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Journal of Bacteriology, December 1998, p. 6529-6537, Vol. 180, No. 24
0021-9193/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
Novel Organization of the Genes for Phthalate
Degradation from Burkholderia cepacia DBO1
Hung-Kuang
Chang and
Gerben J.
Zylstra*
Biotechnology Center for Agriculture and the
Environment, Cook College, Rutgers University, New Brunswick, New
Jersey 08901-8520
Received 5 May 1998/Accepted 6 October 1998
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ABSTRACT |
Burkholderia cepacia DBO1 is able to utilize phthalate
as the sole source of carbon and energy for growth. Two overlapping cosmid clones containing the genes for phthalate degradation were isolated from this strain. Subcloning and activity analysis localized the genes for phthalate degradation to two separate regions on the
cosmid clones. Analysis of the nucleotide sequence of these two regions
showed that the genes for phthalate degradation are arranged in at
least three transcriptional units. The gene for phthalate dioxygenase
reductase (ophA1) is present by itself, while the genes for
an inactive transporter (ophD) and 4,5-dihydroxyphthalate decarboxylase (ophC) are linked and the genes for phthalate
dioxygenase oxygenase (ophA2) and cis-phthalate
dihydrodiol dehydrogenase (ophB) are linked.
ophA1 and ophDC are adjacent to each other but
are transcribed in opposite directions, while ophA2B is
located 4 kb away. The genes for the oxygenase and reductase components of phthalate dioxygenase are located approximately 7 kb away from each
other. The gene for the putative phthalate permease contains a
frameshift mutation in contrast to genes for other permeases. Strains
deleted for ophD are able to transport phthalate into the
cell at rates equivalent to that of the wild-type organism, showing
that this gene is not required for growth on phthalate.
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INTRODUCTION |
Phthalates and phthalate esters are
widely used in the manufacture of plastics, textiles, papers, insect
repellents, pesticides, munitions, and cosmetics (36, 70).
Due to the widespread use of phthalates, there has been great concern
about their release into the environment (34, 45, 57) and
their toxicity to human beings and other organisms (4, 32, 41, 43,
56, 70, 80, 84, 85). Many microorganisms have been isolated from
rivers, soil, and even marine regions for their ability to degrade
phthalate aerobically or anaerobically (1, 27, 47, 60, 67, 68, 73,
74, 78, 79). Two catabolic pathways have been identified for the
aerobic degradation of phthalate. Gram-negative bacteria degrade
phthalate via 4,5-dihydroxyphthalate and protocatechuate (47, 60,
65, 73). Gram-positive bacteria also degrade phthalate through
protocatechuate, but in this case the pathway proceeds through
3,4-dihydroxyphthalate as an intermediate (26, 65, 74).
Protocatechuate, a central metabolite for many aromatic
degradation pathways, is further metabolized through either an
ortho or meta cleavage pathway.
Burkholderia cepacia DBO1 was originally isolated in Florida
for its ability to utilize phthalate as the sole carbon and energy source. The strain was first published as Pseudomonas
fluorescens PHK (46); it was subsequently known as
Pseudomonas putida (12) and was later
reclassified as Pseudomonas cepacia on the basis of detailed
nutritional studies (6). The P. cepacia species is now associated with the Burkholderia genus
(86). The ability of this particular strain to degrade
phthalate (see Fig. 1) has been well documented (47, 73,
74). Phthalate is first dihydroxylated by phthalate dioxygenase
to give 4,5-dihydro-4,5-dihydroxyphthalate (cis-phthalate dihydrodiol). This two-component enzyme
consists of a reductase (phthalate dioxygenase reductase [PDR]) and
an oxygenase (phthalate dioxygenase oxygenase [PDO]). Both proteins have been purified to homogeneity (6), and the crystal
structure of PDR has been determined at a 2.0-Å resolution
(20). The 34-kDa PDR can be subdivided into three parts, a
flavin mononucleotide (FMN) binding domain, an NAD+ binding
domain, and a plant ferredoxin-type [2Fe-2S] domain, that function to
transfer electrons from NADH to PDO. The 48-kDa PDO has one Rieske-type
[2Fe-2S] center, which functions to accept electrons from PDR, and a
mononuclear iron known to be involved in the actual catalytic addition
of oxygen to the aromatic ring. PDO has also been well studied,
especially with regard to the Rieske iron sulfur center which has been
analyzed by electron nuclear double-resonance spectroscopy (17,
37), pulsed electron paramagnetic resonance spectroscopy
(17), resonance Raman spectroscopy (49), and
X-ray absorption spectroscopy (81). The ferrous active site
has been analyzed by magnetic circular dichroism during substrate
binding (33). Phthalate dioxygenase is perhaps the best-studied aromatic dioxygenase from a biophysical point of view.
The second step in the catabolic pathway involves a dehydrogenase that
removes two electrons and two hydrogens from cis-phthalate dihydrodiol to form 4,5-dihydroxyphthalate and NADH. One of the two
carboxyl groups of the latter compound is removed by
4,5-dihydroxyphthalate decarboxylase (72) to form
protocatechuate, a central metabolite in the catabolism of aromatic
compounds. In B. cepacia DBO1, protocatechuate then
undergoes ortho ring cleavage and is metabolized through the
well-known
-ketoadipate pathway to eventually produce tricarboxylic acid cycle intermediates. Protocatechuate 3,4-dioxygenase from B. cepacia DBO1 has been extensively studied at the biochemical (12), genetic (91), and physiological
(90) levels.
Although much is known about the initial biochemical mechanisms by
which B. cepacia DBO1 metabolizes phthalate, nothing is known about the underlying genetic basis. The goal of the present work
was to determine the molecular basis of phthalate degradation by
B. cepacia DBO1 to complement the existing biochemical
studies and to provide a basis for further investigations on these
enzymes. Preliminary reports of this work have been presented elsewhere (14, 15, 54).
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MATERIALS AND METHODS |
Bacterial strains, plasmids, and media.
B.
cepacia DBO1 is the same strain as the P. putida
reported by Bull and Ballou (12) and the P. fluorescens PHK of Ribbons (46). B. cepacia
ATCC 29424 is the original PHK strain deposited by Ribbons in the
American Type Culture Collection (ATCC). B. cepacia ATCC
17616 (77) is a phthalate-degrading strain isolated by other
investigators independently of ATCC 29424. B. cepacia DBO106
is a mutant of DBO1 that accumulates cis-phthalate
dihydrodiol (89). Comamonas testosteroni NH1024
is a mutant that accumulates 4,5-dihydroxyphthalate (60).
Escherichia coli DH5
[F
80dlacZ
M15
(lacZY-argF)U169 deoR recA1 endA1 hsdR17
(rK
mK+) supE44
thi-1 gyrA96 relA1] (Gibco-BRL, Gaithersburg, Md.) was used as
the recipient strain in the cloning experiments, and E. coli
S17-1 (thi pro hsdR hsdM+ recA RP4
tra+) (76) or HB101 (supE44
hsdS20 recA13 ara-14 proA2 lacY1 galK2 rpsL20 xyl-5 mtl-1)
(9) was used as the recipient strain in the cosmid cloning
experiments. The cosmid cloning vectors pMMB34 (29) and
pHC79 (39) were used to construct the genomic libraries, and
the pGEM series of cloning vectors (Promega, Madison, Wis.), pUC19
(83), pRK415 (44), and pTrc99A
(2), were used to construct subclones. Mineral salts basal
(MSB) medium (77) was used as minimal medium, and L broth
(52) was used as complete medium. Ampicillin and
tetracycline were added at 100 and 15 µg/ml, respectively, when
needed. Burkholderia strains were grown at 30°C, and
E. coli strains were grown at 37°C.
Molecular techniques.
Total genomic DNA from B. cepacia DBO1 was prepared by the method of Olsen et al.
(69). Plasmid DNA was isolated by the alkaline-sodium
dodecyl sulfate procedure of Birnboim and Doly (8) or
purified by the QIAprep spin column procedure (Qiagen, Inc., Santa
Clarita, Calif.). Transformation of plasmid DNA into competent E. coli DH5
was performed by the procedure of Hanahan (38) or the calcium chloride-glycerol transformation
procedure (75). Restriction digests and ligations of DNA
samples were performed as recommended by the supplier (Gibco-BRL). Two
genomic libraries were constructed, the first with partially
EcoRI-digested total genomic DNA and the cosmid pMMB34 and
the other with partially Sau3AI-digested total genomic DNA
and the cosmid pHC79, by using procedures described earlier (35,
48). Colony blot and Southern hybridization experiments were
performed as described previously (48, 75). Three
oligonucleotides corresponding to the amino acid sequences of PDR and
PDO were synthesized. PDR-N (5'-CAP-GAP-GAY-GGN-TTY-YT-3') corresponds
to the fourth through ninth amino acids (QEDGFL) from the N-terminal
end of PDR (TTPQEDGFL). PDR-C (5'-AC-RCA-NAC-CAT-DAT-YTG-3') corresponds to amino acids 13 through 18 (QIMVCV) from the C-terminal end of PDR (KGTQIMVCVSRAKSAELVLDL). PDO-N
(5'-CAN-CAY-CAP-GAP-AAY-GA-3') corresponds to the second through the
seventh amino acids from the N-terminal end of PDO (LTHQENE). The
oligonucleotides were labeled with T4 kinase (Gibco-BRL) for use in
Southern hybridization experiments. DNA sequencing was performed with
an AmpliTaq DNA polymerase dye-terminator cycle-sequencing kit
(Perkin-Elmer, Foster City, Calif.) and resolved on an ABI 373 DNA
sequencer (Perkin-Elmer).
Coupled in vitro transcription-translation from purified plasmid DNA
was performed with an E. coli S30 extract system as
described by the manufacturer (Promega). Tritiated leucine was added to the reaction mix to label the protein product. Aliquots (5 µl) from
the reaction mix were analyzed with a denaturing 15% (wt/vol) polyacrylamide gel by using standard procedures (75). The
gel was dried, and the signals were enhanced by fluorography and
detected by X-ray film exposure. Prestained molecular weight markers
(Gibco-BRL) were used to estimate the size of each detected protein.
A knockout mutant of
ophD was constructed by gene
replacement with an inserted kanamycin resistance gene cassette. A
1.2-kb
PCR product containing the
ophA1 gene on the left of
ophD was
PCR amplified by using the primers
GC
GAATTCTGAGCGAAGCGTAGG and
GC
GAGCTCCTGGATACCGGCAGG containing
EcoRI and
SstI restriction
sites (underlined),
respectively. A 1.2-kb PCR product containing
the
ophC gene
on the right of
ophD was PCR amplified by using
the primers
GC
GAGCTCTCAGACAGGAGCAGG and
GC
TCTAGACCATGCCTTCCTCGC
containing
SstI and
XbaI restriction sites (underlined),
respectively.
PCR in these cases was performed with
Taq
polymerase with an initial
denaturation step of 1.0 min at 94°C; 30 cycles of 15 s at 94°C
(denaturation), 30 s at 50°C
(annealing), and 4.0 min at 60°C
(extension); followed by 10 min of
final extension. The two PCR
products were cleaved with the indicated
restriction enzymes and
cloned into pUC19 cut with
EcoRI and
XbaI. The resulting plasmid
was cut with
SstI and
an
SstI fragment containing a kanamycin
resistance cassette
from p34S-Km (
24) was inserted. The latter
construct was
electroporated (
23) into
B. cepacia DBO1 with
selection on Lagar containing kanamycin. One strain resulting
from a
double crossover, designated DBO304, was saved for analysis.
This
strain is missing the entire
ophD gene.
Transformation of phthalate by E. coli strains
carrying cloned genes.
Plasmid-containing strains were incubated
at 37°C with shaking until the optical density of the culture at 600 nm reached 0.7. The cells were harvested by centrifugation, washed
twice with 50 mM sodium/potassium phosphate buffer (pH 7.25), and
resuspended in the same buffer supplemented with 20 mM glucose and 10 mM phthalate. After overnight incubation, the cells were removed by
centrifugation and the supernatant was collected for analysis by
high-performance liquid chromatography (HPLC). A gradient of 0 to 50%
methanol in water under acidic (0.1% acetic acid) conditions with a
reverse-phase 5-µm C18 column (4.6 by 25 mm) was used to
separate the different compounds. Both retention time and UV spectra of
the metabolites were compared with those of the standard compounds.
Phthalate transport assay.
Mid-log-phase B. cepacia DBO1 grown on 10 mM phthalate or 10 mM
p-hydroxybenzoate and B. cepacia DBO304 grown on
10 mM phthalate were harvested by low-speed centrifugation at room
temperature. The cells were washed with an equal volume of 50 mM
phosphate buffer (25 mM KH2PO4 and 25 mM
Na2HPO4 adjusted to pH 6.8 with KOH) and
resuspended in the same buffer containing 10 mM glucose and 10 mM
succinate to an optical density of 1.0 at 600 nm. Cell suspensions were
gently aerated to prevent oxygen limitation. All assays were done at
25°C. Uptake was initiated by diluting cells into an equal volume of
phosphate buffer containing 100 µM
[Ring-UL-14C]phthalate (12.6 mCi/mmol; Sigma Chemical
Co., St. Louis, Mo.). Samples (0.1 ml) were removed from the reaction
mixture at various times (10 s, 30 s, 1 min, 2 min, and 3 min) and
filtered through Isopore polycarbonate membranes (0.2-µm pore size;
Millipore Corp., Bedford, Mass.). The filters were washed before and
after addition of the sample with 2 ml of phosphate buffer. Accumulated
phthalate was determined by scintillation counting of the cells
retained on the filters. Cell protein was determined by the method of
Bradford (10).
Chemicals and biosynthesis of pathway intermediates.
Phthalate and protocatechuate were of the highest quality available
(Aldrich Chemical Co., St. Louis, Mo.). cis-Phthalate dihydrodiol and 4,5-dihydroxyphthalate used as standards were synthesized by using mutant strains accumulating each compound. cis-Phthalate dihydrodiol was synthesized by culturing
B. cepacia DBO106 in MSB medium supplemented with 10 mM
phthalate and 20 mM glucose. The culture supernatant was used directly
(without extraction) as an HPLC standard. A single peak was observed at 3.7 min, which is the same retention time as that obtained for cis-phthalate dihydrodiol enzymatically synthesized from
phthalate by using purified PDR and PDO (6). Acid-catalyzed
dehydration of cis-phthalate dihydrodiol shifted the HPLC
peak to 10.7 min, the retention time of authentic 4-hydroxyphthalate
(Pfaltz and Bauer, Waterbury, Conn.). 4,5-Dihydroxyphthalate was
synthesized by culturing C. testosteroni NH1024 in MSB
medium supplemented with 10 mM phthalate, 20 mM glucose, and 20 mM
L-glutamate as described previously (60). The
culture supernatant yielded a single peak with a retention time of 7.8 min. For comparison, phthalate elutes at 15.8 min and protocatechuate
elutes at 11.7 min under the HPLC conditions used.
Nucleotide sequence accession numbers.
The nucleotide
sequence has been deposited in the GenBank database under accession no.
AF095748.
 |
RESULTS |
Cloning and location of the genes for phthalate degradation from
B. cepacia DBO1.
A cosmid library was constructed by
using partially EcoRI-digested genomic DNA from B. cepacia DBO1, the cosmid cloning vector pMMB34, and the host
E. coli strain S17-1. The cosmid clones were transferred by
conjugation from E. coli S17-1 to B. cepacia
DBO106, a mutant of strain DBO1 previously shown to lack
cis-phthalate dihydrodiol dehydrogenase (89), the
enzyme responsible for the second step in the catabolic pathway (Fig.
1). One cosmid clone of the 2,000 tested
was able to complement the mutation in B. cepacia DBO106.
Digestion of this cosmid clone (pGJZ1301) with EcoRI, the
cloning enzyme, indicated that at least eight EcoRI fragments totaling approximately 25 kb had been cloned into pMMB34. A
subclone (pGJZ1303) containing a 1.6-kb EcoRI fragment from pGJZ1301 allows DBO106 to grow on phthalate.

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FIG. 1.
Catabolic pathway for the metabolism of phthalate to
protocatechuate by B. cepacia DBO1. The genes for each
enzyme have been given the designation oph for
o-phthalate degradation.
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Although pGJZ1301 contains
ophB, it does not contain all of
the other genes needed for the phthalate catabolic pathway.
Initial
biotransformation experiments with
E. coli
S17-1(pGJZ1301) grown
on glucose in the presence of phthalate
showed no disappearance
of phthalate or appearance of a catabolic
intermediate. This suggests
that one or both of the genes for the first
step in the catabolic
pathway is missing or that they are not expressed
in
E. coli.
To explore this further, three oligonucleotides
corresponding
to the N-terminal and C-terminal sequences of PDR
(designated
PDR-N and PDR-C) and the N-terminal sequence of PDO
(designated
PDO-N) were synthesized. In Southern hybridization
experiments,
both PDR-N and PDR-C hybridize to a 9.2-kb
EcoRI fragment and
a 3.2-kb
SphI fragment of
pGJZ1301. The 3.2-kb
SphI fragment was
subsequently
subcloned into pGEM7Zf(

) and designated pGJZ1305.
This data places
the
ophA1 gene at least 5.5 kb away from the
ophB
gene (Fig.
2). No hybridization was
detected between PDO-N
and pGJZ1301, suggesting that the
ophA2 gene is not present on
this cosmid clone.

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FIG. 2.
Complementation tests were done to determine the
locations of the genes for phthalate degradation from B. cepacia DBO1. Abbreviations: PCA, protocatechuate; DHP,
4,5-dihydroxyphthalate; DHDP, cis-phthalate dihydrodiol; B,
BamHI; E, EcoRI; H, HindIII; M,
MluI; N, NspV; S, SphI; St,
SstI. Arrows indicate the direction of transcription of the
lac promoter on the vector. The gray bars under the
consensus map indicate other regions described in the text: the 3.2-kb
SphI fragment on the left is pGJZ1305, and the 1.6-kb
EcoRI fragment on the right is pGJZ1303.
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A second cosmid library was prepared with partially
Sau3A1-digested, size-fractionated total genomic DNA and the
cosmid pHC79.
By screening the new library with the 3.2-kb
SphI fragment from
pGJZ1305 containing
ophA1, one
new clone was obtained, while screening
with the 1.6-kb
EcoRI fragment from pGJZ1303 containing
ophB
resulted
in three separate clones being obtained. None of these four
clones
in
E. coli were able to transform phthalate. This
suggests that
either
ophA1 and
ophA2 are not
closely linked or that one or both
of these genes are not expressed
well in
E. coli. Assuming that
ophA1 and
ophA2 may be distantly linked, two overlapping cosmid
clones
were examined in more detail. These two clones, pGJZ1311
and pGJZ1312,
overlap by 1.9 kb, and each contains approximately
40 kb of cloned DNA;
thus, together they represent approximately
80 kb of contiguous DNA
from
B. cepacia DBO1 (Fig.
2). An 8.2-kb
EcoRI
fragment from pGJZ1311 was subcloned into pRK415 to represent
the left
side of the overlapping region (designated pGJZ1313).
An
SstI deletion was constructed of pGJZ1312 to represent the
right side of the overlapping region (designated pGJZ1314). These
two
compatible plasmids were transformed into the same
E. coli DH5

strain and tested for the ability to transform
phthalate.
Protocatechuate was detected in the culture supernatant,
indicating that these two plasmids together contain all of the
genes
necessary for the first three steps of phthalate
degradation (Fig.
1). To locate the exact positions of the four genes
needed for
this catabolic transformation, several smaller
subclones were
prepared and tested. A 5.1-kb (partial)
SphI fragment and an internal
1.6-kb
SphI-
BamHI fragment were subcloned
separately from pGJZ1313
into pRK415 and designated pGJZ1315
and pGJZ1317, respectively
(Fig.
2). A 3.4-kb
NspV, a
1.6-kb
BamHI-
NspV, and a 1.1-kb
MluI-
NspV
fragment were subcloned
separately from pGJZ1312 into pGEM7Zf(

)
and designated
pGJZ1316, pGJZ1318, and pGJZ1320, respectively
(Fig.
2).
Different combinations of these five plasmids were inserted
into
E. coli, and the resulting strains were tested for the
ability
to transform phthalate to a detectable intermediate.
E. coli containing
pGJZ1315 and pGJZ1316 is able to
transform phthalate to protocatechuate,
delimiting the smallest region
necessary for the four target genes.
E. coli
containing the smaller plasmid pGJZ1317 along with pGJZ1316
was only
able to transform phthalate to 4,5-dihydroxyphthalate.
This
indicates that all or part of the gene (
ophC) for
4,5-dihydroxyphthalate
decarboxylase must be present
in the region deleted from pGJZ1315
to form pGJZ1317. Similarly,
E. coli containing pGJZ1317 and pGJZ1318
is only able
to transform phthalate to
cis-phthalate dihydrodiol.
This indicates that all or part of the gene (
ophB) for
cis-phthalate
dihydrodiol dehydrogenase must be present in
the region deleted
from pGJZ1316 to form pGJZ1318.
E. coli
containing pGJZ1317 and
pGJZ1320 is not able to transform phthalate to
any detectable
products. This indicates that pGJZ1317 and pGJZ1318 must
contain
the two genes (
ophA1 and
ophA2) needed
for phthalate dioxygenase.
It was shown above that
ophA1 could be localized to a 3.2-kb
SphI
fragment by oligonucleotide probing. This places
ophA1 on pGJZ1317
and means that
ophA2 must be
present on pGJZ1318. It is interesting
to note that this means that the
two genes necessary for the first
step in the catabolic
pathway are located at least 6.5 kb apart.
In addition, there is at
least 2.0 kb of space between the
ophC and
ophB
genes that is not needed for the transformation of phthalate
to
pathway
intermediates.
Nucleotide sequence of the genes for phthalate degradation.
To
characterize the genes necessary for phthalate degradation in more
detail at the molecular level, the two regions necessary for the
conversion of phthalate to protocatechuate were sequenced. A diagram of
this sequence is shown at the top of Fig.
3. Open reading frames were assigned gene
names based on the biochemical data presented above. It is important to
note that ophA1 is transcribed in the opposite direction
from that of orf1, ophD, and ophC.

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FIG. 3.
Different organization of the genes involved in
phthalate degradation from B. cepacia DBO1, P. putida NMH102-2 (66), and C. testosteroni
M4-1 (51). Designations: ophA1 and
pht2, genes coding for phthalate dioxygenase reductase;
ophA2 and pht3, genes coding for phthalate
dioxygenase; ophB, pht4, and phtC,
genes coding for 4,5-dihydro-4,5-dihydroxyphthalate dehydrogenase;
ophC, pht5, and phtD, genes coding for
4,5-dihydroxyphthalate decarboxylase; pht3 and
phtR, genes coding for putative phthalate transporter;
orf1 and ophD, genes coding for products that
show homology to the putative phthalate transporter. Abbreviations: B,
BamHI; E, EcoRI; H, HindIII; K,
KpnI; P, PstI; N, NspV; S,
SacI; Sm, SmaI; Sp, SphI. The dashed
lines representing phtC and half of phtR indicate
that the sequences for these have not been determined.
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Analysis of a putative gene for phthalate transport.
A gene
(ophD) for a putative phthalate transporter was identified
in the nucleotide sequence upstream from ophC, which encodes 4,5-dihydroxyphthalate decarboxylase. Initially this gene was identified through its similarity to other known proteins involved in
transport of substrates into the cell and also through its high
similarity to a suspected phthalate transporter cloned and sequenced
from P. putida (66). However, the gene for this
putative transporter in B. cepacia DBO1 is split into two
parts due to a frameshift, into an initial, very small, orf1
and the longer ophD (Fig. 2). This frameshift could be due
to a sequence or cloning artifact. Two experiments were performed to
prove that this was not the case. The region containing the suspected
frameshift was PCR amplified from genomic DNA isolated from B. cepacia DBO1, ATCC 29424, and ATCC 17616. (DBO1 and ATCC 29424 are
the same strain except that DBO1 passed through the laboratories of a
chain of investigators before reaching our lab, while ATCC 29424 was obtained directly from the ATCC.) Each PCR product was then sequenced directly by using the same primers as were used for amplification. The
nucleotide sequences of this region in DBO1 and ATCC 29424 are
identical, showing that the sequence is correct and not the result of a
base change occurring during cloning or subcloning of the genes. This
also means that the base change is not due to a recent
laboratory-acquired mutation since the DBO1 sequence is identical to
the ATCC 29424 sequence. On the other hand, the nucleotide sequence of
this region from ATCC 17616 is identical to that from DBO1 except for
one additional base: an A found between bases 300 and 301 of
orf1 in the DBO1 sequence. The additional base places
orf1 in frame with ophD in ATCC 17616. This
experiment demonstrates that the missing base is not due to a sequence
error since it can be detected in ATCC 17616. This also means that for some reason DBO1, but not ATCC 17616, has lost a single base in this
particular gene, splitting it into two halves. This base change does
not seem to have an effect on the growth of DBO1 on phthalate since
growth curves for DBO1 and ATCC 17616 on phthalate as the sole carbon
source are identical (data not shown).
A second experiment was performed to demonstrate that
ophD
is actually translated (and also to confirm that
orf1 and
ophD are translationally separate, confirming the missing
base). A
1.5-kb
BamHI-
HindIII fragment
containing
orf1 and
ophD was cloned
into the
expression vector p
Trc99A. An in vitro
transcription-translation
experiment was then performed, and the
products were analyzed
by SDS-PAGE (Fig.
4). Two peptides are produced by this
clone
in contrast to the negative control: one small peptide with a
molecular mass of approximately 13 kDa and a large peptide with
a
molecular mass of approximately 38 kDa. These two molecular
masses are
consistent with those predicted for the proteins encoded
by
orf1 and
ophD: 12.7 and 37.2 kDa, respectively.
However, based
on the difference in signal intensities, the gene
products are
produced in different quantities. Orf1 is produced in a
much larger
quantity than OphD. This is most likely due to the presence
of
a ribosome binding site in front of
orf1, while
translation of
ophD is dependent on translational coupling
since the putative
initiation codon of
ophD (ATG) overlaps
the stop codon (TGA) of
orf1.

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FIG. 4.
SDS-PAGE of an in vitro transcription-translation of a
clone containing orf1 and ophD. Lane 1, pTRC99A
control; lane 2, pGJZ1321. The numbers on the left are the running
positions of the molecular weight markers (from top to bottom:
ovalbumin, carbonic anhydrase, -lactoglobulin, and lysozyme; in
thousands). The arrows on the right indicate the two translated
proteins, Orf1 and OphD.
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One question that remains is whether
ophD is actually
required for growth on phthalate by DBO1. This would provide
physiological
proof that OphD actually functions as a phthalate
transporter.
The DBO1
ophD gene region was deleted and
replaced with a kanamycin
resistance gene cassette by double reciprocal
recombination as
described in Materials and Methods. The resulting
mutant strain
(designated DBO304) grows normally on phthalate with a
doubling
time in liquid culture (MSB medium plus phthalate) equivalent
to the wild-type strain. This suggests that
ophD is
dispensable
for growth on phthalate. Phthalate transport assays were
performed
to prove that
ophD is not involved in the
transport of phthalate
into the cell (Fig.
5). DBO1 grown on phthalate rapidly
transports
phthalate into the cell (3.2 nmol/min/mg of cells). DBO1
grown
on
p-hydroxybenzoate does not transport phthalate into
the cell
at any measurable rate, demonstrating that this is a
phthalate-inducible
activity. On the other hand, the
ophD
knockout mutant, DBO304,
transports phthalate at a rate identical to
that of DBO1. This
indicates that
ophD, although it is
similar to known genes encoding
permeases, is not involved in phthalate
uptake.

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|
FIG. 5.
Uptake of phthalate by B. cepacia DBO1 (wild
type) grown on phthalate ( ) and p-hydroxybenzoate ( )
and B. cepacia DBO304 (ophD mutant) grown on
phthalate ( ). Error bars represent the standard deviation from three
independent assays.
|
|
 |
DISCUSSION |
Many genes for the degradation of aromatic compounds are organized
into operons of functional units (3, 25, 30, 66, 82). This
does not appear to be the case for the B. cepacia DBO1 genes
for phthalate degradation described here. The five structural genes
coding for the conversion of phthalate to protocatechuate and a
nonfunctional permease are arranged in at least three transcriptional units based on orientation: ophA1, ophDC, and
ophA2B. In fact, the two genes (ophA1 and
ophA2) encoding the oxygenase and reductase components of
phthalate dioxygenase, the first step in the pathway, are located at
opposite ends of the sequenced region, approximately 7.0 kb apart. This
gene organization is not a unique feature of DBO1 as another B. cepacia strain, ATCC 17616, which also degrades phthalate, has an
identical restriction fragment length polymorphism pattern when probed
with the cloned genes described here (13). The genes for
phthalate degradation from P. putida NMH102-2 have also been
cloned and sequenced (Fig. 3). The genes in this case were identified
simply by sequence analysis, and their functions were predicted by
homology to genes encoding other proteins. The P. putida
genes are clustered and transcribed in the same direction in the order
pht1 (coding for permease), pht2 (phthalate
oxygenase reductase), pht3 (phthalate oxygenase),
pht4 (cis-phthalate dihydrodiol dehydrogenase),
and pht5 (4,5-dihydroxyphthalate decarboxylase). The order
of the genes is thus the same as the order in the catabolic pathway.
Three different transcripts were identified by Northern blotting, and
the authors' analysis of the nucleotide sequence suggested promoters
in front of pht1, pht3, and pht5.
However, although the genes for phthalate degradation in P. putida NMH102-2 and B. cepacia DBO1 are closely related
based on their nucleotide sequence (see below), one cannot postulate a
simple mechanism for the evolutionary rearrangement of the genes going
from one strain to another. It is interesting to note that the genes
for phthalate degradation are present on a plasmid in P. putida NMH102-2 (64) and in the chromosome of B. cepacia DBO1 and ATCC 17616 (16, 87). The gene for
4,5-dihydroxyphthalate decarboxylase from C. testosteroni
M4-1 has also been cloned and sequenced (51). In this case,
the authors suggested that a putative transport gene is located
upstream (based on a partial nucleotide sequence) and a gene for
cis-phthalate dihydrodiol dehydrogenase is located over 2 kb
away (based on functional assays). Although the genes for the oxygenase
and the reductase were not located and the complete nucleotide
sequences of two of the three genes located are not available, the gene
organization postulated for C. testosteroni M4-1 is similar
to that identified here for B. cepacia DBO1.
The two components of B. cepacia DBO1 phthalate dioxygenase,
PDO and PDR, have been well studied (see the introduction). The corresponding genes have been identified in the present work by activity assays of subclones and by correlation with N- and C-terminal sequences of the purified proteins. The crystal structure of PDR has
been solved at a 2.0-Å resolution (20) by using a partial amino acid sequence obtained through protein sequencing of the purified
protein. The deduced amino acid sequence presented here will enable a
more defined examination of the structure of the reductase. Since
phthalate dioxygenase belongs to a family of oxygenases comprised of
two components (Fig. 6), it should be possible to extend by analogy what is known about PDR and PDO to other
members of this family. For instance, the crystal structure of PDR
reveals an FMN binding domain in the N terminus, an NAD binding domain
in the center, and a plant-type ferredoxin [2Fe-2S] domain in the C
terminus. One arginine, one tyrosine, one serine, and one leucine are
conserved in this reductase family for binding the FMN-isoalloxazine
ring (Fig. 7). The PDR crystal structure shows that Tyr-58 contacts the si face of the flavin while
Phe-226 stacks against the re side of the flavin ring
(20). The consensus sequence XRGGS (where X is G or S) for
binding the phosphate of FMN is conserved in all of the reductases but
CbaB (Fig. 7). Arg-81 in PDR binds intimately to the FMN phosphate
group and contributes to the specificity for FMN over flavin adenine
dinucleotide. The fingerprint sequence GXGXXP for NADH or NADPH binding
can also be detected, but in the case of this family, the consensus is the larger sequence XGGIGZTP (where X is A or C and Z is I or V) (Fig.
7). Pro-126 in this sequence contacts the bound nicotinamide (20). Finally, there are a number of conserved amino acids
found around the conserved [2Fe-2S] chloroplast-type ferredoxin
binding site (Fig. 7).

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FIG. 6.
Dendrograms showing the relationship of OphA1, OphA2,
and OphB to similar proteins. Reference strains include B. cepacia DBO1 (this work), P. putida NMH102-2
(66), Flavobacterium sp. strain ATCC 39823 (50), P. pseudoalcaligenes POB310
(22), Pseudomonas sp. strain ATCC 19151 (11), C. testosteroni T2 (42),
Alcaligenes sp. strain BR60 (58), P. pseudoalcaligenes KF707 (31), P. putida F1
(88), Pseudomonas sp. strain D12 (25),
and A. calcoaceticus BD413 (61).
|
|

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FIG. 7.
Conserved regions in PDR, PDO, and related proteins. The
consensus shown below the aligned sequences is where all sequences are
identical. An asterisk indicates those positions where all but one
sequence is identical. A period indicates a gap in the aligned
sequences. The number before each sequence is the distance from the
N-terminal end of the protein.
|
|
The oxygenase components of this two-component dioxygenase family are
also related, at approximately the same level of similarity as seen
with the reductase components (Fig. 6). All of the dioxygenases have
the consensus sequence (CXHX16-17CXXH) which has been proposed for binding a Rieske-type [2Fe-2S] center (55,
62). Figure 7 shows this region for sequences in the same family
as PDO. In addition to the Rieske-type [2Fe-2S] center, the oxygenase components also contain a mononuclear iron. In many oxygenases, one
glutamate, one aspartate, one tyrosine, and two histidines are
conserved for binding mononuclear iron (40). However, in phthalate dioxygenase and related enzymes, the glutamate and the tyrosine are not conserved (Fig. 7). The glutamate in some cases is
conservatively replaced with an aspartate. The conserved amino acids
Glu-214, Asp-219, Tyr-221, His-222, and His-228 of TodC1 (the
subunit of the terminal oxygenase component of toluene dioxygenase)
from P. putida F1 were independently replaced with alanine
residues by site-directed mutagenesis (40). Toluene dioxygenase with mutations at Glu-214, Asp-219, His-222, or His-228 completely lost activity. However, TodC1 with an alanine substitution at Tyr-221 retained 42% activity. These laboratory-generated data are
consistent with the observation provided by nature in the amino acid
sequence alignments shown in Fig. 7: the tyrosine is dispensable.
OphB is quite dissimilar from most other cis-dihydrodiol
dehydrogenases involved in aromatic compound degradation (Fig. 6). OphB
groups with the similar enzyme Pht4 from P. putida NMH102-2 (66) and CbaC from Alcaligenes sp. strain BR60
(58). However, OphB is 50 amino acids shorter than Pht4.
That these three proteins cluster together into a new family of
dihydrodiol dehydrogenases is probably due to the fact that their
substrate is a compound with the dihydrodiol moiety opposite a carboxyl
on the aromatic ring. On the other hand, OphB shows only 41 to 46%
similarity to dihydrodiol dehydrogenases that act on neutral aromatic
substrates such as BphB (biphenyl cis-dihydrodiol
dehydrogenase) from Pseudomonas pseudoalcaligenes KF707
(31) and TodD (toluene cis-dihydrodiol dehydrogenase) from P. putida F1 (88) and that
act on acidic substrates such as BenD (benzoate
cis-dihydrodiol dehydrogenase) from Acinetobacter
calcoaceticus BD413 (61) and TsaC
(p-toluenesulfonate cis-dihydrodiol
dehydrogenase) from C. testosteroni T2 (42).
The enzyme responsible for the third step of the catabolic pathway,
4,5-dihydroxyphthalate decarboxylase, has been purified from both
B. cepacia DBO1 and C. testosteroni NH1000
(59, 72). The C. testosteroni enzyme has a
molecular mass of 38 kDa as determined by sodium dodecyl
sulfate-polyacrylamide gel electrophoresis (SDS-PAGE) and a molecular
weight of 150,000 as determined by gel filtration through Sephadex
G-200 (59). However, the same enzyme purified from B. cepacia DBO1 has a molecular mass of 66 kDa as determined by
SDS-PAGE and a molecular weight of 420,000 as determined by gel
filtration through Sepharose 6B (72). The calculated
molecular mass for 4,5-dihydroxyphthalate decarboxylase
(ophC gene product) based on the nucleotide sequence
presented above is 37.4 kDa. This is in excellent agreement with that
calculated (37.2 kDa) for the decarboxylase based on the nucleotide
sequence of phtD from C. testosteroni M4-1
(51). It is also in agreement with that calculated (37.8 kDa) for the decarboxylase based on the corrected sequence of
pht5 from P. putida NMH102-2. (We suspect that
the NMH102-2 nucleotide sequence is missing a base immediately after
position 6387 based on a comparison with the sequences from B. cepacia DBO1 and C. testosteroni M4-1.) These data
correlate well with those derived from the purified enzyme from
C. testosteroni NH1000, a 37- to 38-kDa monomer. However,
the molecular mass based on the data derived from the purified
decarboxylase from DBO1 is almost twice that derived from the
nucleotide sequence. Further investigation is required to resolve this discrepancy.
The gene for a putative transporter (ophD) was identified by
the similarity of the deduced protein to known or suspected aromatic acid transporters such as PcaK for protocatechuate and
p-hydroxybenzoate (63), BenK for benzoate
(19), VanK for vanillate (18), TfdK for
2,4-dichlorophenoxyacetate (53), HppK (5) and
MhpT (28) for m-hydroxyphenylpropionate, HpaX for
p-hydroxyphenylacetate (71), and Pht1 for
phthalate (66). However, it is obvious through comparisons
with these other related gene products that a frameshift mutation
caused the production of two peptides (Orf1 and OphD). This frameshift
is present in B. cepacia DBO1 and B. cepacia ATCC
29424 (ostensibly identical strains) but not in B. cepacia
17616. Both Orf1 and OphD are produced, as evidenced by in vitro
transcription-translation, with a noticeable difference in the levels
of protein produced (Fig. 5). Although this frameshift separates the
leader sequence from the main body of the protein, the split occurs
after two putative membrane-spanning regions of the protein. Since
phthalate is a negatively charged compound at neutral pH, it is highly
likely that it must be transported into the cell and thus a transport
protein would be required. It has been shown that a signal sequence is
not required for lactose permease to insert itself into the cell
membrane and to function normally (7), and this may also be
the case for phthalate permease in DBO1. However, a knockout mutation
of ophD results in no detectable loss of the ability to
transport phthalate into the cell (Fig. 5), demonstrating that OphD is
not involved in phthalate transport in DBO1. One possibility is that a
related aromatic acid transporter can take its place, as has been shown
in Acinetobacter for the transport of aromatic acids
(18, 21). However, no phthalate uptake was detected when
DBO1 was grown on p-hydroxybenzoate (the phthalate and
p-hydroxybenzoate catabolic pathways intersect at protocatechuate), demonstrating not only that phthalate transport is a
phthalate-inducible phenotype but also that related aromatic acid
transporters are not involved.
 |
ACKNOWLEDGMENTS |
We thank Teruko Nakazawa, David Ribbons, and Thomas Lessie for
supplying strains; Chris Batie, Carl Correll, David Ballou, and Martha
Ludwig for providing N- and C-terminal sequences of purified PDO and
PDR; and Ruilong Liu, Ravindra Ramadhar, and Michael Murillo for
technical assistance.
This work was supported by a National Science Foundation Young
Investigator Award to G.J.Z. and cooperative agreement CR822634 from
the U.S. Environmental Protection Agency Gulf Breeze Environmental Research Laboratory.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Biotechnology
Center for Agriculture and the Environment, Foran Hall, 59 Dudley Rd., Cook College, Rutgers University, New Brunswick, NJ 08901-8520. Phone:
(732) 932-8165, ext. 320. Fax: (732) 932-0312. E-mail: zylstra{at}aesop.rutgers.edu.
 |
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