomonas
sp. KKS102 (M26433); Dyella sp. LA-4 (EU258607); Rhodococcus sp. R04 (DQ403247); Sphingobium sp. B1 (EF151283); Pseudomonas sp. OU83
(X91876); Rhodococcus sp. RHA1 (D32142); Comamonas sp. TK102 (AB086835); Comamonas sp. B-356 (U91936); Pseudomonas sp. Cam-1
(AY027651); Burkholderia sp. LB400 (X66122); Pseudomonas sp. KF715 (M33813); Pseudomonas sp. KF707 (M83673); Delftia sp. SMN4 (AY028943);
Pseudomonas sp. pWW0 (M64747); TodE Pseudomonas sp. DOT-T1 (Y18245); Sphingomonas sp. RW1 (AJ223219). (b) Comparison of amino acid
sequences of BphC_LA-4 with BphC_KKS102 and BphC_LB400. �Residues binding the Fe ion. #Residues that play potential catalytic roles. $Residues
that play structural or folding roles. &Residues that interact with the benzene ring moiety of 2,3-dihydroxybiphenyl.
FEMS Microbiol Lett 292 (2009) 231–239c� 2009 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
234 A. Li et al.
identified with the prediction of molecular mass (36.8 kDa)
using the PROTPARAM tool.
The BphC_LA-4 activities for 2,3-dihydroxybiphenyl and
other dihydroxylated substrates were investigated. The spe-
cific activity was 118.3 U mg�1 for 2,3-dihydroxybiphenyl,
which was the best substrate for BphC_LA-4. The optimal
pH for BphC_LA-4 was 8.0, and the enzyme showed its
maximal activity at 40 1C (Fig. 5).
To determine the substrate specificity, the enzyme was
tested for its ability to oxidize 2,3-dihydroxybiphenyl, cate-
chol, 4-chlorocatechol, 3-methylcatechol and 4-methylcate-
chol. The apparent kinetic constants of BphC_LA-4 are
listed in Table 1. The Km for 2,3-dihydroxybiphenyl was the
lowest (18.9mM), and the Km for 4-methylcatechol the
biggest (359.7 mM). The biggest Kcat was for 2,3-dihydrox-
ybiphenyl, and the largest reduction of Kcat was for 4-
methylcatechol. According to the specificity constant (Kcat/
Km) (Table 1), BphC_LA-4 was able to cleave dihydroxylated
substrates in the following order of specificity: 2,3-
dihydroxybiphenyl4 3-methylcatechol4 catechol4 4-
chlorocatechol4 4-methylcatechol. The results agreed with
the prediction of specificity of BphC_LA-4 using enzyme–
substrate complexes.
Effects of metal ions on the enzyme activities
The effects of metal ions on BphC_LA-4 activity are shown
in Fig. 6a. The results indicated that Ca21 and Mg21 were
able to enhance the BphC activities, and Ba21 had no effect
on the activity of BphC_LA-4. However, other metal ions,
especially Cu21, were able to inhibit the activities signifi-
cantly.
Effects of chemical compounds on the enzymeactivities
BphC_LA-4 could be inhibited by various compounds, and
the results are shown in Fig. 6b–d. The enzyme activity of
BphC_LA-4 was completely inhibited when there was
4 25 mM L-ascorbic acid. KI 600 mM reduced the specific
activity of the enzyme by 35%. Meanwhile, it was observed
that 1.25 mM SDS inhibited nearly 60% of BphC_LA-4
activity. The oxidant H2O2 significantly inhibited the en-
zyme activity, and the activity was completely inhibited by
1 mM H2O2 (data not shown). In agreement with previous
reports, it was typical for all iron (II)-dependent extradiol
Fig. 3. Stereo pictures of enzyme–substrate complexes of BphC_LA-4.
(a) 2,3-Dihydroxybiphenyl:BphC complex; (b) catechol:BphC complex; (c)
4-chlorocatechol:BphC complex; (d) 3-methylcatechol:BphC complex;
(e) 4-methylcatechol:BphC complex.
44.3 kDa
29.0 kDa
36 kDa
M 1 2
Fig. 4. SDS-PAGE of purified BphC. Lane M: protein molecular weight
marker (Broad); lane 1: crude cell extracts; lane 2: purified His-Tag BphC.
FEMS Microbiol Lett 292 (2009) 231–239 c� 2009 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
235Enzyme–substrate complexes and characterization of BphC_LA-4
dioxygenases that the enzyme activities were completely
inhibited in the presence of over 1 mM H2O2, while manga-
nese-dependent extradiol dioxygenases showed relatively
weak inactivation (Que et al., 1981; Boldt et al., 1995; Hatta
et al., 2003). This demonstrated that BphC_LA-4 is an iron
(II)-dependent extradiol dioxygenase.
Discussion
A bphC gene was amplified by PCR from PCB-degrading
bacteria D. ginsengisoli LA-4. The deduced amino acid
sequence of BphC_LA-4 showed <74% identity with other
known BphC. In the classification of extradiol dioxygenases
based on the phylogenetic relationship, the enzyme be-
longed to a superfamily with the sequences within the same
subfamily exhibiting over 54% identity (Eltis & Bolin, 1996).
Clearly, BphC_LA-4 belonged to the subfamily of BphCs
obtained from gram-negative bacteria such as BphC_LB400
and BphC_KF707, which were type I iron (II)-dependent
extradiol dioxygenases.
The metal ligands and catalytic residues were strictly
conserved in BphC_LA-4. The other residues playing struc-
tural or folding roles in BphC_LA-4 were also strictly
conserved (Eltis & Bolin, 1996). Among these residues, His-
194 took part in a weak hydrogen bond with the hydroxyl
group of the substrate (Uragami et al., 2001). The proto-
nated His-194 could stabilize a negative charge on the O2
molecule located in the hydrophobic O2-binding cavity and
seemed to function as a proton donor (Sato et al., 2002).
The residues interacting with the benzene ring moiety of
2,3-dihydroxybiphenyl, such as Ile-174, Phe-201 and Thr-
280 in BphC_KKS102, determined the substrate specificities
(Senda et al., 1996). However, these residues were less well
conserved among the related enzymes. Comparison of
BphC_LA-4 and BphC_LB400 showed that Ile-174 and Ile-
279 in BphC_LA-4 were replaced by Met and Pro in
BphC_LB400, respectively. But Phe-201 in BphC_LA-4 and
BphC_LB400 were conserved. The Vmax values of
BphC_LB400 for the dihydroxylated substrates were in the
following order: 2,3-dihydroxybiphenyl4 catechol4 3-
methylcatechol; the specific activity for 4-methylcatechol
was too low to be accurately determined (Eltis et al., 1993).
However, the Kcat value of BphC_LA-4 for 3-methylcatechol
was higher than that for catechol, and the kinetic parameters
for 4-methylcatechol could be determined. It was obvious
that the residues Ile-174, Phe-201 and Ile-279 determined
the specificity of BphC_LA-4.
According to previous reports, the structurally character-
ized proteins are limited compared with the number of
known protein sequences (Arnold et al., 2006). Crystal
structures of BphC_LB400 and BphC_KKS102 have been
reported for the substrate-free enzyme as well as for the
enzyme–substrate complexes (Han et al., 1995; Senda et al.,
1996; Vaillancourt et al., 1998; Dai et al., 2002; Sato et al.,
2002; Vaillancourt et al., 2002a b). However, the enzyme–
substrate complexes were mainly focused on only three
dihydroxylated substrates, such as 2,3-dihydroxybiphenyl,
catechol, and 3-methylcatechol. To our knowledge there
have been no reports demonstrating the specificity of BphC
for 4-chlorocatechol or 4-methylcatechol using enzyme–
substrate complexes. Therefore, we constructed a 3D struc-
ture of BphC and enzyme–substrate complexes. Comparing
the 3D structures of BphC_LA-4, BphC_LB400 and
BphC_KKS102, the b-strand between two a-helices was
absent in the second babbb motif of BphC_LA-4 in the N-
terminal domain (Han et al., 1995; Senda et al., 1996).
According to the enzyme–substrate complexes, the volume
in the active site occupied by the second ring of biphenyl
played an important role in the determination of the
specificity of BphC for bicyclic and monocyclic catecholic
substrates (Vaillancourt et al., 2005). As shown in Fig. 3, the
7.0 7.5 8.0 8.5 9.00
102030405060708090
100R
elat
ive
activ
ity (
%)
pH20 30 40 50 60 70 80
60
70
80
90
100
110
120
130
140
Rel
ativ
e ac
tivity
(%
)
Temperature (°C)
(a) (b)
Fig. 5. Effects of pH and temperature on
enzyme activity. (a) pH; (b) temperature.
Table 1. Apparent kinetic parameters of BphC_LA-4
Substrate Km (mM) Kcat (S�1)
Kcat/Km
(10�2 S�1 mM�1)
2,3-Dihydroxybiphenyl 18.9 84.1 445.0
Catechol 281.0 6.7 2.4
4-Chlorocatechol 49.6 1.0 2.0
3-Methylcatechol 68.8 16.0 23.3
4-Methylcatechol 359.7 0.7 0.2
FEMS Microbiol Lett 292 (2009) 231–239c� 2009 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
236 A. Li et al.
volume was free in the enzyme–substrate complexes of
monocyclic catecholic substrates. It was suggested that the
specificity of BphC_LA-4 for bicyclic substrate was higher
than that for monocyclic substrate. Because the methyl group
of 3-methylcatechol partially occupied this free volume, the
specificity for 3-methylcatechol should be higher than that
for catechol. As per Senda’s report, the amino acid residues in
BphC_KKS102, Phe-186 and Thr-280 interacted with posi-
tion C6 of the catechol ring of biphenyl, which corresponded
with position C4 of monocyclic catecholic substrates. The
amino acid residue Phe-186 interacted with the catechol ring
and contributed to the O2-binding pocket, which was well
conserved in known BphCs (Senda et al., 1996; Sato et al.,
2002). This suggested that Phe-186 was important for the
enzymatic activity, but could not determine substrate speci-
ficities. However, Thr-280 was located at the entrance and
interacted with the benzene ring moiety of 2,3-dihydroxybi-
phenyl (Senda et al., 1996), indicating that Thr-280 was very
important for the specificity of BphC_KKS102. In BphC_LA-
4, Thr-280 was replaced with an Ile residue (Fig. 2b). In the
4-chlorocatechol:BphC complex and 4-methylcatechol:BphC
complex, the steric hindrance by Ile-279 played an important
role in the specificity of BphC_LA-4. Furthermore, the
specificity for 4-methylcatechol should be lower than that
for 4-chlorocatechol, because the methyl group was larger
than the chlorine atom. Therefore, we hypothesized that the
specificity of BphC_LA-4 was in the following order:
2,3-dihydroxybiphenyl4 3-methylcatechol4 catechol4 4-
chlorocatechol4 4-methylcatechol.
The purified BphC activities in 2,3-dihydroxybiphenyl
and other dihydroxylated substrates were determined. The
results showed that BphC_LA-4 exhibited higher cleavage
activity for 2,3-dihydroxybiphenyl and 3-methylcatechol.
However, catechol, 4-methylcatechol and 4-chlorocatechol
could be transformed with relatively low activities. The
specific activity for 2,3-dihydroxybiphenyl of BphC_LA-4
was higher than that of BphC_KF707 (87.2 U mg�1), but
lower than that of BphC_LB400 (191 U mg�1) (Furukawa &
Arimura 1987; Eltis et al., 1993). The optimal temperature
for BphC_LA-4 was 40 1C (Fig. 5), which was higher than
for BphC_LB400 and BphC2_P6 (Asturias et al., 1994;
Seeger et al., 1995). To our knowledge, the optimal tempera-
ture for BphC_LA-4 was the highest, with the exception of
BphC_JF8, which was a thermostable manganese-dependent
2,3-dihydroxybiphenyl 1,2-dioxygenase (Hatta et al., 2003).
Because the Km for 2,3-dihydroxybiphenyl was the lowest
among these dihydroxylated substrates, the BphC_LA-4
showed the highest affinity for 2,3-dihydroxybiphenyl, im-
plying a better fit with the bigger substrate. According to the
specificity constant (Kcat/Km) (Table 1), BphC_LA-4 cleaved
dihydroxylated substrates in the same order with the pre-
dicted specificity by enzyme–substrate complexes. The
(d)(c)
(b)(a)
0 5 10 15 20 25 30
0
20
40
60
80
100
Rel
ativ
e ac
tivity
(%
)
L-Ascorbic acid concentration (mM)
0.0 0.2 0.4 0.6 0.8 1.0 1.2 1.4
40
50
60
70
80
90
100
Rel
ativ
e ac
tivity
(%
)
SDS concentration (mM)0 100 200 300 400 500 600
0
20
40
60
80
100
Rel
ativ
e ac
tivity
(%
)
KI concentration (mM)
Fig. 6. Effects of metal ions and inhibitors on
enzyme activity. (a) Effects of metal ions; (b)
effects of L-ascorbic acid; (c) effects of KI; (d)
effects of SDS.
FEMS Microbiol Lett 292 (2009) 231–239 c� 2009 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
237Enzyme–substrate complexes and characterization of BphC_LA-4
specificity of BphC_LA-4 for dihydroxylated substrates was
different with BphC_JF8 and BphC_LB400 (Eltis et al., 1993;
Hatta et al., 2003). Moreover, BphC_LA-4 preferentially
cleaved these substituted catechols in the order 3-sub-
stituted4 4-substituted and 4-Cl4 4-methyl, which sug-
gested that catalysis was affected by steric determinants.
In summary, the bphC gene of strain LA-4 was amplified
and expressed successfully. BphC_LA-4 was an iron (II)-
dependent type I extradiol dioxygenase. This is an effective
way to predict or explain the specificity of BphC using the
enzyme–substrate complexes constructed by the method of
bioinformatics.
Acknowledgement
This work was supported by the National Natural Science
Foundation of China (No. 50608011).
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239Enzyme–substrate complexes and characterization of BphC_LA-4