Previous Article | Next Article 
Applied and Environmental Microbiology, May 2003, p. 2707-2711, Vol. 69, No. 5
0099-2240/03/$08.00+0 DOI: 10.1128/AEM.69.5.2707-2711.2003
Copyright © 2003, American Society for Microbiology. All Rights Reserved.
Characterization of the 4-Hydroxybenzoyl-Coenzyme A Thioesterase from Arthrobacter sp. Strain SU
Zhihao Zhuang,1 Karl-Heinz Gartemann,2 Rudolf Eichenlaub,2 and Debra Dunaway-Mariano1*
Department of Chemistry, University of New Mexico, Albuquerque, New Mexico 87131,1
Department of Microbiology/Gene Technology, University of Bielefeld, 33615 Bielefeld, Germany2
Received 13 December 2002/
Accepted 20 February 2003

ABSTRACT
The
Arthrobacter sp. strain SU 4-chlorobenzoate (4-CBA) dehalogenation
pathway converts 4-CBA to 4-hydroxybenzoate (4-HBA). The pathway
operon contains the genes
fcbA,
fcbB, and
fcbC (A. Schmitz,
K. H. Gartemann, J. Fiedler, E. Grund, and R. Eichenlaub, Appl.
Environ. Microbiol. 58:4068-4071, 1992). Genes
fcbA and
fcbB encode 4-CBA-coenzyme A (CoA) ligase and 4-CBA-CoA dehalogenase,
respectively, whereas the function of
fcbC is not known. We
subcloned
fcbC and expressed it in
Escherichia coli, and we
purified and characterized the FcbC protein. A substrate activity
screen identified benzoyl-CoA thioesters as the most active
substrates. Catalysis of 4-HBA-CoA hydrolysis to 4-HBA and CoA
occurred with a
kcat of 6.7 s
-1 and a
Km of 1.2 µM. The
kcat pH rate profile for 4-HBA-CoA hydrolysis indicated optimal
activity over a pH range of 6 to 10. The amino acid sequence
of the FcbC protein was compared to other sequences contained
in the protein sequence data banks. A large number of sequence
homologues of unknown function were identified. On the other
hand, the 4-HBA-CoA thioesterases isolated from 4-CBA-degrading
Pseudomonas strains did not share significant sequence identity
with the FcbC protein, indicating early divergence of the thioesterase-encoding
genes.

INTRODUCTION
During the last century, large quantities of industrially produced
4-chlorobenzoate (4-CBA) or 4-CBA progenitors (herbicides and
polychlorinated biphenyl pesticides) (
8,
14,
17,
19) have been
released into the environment. A wide variety of 4-CBA-degrading
bacterial strains, which are capable of growth on 4-CBA as the
principal source of carbon, have been isolated from soil (
11,
35). In these bacteria, 4-CBA is first converted to 4-hydroxybenzoate
(4-HBA), which is then further metabolized via the
ortho- or
meta-cleavage pathway (
11).
The 4-CBA dehalogenation pathway of the 4-CBA-degrading bacterium Pseudomonas sp. strain CBS3 (21) was the first to be characterized. The pathway consists of three reaction steps (28) (see Fig. 1) which are catalyzed by the enzymes 4-CBA-coenzyme A (CoA) ligase, 4-CBA-CoA dehalogenase, and 4-HBA-CoA thioesterase. Each of these enzymes has been isolated, and their kinetic properties have been defined (7). The three 4-CBA dehalogenation pathway genes are organized within an operon that is under the regulatory control of 4-CBA. In some 4-CBA-degrading bacteria, the gene cluster is located within the chromosomal DNA (6, 23, 26), whereas in others it is carried on a plasmid (22, 25).
The
Arthrobacter sp. strain SU 4-CBA dehalogenation pathway
operon was isolated on a 3.6-kb DNA fragment derived from a
120-kb plasmid (
27). The DNA fragment was shown to contain six
open reading frames, three of which (
fcbA,
fcbB, and
fcbC) are
transcribed in the same direction. Truncation mutants lacking
fcbA or
fcbB were unable to dehalogenate 4-CBA, whereas the
truncation mutant devoid of
fcbC was 10-fold less active. The
fcbA gene encoded a 57-kDa protein that shares 38% sequence
identity with the 57-kDa 4-CBA-CoA ligase of the
Pseudomonas sp. strain CBS3 4-CBA dehalogenation pathway. The
fcbB gene
encoded a 30-kDa protein that shares 50% sequence identity with
the 30-kDa 4-CBA-CoA dehalogenase of the
Pseudomonas sp. strain
CBS3 4-CBA dehalogenation pathway. The
fcbA and
fcbB genes were
thus assumed to encode 4-CBA-CoA ligase and 4-CBA-CoA dehalogenase
(
27). The neighboring gene,
fcbC, encoded a 16-kDa protein that
did not share a significant level of sequence homology with
the known 16-kDa
Pseudomonas sp. strain CBS3 4-HBA-CoA thioesterase.
The lack of sequence homology between the
Pseudomonas thioesterase
and the putative
Arthrobacter thioesterase, as well as the different
gene order observed in the
Pseudomonas (dehalogenase-ligase-thioesterase)
and
Arthrobacter (ligase-dehalogenase-putative thioesterase)
operons, made the assignment of the
fcbC as the 4-HBA-CoA thioesterase
gene uncertain. In the present study, the
fcbC gene was subcloned,
and its protein product was characterized.

MATERIALS AND METHODS
4-HBA-CoA thioesterase preparation.
The
Arthrobacter sp. strain SU
fcbC was amplified by PCR (
13)
by using the
pAS5 clone (previously prepared from the native
plasmid pASU1) (
27) as a template and commercial oligonucleotides
as primers. The PCR products were digested with the restriction
enzymes
NdeI and
HindIII and then purified by agarose gel chromatography
before T4 DNA ligase-catalyzed ligation to the
NdeI- and
HindIII-digested
pET-23b vector (Novagen). The resulting clone was transformed
into competent
Escherichia coli BL21(DE3) cells for gene expression.
The cloned gene was verified by DNA sequencing. A WT-Arthio/pET-23b
transformant of
E. coli BL21(DE3) was grown aerobically at 37°C
in Luria-Bertani medium containing 50 µg of carbenicillin/ml.
Protein production was induced with 0.4 mM IPTG (isopropyl-ß-
D-thiogalactopyranoside)
at ca. 10 h postinoculation (cell density had reached an optical
density at 600 nm of 1.0). After a 5-h induction period, the
cells were harvested by centrifugation (5,000
x g for 15 min)
and then resuspended in 200 ml of buffer (50 mM K
+HEPES [potassium
salt of HEPES], 1 mM dithiothreitol, 0.1 mM phenylmethylsulfonyl
fluoride; pH 7.5) at 0°C. The cell suspension was passed
through a French press at 1,200 lb/in
2 twice before centrifugation
at 48,000
x g and 4°C for 60 min. The supernatant was applied
to a (5 by 40 cm) DEAE-Sepharose (Amersham Pharmacia Biotech)
column and eluted at 4°C with a 2-liter gradient of 0 to
0.5 M KCl in 50 mM HEPES (pH 7.5). The chromatography was monitored
by measuring the eluant absorbance (280 nm) and thioesterase
activity (see below). The thioesterase-containing fractions
(eluted at

0.2 M KCl) were combined, and then treated with ammonium
sulfate. The 60 to 80% ammonium sulfate (wt/vol) protein precipitant
was dissolved in 2 ml of 50 mM HEPES-0.2 M KCl (pH 7.5) buffer,
applied to a 2-by-100-cm Sephacryl S-200 column (Amersham Pharmacia
Biotech), and eluted at 4°C with the same buffer. The thioesterase-containing
fractions were pooled and concentrated with a 10-kDa Macrosep
Centricon (Pall Filtron). The yield of homogeneous thioesterase
(based on sodium dodecyl sulfate-polyacrylamide gel electrophoresis
[SDS-PAGE] analysis) was 100 mg/g of wet cell.
Thioesterase molecular size determination.
The molecular mass was calculated from the amino acid composition, derived from the gene sequence, by using the EXPASY molecular biology server program Compute pI/Mw (2). The molecular mass was measured by electrospray mass spectrometry (mass spectrometry facility at the University of New Mexico) and by SDS-PAGE (a 4% stacking gel and a 16% separating gel). Commercial protein molecular weight standards were used to generate a plot of log of the molcular mass versus the distance traveled on the gel.
Synthesis of [14C]-labeled 4-HBA-CoA.
[14C]4-HBA-CoA (14C-labeled benzoyl C=O) was prepared by Pseudomonas sp. strain CBS3 4-CBA-CoA dehalogenase (7)-catalyzed dehalogenation of [14C]4-CBA-CoA (34). A typical reaction contained 46 µM [14C]4-CBA-CoA (specific activity = 56 µCi/µmol) and 1.5 µM dehalogenase in 100 µl of 50 mM K+HEPES (pH 7.5). After incubation for 3 h at room temperature, the reaction solution was filtered through a 3-kDa microfilter (Pall Gelman) to remove the enzyme from the [14C]4-HBA-CoA product.
Steady-state kinetic constant determination.
Owing to its small value, the 4-HBA-CoA Km was measured by using a fixed-time, radioisotope-based assay. [14C]4-HBA-CoA (56 µCi/µmol; 1.2 to 4.6 µM) was incubated with 1.8 nM thioesterase in 21 µl of 50 mM K+HEPES (pH 7.5) for a specified time period (typically 0.5 or 1 min) and then mixed with 10 µl of 0.3 M HCl to terminate the reaction within 20% conversion. Unlabeled 4-HBA-CoA and 4-HBA were added to the reaction solution prior to chromatography on a Beckman Ultrasphere analytical reversed-phase C18 column (4.6 by 250 mm; Rainin Dynamax HPLC System). A sequential, linear gradient (10 to 33.5% solvent B for 0 to 12 min and 33.5 to 70% solvent B for 12 to 14 min) was used to elute the column at a flow rate of 1 ml/min. Solvent A was 20 mM ammonium phosphate (adjusted to pH 6.7 with H3PO4), and solvent B was 16:9 (vol/vol) CH3CN-H2O and 20 mM ammonium phosphate (adjusted to pH 6.7 with H3PO4). The eluant was analyzed by measuring the absorbance at 260 nm and by liquid scintillation counting. The retention times of 4-HBA and 4-HBA-CoA were 3.3 and 11.1 min, respectively. The concentration of the product formed in the reaction was calculated from the ratio of the counts per minute (cpm) in the 4-HBA peak to the total cpm in the eluant and the concentration of [14C]4-HBA-CoA in the original reaction solution. The initial velocity was calculated from the concentration of product formed divided by the reaction time. The initial velocity data, measured as a function of substrate concentration, were analyzed by using the following equation and the computer program KinetAsyst (IntelliKinetics): V = Vmax [S]/([S] + Km), where V is the initial velocity, Vmax is the maximum velocity, [S] is the substrate concentration, and Km is the Michaelis constant. The kcat was calculated from Vmax/[E], where [E] is the total enzyme concentration (determined by the Bradford method [5]).
Other kcat and Km determinations were made by using a DTNB [5,5'-dithio-bis(2-nitrobenzoic acid)]-based continuous spectrophotometric assay. Hydrolysis reactions of the acyl-thioester substrates were monitored at 25°C by measuring the absorbance of 5-thio-2-nitrobenzoate at 412 nm (
= 13.6 mM-1 cm-1), formed by reaction of DTNB with the product, CoA. Reaction mixtures (200 µl) contained thioesterase, acyl-CoA substrate (0.5 to 5 Km), DTNB (2 mM), KCl (0.2 M), and 50 mM K+HEPES (pH 7.5). The kinetic parameters of Vmax and Km were determined from initial velocity data, measured as a function of substrate concentration, by using the equation presented above and the computer program KinetAsyst. Inactivation of the thioesterase by the DTNB was tested and ruled out by carrying out enzyme-DTNB preincubation experiments.
pH rate profile analysis.
The initial velocities of the Arthrobacter sp. strain SU thioesterase-catalyzed hydrolysis of saturating 4-HBA-CoA (100 µM) were monitored at 25°C by measuring the decrease in solution absorbance at 300 nm resulting from the disappearance of reactant (i.e., 
= 11.8 mM-1 cm-1.). A universal tribuffer system containing 50 mM acetate, 50 mM 2-(N-morpholino)ethanesulfonate, and 100 mM Tris (pH 4.6 to 9.6) (12) was used to measure the pH dependence of the catalyzed reaction. The kcat was calculated from the ratio of the experimental initial velocity (by assuming equivalence to maximum velocity) and the enzyme concentration of reaction mixture. The enzyme concentration was determined by using a Bradford assay (5).

RESULTS
Thioesterase purification and molecular size determination.
The
Arthrobacter sp. strain SU thioesterase gene was overexpressed
in
E. coli BL21(DE3) cells transformed with the WT-Arthio/pET-23b
clone. After induction and cell lysis, the thioesterase was
purified by anion exchange and gel filtration column chromatography
in a yield of 100 mg/g of wet cells. The purified protein was
judged to be homogeneous based on SDS-PAGE analysis (see Fig.
2, estimated size of 17 kDa). The theoretical mass of 16,394.41
Da agrees closely with the actual mass measured by electrospray
mass spectrometry of 16394.40 Da, thus showing that the N-terminal
Met1 was not removed by posttranslational modification.
Thioesterase substrate specificity.
Common soil-dwelling bacteria such as members of the genus
Arthrobacter degrade a variety of aromatic compounds, including phenylacetate,
benzoate, and mono- and di-hydroxybenzoates (
10,
15,
18,
33).
The steady-state kinetic constants measured for the thioesterase-catalyzed
hydrolysis of several aromatic acyl-CoA thioesters are listed
in Table
1. The value of
kcat/
Km (or specificity constant) is
a measure of substrate activity. The large value of the 4-HBA-CoA
kcat/
Km = 5.4
x 10
6 M
-1 s
-1 (which compares to the
kcat/
Km =
3.1
x 10
6 M
-1 s
-1 measured for the 4-HBA-CoA thioesterase of
Pseudomonas sp. strain CBS3 [
37]) indicates that 4-HBA-CoA is
a natural substrate for the thioesterase. Although a
kcat/
Km value of 7.2
x 10
5 M
-1 s
-1 of 3-HBA-CoA was found to be ca.
10-fold lower, this substrate is still considered to be quite
active. Interestingly, the
kcat of 3-HBA-CoA was

3-fold larger
than that of the 4-HBA-CoA. The greater reactivity might be
explained by the resonance effect (i.e., reduced electron donation
of the hydroxyl substituent from the
meta position). The 2,5-dihydroxybenzoyl-CoA
was, by comparison, a poor substrate. The presence of a hydroxyl
group in the
ortho position may cause steric hindrance to the
nucleophilic attack occurring at the carbonyl carbon.
View this table:
[in this window]
[in a new window]
|
TABLE 1. Steady-state kinetic constants for Arthrobacter sp. strain SU thioesterase-catalyzed hydrolysis of acyl-CoA thioesters at pH 7.5 and 25°C determined by using the DTNB spectrophotometric assaya
|
Benzoyl-CoA, which lacks a ring hydroxyl group, was almost 1,000-fold
less reactive than 4-HBA-CoA. However, once bound to the enzyme,
the rate of hydrolysis (
kcat = 1.9 s
-1) was only 3.6-fold lower
than that of 4-HBA-CoA. Thus, the ring hydroxyl substituent
appears to be an important factor in substrate binding, enhancing
binding when located at the
para position.
The phenylacetyl-CoA was by far the least reactive substrate among the aromatic acyl-CoA thioesters tested (kcat/Km = 6.5 M-1 s-1). The conjugation of the thioester moiety to the aromatic ring appears to be required for substrate recognition by the thioesterase.
Fatty acyl-CoA and short-chain acyl-CoA thioesters are produced in bacterial cells to perform a variety of roles in metabolism and membrane function. We tested the substrate activities of a variety of short- and medium-chain acyl-CoA thioesters. As indicated in Table 1, none of these thioesters showed substantial substrate activity. Thus, the Arthrobacter sp. strain SU thioesterase appears to be specific for the benzoyl-CoA core structure and most active with the benzoyl-CoA thioester that is hydroxylated at the para position. This substrate specificity profile is consistent with the primary role of the thioesterase in the metabolism of 4-CBA via the dehalogenation pathway of Fig. 1.
Lastly, the substrate activity of 4-CBA-CoA with the thioesterase was tested. In the bacterium, 4-CBA dehalogenation occurs via conversion of the 4-CBA carboxyl group to a thioester, followed by nucleophilic substitution of the ring chloride and regeneration of the ring carboxylate group by thioester hydrolysis (Fig. 1). The conversion of the 4-CBA to the 4-CBA-CoA thioester consumes a molecule of ATP (for 4-CBA-adenylate formation). Therefore, it is essential that thioesterase catalyzed hydrolysis of 4-CBA-CoA does not compete with the dehalogenation of 4-CBA-CoA to 4-HBA-CoA. Otherwise, a futile cycle of 4-CBA-CoA synthesis and hydrolysis would occur at the expense of cellular ATP. The kcat/Km = 2.2 x 103 M-1 s-1 for thioesterase-catalyzed 4-CBA-CoA hydrolysis (Table 1) was 10-fold smaller than the kcat/Km = 2.3 x 104 M-1 s-1 for dehalogenase-catalyzed 4-CBA-CoA dehalogenation measured under the same conditions (pH 7.5, 25°C) (Y. Wei and D. Dunaway-Mariano, unpublished data). This rate difference should prevent loss of the 4-CBA-CoA to thioesterase-catalyzed hydrolysis provided that the cellular dehalogenase concentration is as great or greater than the cellular thioesterase concentration.
Thioesterase pH optimum.
To determine the optimal pH range for thioesterase catalysis, the variation in the value of kcat values for 4-HBA-CoA hydrolysis was measured. As illustrated in Fig. 3, there was no substantial change in the rate of catalysis over a pH range from 4.6 to 9.6. This indicates that acid and base catalysis is not required for the catalyzed reaction or, alternatively, that the pKa values of the participating acid or base groups reside outside of the pH range examined. The C(4)OH of the 4-HBA-CoA in aqueous solution ionizes with a pKa of 8.6 (32). Thus, it might be expected that substrate ionization would impair catalysis at an alkaline pH. Since the kcat is not significantly reduced, it can be inferred that either the environment of the active site increases the pKa of the bound substrate or only the protonated form of the substrate binds to the enzyme. In future studies the pH profiles of the substrate kcat/Km and the Ki for inhibitor binding will be measured to learn more about the pH dependency of substrate binding.
4-HBA-CoA thioesterase sequence comparison.
The observation that two bacterial enzymes functioning in the
same metabolic pathway and catalyzing the same reaction with
equal efficiency share no significant sequence similarity is
quite remarkable. A protein-threading study using the program
3D-PSSM (
20) with
Arthrobacter thioesterase as a query sequence
identified the known
Pseudomonas 4-HBA-CoA thioesterase fold
(
3) with 95% certainty. Thus, despite the absence of sequence
homology, the two enzymes may share the same fold. The determination
of the X-ray crystal structure of the
Arthrobacter 4-HBA-CoA
thioesterase, which is under way, should provide helpful insight
into the structural divergence of these two enzymes.
The results from sequence homology searches carried out with the Pseudomonas and Arthrobacter thioesterase sequences further underscored their evolutionary distance. The NCBI PSI/PHI-BLAST searches (1), carried out through six iterations by using the Pseudomonas and Arthrobacter thioesterase sequences as queries, respectively, identified two unique groups of protein homologs (i.e., none of the homologs were common to both groups of sequences). Additionally, when the two groups of sequences (40 representative sequences from each) were combined and analyzed by using the GCG PILE-UP program, the Pseudomonas thioesterase-derived sequences separated into one group and the Arthrobacter thioesterase homologs separated into a second group. Based on these results, it was concluded that these two groups of sequences represent two distinct subfamilies within the hotdog-fold enzyme superfamily, to which the Pseudomonas sp. strain CBS3 4-HBA-CoA thioesterase has been assigned (3).
The first 20 sequences taken from each of the two sequence families are shown in Fig. 4. The active-site carboxylate residues Asp17 and Asp32 (30) of the Pseudomonas thioesterase are indicated by an asterisk. Asp17 functions in base or nucleophilic catalysis (30) and is stringently conserved among the subfamily members. Remarkably, there are no polar residues found in the Arthrobacter thioesterase, which are stringently conserved among its subfamily members.

DISCUSSION
The present work has demonstrated that the
Arthrobacter sp.
strain SU
fcbC gene encodes 4-HBA-CoA thioesterase. Therefore,
it is evident that the operons encoding 4-CBA dehalogenation
in
Pseudomonas sp. strain CBS3 and
Arthrobacter sp. strain SU
display different gene orders. Examination of the literature
reveals that the ligase-dehalogenase-thioesterase arrangement
observed in
Arthrobacter sp. strain SU is also observed in
Arthrobacter sp. strain TM1 (GenBank accession no.
AF042490). Moreover, the
dehalogenase-ligase-thioesterase gene order observed in the
Pseudomonas sp. strain CBS3 is observed in the
Pseudomonas sp.
strain DJ-12 (
6). However, in this latter strain, three transport
protein genes are inserted between the ligase and thioesterase
genes. The differences observed in pathway gene order in different
host strains suggests that the 4-CBA pathway operon has been
subjected to reorganization.
In addition to differences in the gene order, the proteins themselves have undergone sequence divergence. Whereas the respective 4-CBA dehalogenation pathway proteins of the two Arthrobacter strains are matched in sequence, those of the two Pseudomonas strains are not. Sequence comparisons between paired enzymes from the two Pseudomonas dehalogenation pathways show that the sequence identity between the ligases is 58%, that between the dehalogenases is 86%, and that between the thioesterases is only 65%. Even greater sequence divergence is evident from the Arthrobacter-Pseudomonas 4-CBA pathway protein sequence comparisons (50% identity for dehalogenases, 38% for ligases and ca. 10% for thioesterases).
The divergence in the 4-CBA pathway operon at the level of gene order and at the level of protein sequence indicates that the 4-CBA dehalogenation pathway genes are not the result of recent adaptation. Thus, it is unlikely that the evolution of the dehalogenation pathway was triggered by the release of 4-CBA and 4-polychlorinated biphenyls into the environment by industry as was originally thought (4). Enzymes, such as atrazine chlorohydrolase (29), known to have evolved in response to global pollution by a novel substrate do not deviate in amino acid sequence from one host bacterial strain to another. In addition, a recently evolved enzyme will display a close sequence match (>90% identity) with a protein (its progenitor) that performs a different catalytic function in a classical metabolic pathway (29). This is not the case with any one of the three 4-CBA pathway enzymes.
In view of the variety of halogenated aromatic compounds made by both prokaryotes and eukaryotes (9, 16, 31), it is suspected that natural sources of 4-CBA exist (24). The 4-CBA degradation pathway may have emerged in opportunistic bacteria once these sources became established, and the genes of the 4-CBA dehalogenation pathway may have thus had the opportunity to diverge through the process of random mutation and selection over a very long period of time. As with other operons that offer survival advantages to bacteria in particular niches, the 4-CBA dehalogenation pathway operon appears to have been passed from one strain to another (with some disruption). Indeed, evidence for horizontal operon transfer can be found in the transposon sequence (GenBank accession no. AF537222) that flanks the 4-CBA dehalogenation pathway operon (36) in Alcaligenes sp. strain AL3007 (22).

ACKNOWLEDGMENTS
This work was supported in part by NIH grant GM28688 to D.D.-M.
We thank Lawrence Kelley in the Biomolecular Modelling Lab at Imperial College of Science of the United Kingdom for assistance with the 3D-PSSM threading analysis.

FOOTNOTES
* Corresponding author. Mailing address: Department of Chemistry, University of New Mexico, Clark Hall 103, Albuquerque, NM 81713. Phone: (505) 277-3383. Fax: (505) 277-6202. E-mail:
dd39{at}unm.edu.


REFERENCES
1 - Altschul, S. F., T. L. Madden, A. A. Schaffer, J. Zhang, Z. Zhang, W. Miller, and D. J. Lipman. 1997. Gapped BLAST and PSI-BLAST: a new generation of protein database search programs. Nucleic Acids Res. 25:3389-3402.[Abstract/Free Full Text]
2 - Appel, R. D., A. Bairoch, and D. F. Hochstrasser. 1994. A new generation of information retrieval tools for biologists: the example of the ExPASy WWW server. Trends Biochem. Sci. 19:258-260.[CrossRef][Medline]
3 - Benning, M. M., G. Wesenberg, R. Liu, K. L. Taylor, D. Dunaway-Mariano, and H. M. Holden. 1998. The three-dimensional structure of 4-hydroxybenzoyl-CoA thioesterase from Pseudomonas sp. strain CBS-3. J. Biol. Chem. 273:33572-33579.[Abstract/Free Full Text]
4 - Benning, M. M., K. L. Taylor, R. Q. Liu, G. Yang, H. Xiang, G. Wesenberg, D. Dunaway-Mariano, and H. M. Holden. 1996. Structure of 4-chlorobenzoyl coenzyme A dehalogenase determined to 1.8 Å resolution: an enzyme catalyst generated via adaptive mutation. Biochemistry 35:8103-8109.[CrossRef][Medline]
5 - Bradford, M. M. 1976. A rapid and sensitive method for the quantitation of microgram quantities of protein utilizing the principle of protein-dye binding. Anal. Biochem. 72:248-254.[CrossRef][Medline]
6 - Chae, J. C., Y. Kim, Y. C. Kim, G. J. Zylstra, and C. K. Kim. 2000. Genetic structure and functional implication of the fcb gene cluster for hydrolytic dechlorination of 4-chlorobenzoate from Pseudomonas sp. DJ-12. Gene 258:109-116.
7 - Chang, K. H., P. H. Liang, W. Beck, J. D. Scholten, and D. Dunaway-Mariano. 1992. Isolation and characterization of the three polypeptide components of 4-chlorobenzoate dehalogenase from Pseudomonas sp. strain CBS-3. Biochemistry 31:5605-5610.
8 - Cork, D. J., and J. P. Krueger. 1991. Microbial transformations of herbicides and pesticides. Adv. Appl. Microbiol. 36:1-66.[Medline]
9 - de Jong, E., and J. A. Field. 1997. Sulfur tuft and turkey tail: biosynthesis and biodegradation of organohalogens by Basidiomycetes. Annu. Rev. Microbiol. 51:375-414.[CrossRef][Medline]
10 - Diaz, E., A. Ferrandez, M. A. Prieto, and J. L. Garcia. 2001. Biodegradation of aromatic compounds by Escherichia coli. Microbiol. Mol. Biol. Rev. 65:523-569.[Abstract/Free Full Text]
11 - Dunaway-Mariano, D., and P. C. Babbitt. 1994. On the origins and functions of the enzymes of the 4-chlorobenzoate to 4-hydroxybenzoate converting pathway. Biodegradation 5:259-276.[CrossRef][Medline]
12 - Ellis, K. J., and J. F. Morrison. 1982. Buffers of constant ionic strength for studying pH-dependent processes. Methods Enzymol. 87:405-426.[Medline]
13 - Erlich, H. A. 1992. PCR technology principles and applications for DNA amplification. W. H. Freeman and Co., New York, N.Y.
14 - Furukawa, K. 1994. Molecular genetics and evolutionary relationship of PCB-degrading bacteria. Biodegradation 5:289-300.[CrossRef][Medline]
15 - Gerischer, U. 2002. Specific and global regulation of genes associated with the degradation of aromatic compounds in bacteria. J. Mol. Microbiol. Biotechnol. 4:111-121.[CrossRef][Medline]
16 - Gribble, G. W. 1996. Naturally occurring organohalogen compounds: a comprehensive survey. Prog. Org. Nat. Prod. 68:1-498.
17 - Haggblom, M. M. 1992. Microbial breakdown of halogenated aromatic pesticides and related compounds. FEMS Microbiol. Rev. 9:29-71.[Medline]
18 - Harwood, C. S., G. Burchhardt, H. Herrmann, and G. Fuchs. 1999. Anaerobic metabolism of aromatic coumpounds via the benzoyl-CoA pathway. FEMS Microbiol. Rev. 22:439-458.[CrossRef]
19 - Higson, F. K. 1992. Microbial degradation of biphenyl and its derivatives. Adv. Appl. Microbiol. 37:135-164.[Medline]
20 - Kelley, L. A., R. M. MacCallum, and M. J. Sternberg. 2000. Enhanced genome annotation using structural profiles in the program 3D-PSSM. J. Mol. Biol. 299:499-520.[Medline]
21 - Klages, U., and F. Lingens. 1980. Degradation of 4-chlorobenzoic acid by Pseudomonas sp. Zentbl. Bakteriol. Parasitenkd. Infectionskr. Hyg. Abt. 1 Orig. C 1:215-223.
22 - Layton, A. C., J. Sanseverino, W. Wallace, C. Corcoran, and G. S. Sayler. 1992. Evidence for 4-chlorobenzoic acid dehalogenation mediated by plasmids related to pSS50. Appl. Environ. Microbiol. 58:399-402.[Abstract/Free Full Text]
23 - Marks, T. S., R. Wait, A. R. Smith, and A. V. Quirk. 1984. The origin of the oxygen incorporated during the dehalogenation/hydroxylation of 4-chlorobenzoate by an Arthrobacter sp. Biochem. Biophys. Res. Commun. 124:669-674.[CrossRef][Medline]
24 - Niedan, V., and H. F. Scholer. 1997. Natural formation of chlorobenzoic acids (CBA) and distinction between PCB-degraded CBA. Chemosphere 35:1233-1241.[CrossRef]
25 - Ruisinger, S., U. Klages, and F. Lingens. 1976. Degradation of 4-chlorobenzoic acid by an Arthrobacter species. Arch. Microbiol. 110:253-256. (In German.)
26 - Savard, P., L. Peloquin, and M. Sylvestre. 1986. Cloning of Pseudomonas sp. strain CBS3 genes specifying dehalogenation of 4-chlorobenzoate. J. Bacteriol. 168:81-85.[Abstract/Free Full Text]
27 - Schmitz, A., K. H. Gartemann, J. Fiedler, E. Grund, and R. Eichenlaub. 1992. Cloning and sequence analysis of genes for dehalogenation of 4-chlorobenzoate from Arthrobacter sp. strain SU. Appl. Environ. Microbiol. 58:4068-4071.[Abstract/Free Full Text]
28 - Scholten, J. D., K. H. Chang, P. C. Babbitt, H. Charest, M. Sylvestre, and D. Dunaway-Mariano. 1991. Novel enzymic hydrolytic dehalogenation of a chlorinated aromatic. Science 253:182-185.[Abstract/Free Full Text]
29 - Seffernick, J. L., and L. P. Wackett. 2001. Rapid evolution of bacterial catabolic enzymes: a case study with atrazine chlorohydrolase. Biochemistry 40:12747-12753.[CrossRef][Medline]
30 - Thoden, J. B., H. M. Holden, Z. Zhuang, and D. Dunaway-Mariano. 2002. X-ray crystallographic analyses of inhibitor and substrate complexes of wild-type and mutant 4-hydroxybenzoyl-CoA thioesterase. J. Biol. Chem. 277:27468-27476.[Abstract/Free Full Text]
31 - van Pee, K. H. 1996. Biosynthesis of halogenated metabolites by bacteria. Annu. Rev. Microbiol. 50:375-399.[CrossRef][Medline]
32 - Webster, L. T., Jr., J. J. Mieyal, and U. A. Siddiqui. 1974. Benzoyl and hydroxybenzoyl esters of coenzyme A: ultraviolet characterization and reaction mechanisms. J. Biol. Chem. 249:2641-2645.[Abstract/Free Full Text]
33 - Williams, P. A., and J. R. Sayers. 1994. The evolution of pathways for aromatic hydrocarbon oxidation in Pseudomonas. Biodegradation 5:195-217.[CrossRef][Medline]
34 - Yang, G., P. H. Liang, and D. Dunaway-Mariano. 1994. Evidence for nucleophilic catalysis in the aromatic substitution reaction catalyzed by (4-chlorobenzoyl)coenzyme A dehalogenase. Biochemistry 33:8527-8531.[CrossRef][Medline]
35 - Yi, H., K. Min, C. Kim, and J. Ka. 2000. Phylogenetic and phenotypic diversity of 4-chlorobenzoate-degrading bacteria isolated from soils. FEMS Microbiol. Ecol. 31:53-60.[CrossRef][Medline]
36 - Zhang, W. 2000. Ph.D. thesis. University of Maryland, College Park.
37 - Zhuang, Z., F. Song, W. Zhang, K. Taylor, A. Archambault, D. Dunaway-Mariano, J. Dong, and P. R. Carey. 2002. Kinetic, Raman, NMR, and site-directed mutagenesis studies of the Pseudomonas sp. strain CBS3 4-hydroxybenzoyl-CoA thioesterase active site. Biochemistry 41:11152-11160.[CrossRef][Medline]
Applied and Environmental Microbiology, May 2003, p. 2707-2711, Vol. 69, No. 5
0099-2240/03/$08.00+0 DOI: 10.1128/AEM.69.5.2707-2711.2003
Copyright © 2003, American Society for Microbiology. All Rights Reserved.
This article has been cited by other articles:
-
Song, F., Zhuang, Z., Finci, L., Dunaway-Mariano, D., Kniewel, R., Buglino, J. A., Solorzano, V., Wu, J., Lima, C. D.
(2006). Structure, Function, and Mechanism of the Phenylacetate Pathway Hot Dog-fold Thioesterase PaaI. J. Biol. Chem.
281: 11028-11038
[Abstract]
[Full Text]
-
Thoden, J. B., Zhuang, Z., Dunaway-Mariano, D., Holden, H. M.
(2003). The Structure of 4-Hydroxybenzoyl-CoA Thioesterase from Arthrobacter sp. strain SU. J. Biol. Chem.
278: 43709-43716
[Abstract]
[Full Text]