Previous Article | Next Article 
Applied and Environmental Microbiology, July 2001, p. 3304-3308, Vol. 67, No. 7
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.7.3304-3308.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
Organization and Regulation of meta
Cleavage Pathway Genes for Toluene and o-Xylene Derivative
Degradation in Pseudomonas stutzeri OX1
Fabio L. G.
Arenghi,1
Davide
Berlanda,1
Enrica
Galli,1
Guido
Sello,2 and
Paola
Barbieri1,3,*
Dipartimento di Genetica e di Biologia dei
Microrganismi1 and Dipartimento di
Chimica Organica e Industriale,2
Università degli Studi di Milano, Milano, and
Dipartimento di Biologia Strutturale e Funzionale,
Università dell'Insubria, Varese,3 Italy
Received 29 January 2001/Accepted 2 May 2001
 |
ABSTRACT |
Pseudomonas stutzeri OX1 meta pathway genes
for toluene and o-xylene catabolism were analyzed, and loci
encoding phenol hydroxylase, catechol 2,3-dioxygenase,
2-hydroxymuconate semialdehyde dehydrogenase, and 2-hydroxymuconate
semialdehyde hydrolase were mapped. Phenol hydroxylase converted a
broad range of substrates, as it was also able to transform the
nongrowth substrates 2,4-dimethylphenol and 2,5-dimethylphenol into
3,5-dimethylcatechol and 3,6-dimethylcatechol, respectively, which,
however, were not cleaved by catechol 2,3-dioxygenase. The identified
gene cluster displayed a gene order similar to that of the
Pseudomonas sp. strain CF600 dmp operon for
phenol catabolism and was found to be coregulated by the
tou operon activator TouR. A hypothesis about the
evolution of the toluene and o-xylene catabolic pathway in
P. stutzeri OX1 is discussed.
 |
TEXT |
In bacteria, aerobic catabolic
pathways for aromatic hydrocarbon degradation can schematically be
divided into two major biochemical steps. First, early reactions, the
so-called upper pathways or peripheral routes, channel the hydrocarbons
towards the formation of partially oxidized aromatic intermediates.
Then, dihydroxylated aromatic molecules that can undergo the cleavage
of the ring are produced and further processed to give compounds that
can enter the tricarboxylic acid cycle. Whereas a wide variety of very
different peripheral routes for the oxidation of many different
aromatic hydrocarbons exists, only a limited number of dihydroxylated
compounds that can be cleaved and productively processed to enter the
tricarboxylic acid cycle are known.
A good example of this is represented by the diversity of the
known toluene catabolic pathways. Toluene is oxidized through different
routes: via progressive oxidation of the methyl group (TOL pathway)
(6), via dioxygenation (25), or via
monooxygenations of the aromatic ring in different positions (18,
22, 31). Most of these pathways give rise to (methyl)catechols
further processed through meta cleavage pathways. At least
in one strain, Pseudomonas mendocina KR1, protocatechuate is
produced and then cleaved in intradiol position (27). The
genes coding for upper and lower pathways may be clustered in one
(32), two (6), or more (18, 29)
operons, independently but coordinately regulated.
The combination of different upper operons with one or more lower
operons can thus increase not only the number of pathways through which
a certain molecule can be degraded but also the range of substrates
utilized for growth (10), and it is recognized as a mode
for the evolution of new catabolic pathways (23, 28).
Pseudomonas stutzeri OX1 is able to utilize toluene and
o-xylene as the sole carbon and energy sources. For both
compounds the degradation proceeds through two successive
monooxygenations of the aromatic nucleus catalyzed by
toluene-o-xylene monooxygenase (ToMO) followed by extradiol
ring cleavage (3). Here we investigate the organization of
genes involved in the further degradation of toluene and
o-xylene derivatives produced by the action of ToMO.
Identification of a P. stutzeri OX1 phenol hydroxylase
activity.
The maps of pFB3401 and its derivatives (see Table
1 for a description of strains and
plasmids) are reported in Fig. 1.
Previously, a catechol 2,3-dioxygenase (C2,3O) gene was roughly mapped
to the 7.2-kb EcoRI fragment at the right end of the pFB3401
insert (3). As the ToMO-encoding operon did not contain
genes involved in the lower pathway (1, 4), it was
supposed that the C2,3O gene was part of a distinct meta
operon.

View larger version (10K):
[in this window]
[in a new window]
|
FIG. 1.
Restriction endonuclease maps of the P. stutzeri OX1 chromosomal DNA fragment cloned in pFB3401 and its
derivatives (3). pFB3401 allowed the host cells to convert
toluene, o-xylene, and their phenolic derivatives into the
corresponding ring fission products. The ToMO-encoding operon and the
regulatory gene (touR) controlling its expression are
indicated (1, 4). The point of the arrows indicates the
direction of transcription. The ability (+) or inability ( ) of the
plasmids to direct the conversion of o-cresol into ring
fission products in the absence ( ) or in the presence (+) of
touR, cloned in pRZ7085 and provided in trans, is
indicated to the right of the restriction maps. +/ , mildly positive
reaction after prolonged exposure. Abbreviations: A, ApaI;
B, BamHI; E, EcoRI; H, HindIII; N.A.,
not applicable; P, PstI; S, SacI; X,
XhoI; Xb, XbaI. Only relevant restriction sites
are indicated.
|
|
In an attempt to verify if the C2,3O expression was controlled by the
ToMO operon transcriptional activator TouR,
E. coli JM109(pFB1021) cells were transformed with the compatible plasmid
pRZ7085 carrying the regulatory gene
touR in order to assay
a
possible increase in C2,3O activity upon exposure to the phenolic
compounds that were demonstrated to be TouR effectors (
1).
Surprisingly, a yellow color, indicative of the accumulation of
a ring
fission product, developed in cultures exposed for 1 h
to
o-cresol (Fig.
1). When the same experiment was performed
with
cells carrying pRZ7085 and pFB1036, a faint yellow color was
detectable
only after prolonged incubation of more than 24 h. These
results
suggested that in the pFB1021 insert, a gene or genes coding
for
a phenol hydroxylase activity, able to catalyze the conversion
of
the phenolic compound into a catechol, might be
present.
Mapping of meta pathway genes.
To localize genes
involved in meta pathway reactions, several overlapping
fragments from the insert of pFB1021 and of pFB3411 were subcloned in
Escherichia coli IPTG
(isopropyl-
-D-thiogalactopyranoside)-inducible vectors.
The insert of pFB3411 partially overlapped and extended beyond the
right end of pFB3401, and it was unable to direct the conversion of
both hydrocarbons and phenols into catechols (3). The
plasmids obtained were examined for phenol hydroxylase (PH), C2,3O,
2-hydroxymuconate semialdehyde hydrolase (HMSH), and 2-hydroxymuconate semialdehyde dehydrogenase (HMSD) activities, and the encoding loci
were mapped (Fig. 2). PH activity was
determined in resting cells by monitoring the decrease in concentration
of phenol in the medium, using a colorimetric assay described
previously (3, 15). C2,3O, HMSH, and HMSD were assayed in
crude extracts by measuring the formation rate (17) or the
decrease (21) of the catechol ring fission product.

View larger version (14K):
[in this window]
[in a new window]
|
FIG. 2.
Restriction endonuclease maps of DNA fragments subcloned
from pFB1021 (pJ and pBZ series) and from pFB3411 (pVS series). Only
the plasmids containing the minimal region coding for PH, C2,3O, HMSH,
and HMSD are reported. The black arrowheads indicate the position of
the Plac of the vector. To the right of the restriction
maps, the enzymatic activities expressed from the indicated plasmids in
uninduced ( ) or IPTG-induced (+) E. coli JM109 cells are
reported. At the bottom, the map obtained by subcloning, Southern, and
sequence analyses (see text for details) displaying the gene
arrangement and the putative promoter is shown. The presence of the
gene indicated in parentheses can be hypothesized but has not been
investigated. Abbreviations: B, BamHI; E, EcoRI;
H, HindIII; M, MluI; ND, not detectable; P,
PstI; S, SacI; Sm, SmaI; X,
XhoI; Xb, XbaI. Only relevant restriction sites
are indicated.
|
|
Quantitative assays performed on cells carrying the plasmids depicted
in Fig.
2 or plasmids carrying the same inserts cloned
in the opposite
direction with respect to the
Plac promoter of
the vector
(not shown) suggested that the genes mapped are transcribed
in the same
direction, from the left to the right with respect
to the maps shown in
Fig.
2.
Substrate range of the cloned phenol hydroxylase.
Plasmids
pJEX159 and pJSX148 were also examined and found not to confer upon
cells the ability to convert toluene and o-xylene to
phenolic compounds. The activity cloned in pJEX159 and pJSX148 is thus
specific for the introduction of a hydroxyl group on phenolic compounds. The substrate range of the cloned PH was investigated in
E. coli JM109(pJSX148) cells. Specific activities are
reported in Table 2 and found comparable
for all the phenols tested. p-Cresol, 2,4-dimethylphenol
(2,4-DMP), and 3,4-DMP, due to the presence of a substituent
para to the hydroxyl group, were undetectable in this assay.
High-pressure liquid chromatography (HPLC) analyses, however,
demonstrated that these phenols were oxidized by the cloned enzyme.
View this table:
[in this window]
[in a new window]
|
TABLE 2.
Substrate range and reaction product identification for
the P. stutzeri OX1 PH from IPTG-induced E. coli
JM109(pJSX148) cells
|
|
To identify the reaction products, the supernatants of
E. coli JM109(pJSX148) cell reactions, with different phenols
supplied
at a final concentration of 0.5 to 3 mM depending on the
compound,
were extracted with a 1/5 volume of acetonitrile; the organic
phase was filtered, deoxygenated with N
2, and then analyzed
by
reverse-phase HPLC; and the retention times were compared with
those
of authentic standards (Table
2). The supernatants were
also treated
with partially purified C2,3O expressed from pBZ3120
and checked by
HPLC analyses for the complete disappearance of
PH reaction products.
The spectral properties of the yellow compounds
produced after C2,3O
reaction were identical to those determined
for the extradiol ring
fission products obtained from authentic
standards of catechol,
3-methyl-, 4-methyl-, and 3,4-dimethylcatechol
(data not shown). The
further data confirmed the identification
of the reaction products and
suggested that
m-cresol and 3,4-DMP
were mainly converted
into 3-methyl- and 3,4-dimethylcatechol,
respectively, although the
presence of small amounts of other
isomers could not be excluded. The
reactions catalyzed by PH thus
appear to be redundant with respect to
those catalyzed by ToMO,
at least as regards the phenols derived from
toluene and
o-xylene.
Identification of the products derived from 2,4-DMP and
2,5-DMP.
The P. stutzeri OX1 PH acts on a very broad
range of substrates, as it was able to produce more polar compounds,
presumably dimethylcatechols, even from 2,4-DMP, 3,5-DMP, and 2,5-DMP,
which are not growth substrates for P. stutzeri OX1. As
standards of 3,5- and 3,6-dimethylcatechols for HPLC analyses were not
available, we set out to identify these compounds by nuclear magnetic
resonance (NMR). The reaction products obtained upon exposure of
E. coli JM109(pJSX148) cells to 3 mM 2,4-DMP and 2,5-DMP
were extracted from the supernatants with ethyl acetate, separated by
flash column chromatography, and analyzed by 1H-NMR. The
protonic signals had the following features:
6.55 (s, 2H),
5.20 (br s, 2H, D2O); and
2.25 (s, 6H) for the product obtained from 2,4-DMP and
6.60 (s, 2H),
5.60 (br s, 2H,
D2O), and
2.23 (s, 6H) for the product obtained from
2,5-DMP. Reactions of 5.20 and 5.60 protons, respectively, with
D2O confirmed the assignment of the signals to hydroxyl
groups. The registered spectra were consistent with those reported in
literature for 3,5-dimethylcatechol (26) and
for 3,6-dimethylcatechol (14). Thus, the P. stutzeri OX1 PH displays precise regioselectivity, as it produces
catechols from all the phenols tested. The product from 3,5-DMP was not analyzed.
The dimethylcatechols from 2,4-DMP, 2,5-DMP, and, presumably, 3,5-DMP
did not disappear in the supernatants treated with C2,3O,
nor did the
typical yellow color of extradiol ring fission products
develop (Table
2). To further assess if the
P. stutzeri C2,3O
was unable to
catalyze the cleavage of 3,5- and 3,6-dimethylcatechol,
specific
activities were measured and found to be 0.01 and 0.05%,
respectively,
of the activity measured using catechol as the reaction
substrate.
In
P. stutzeri OX1, 2,4-DMP and 2,5-DMP were derived from
the ToMO-catalyzed hydroxylation of
m-xylene and
p-xylene and are
not used for growth (
2,
3).
Thus, in
P. stutzeri OX1, catechol
2,3-dioxygenase
represents the bottleneck for
m-xylene and
p-xylene
degradation through the monooxygenation
pathway.
Arrangement of the PH genes.
The length of the minimal DNA
region to detect PH activity in E. coli cells suggested that
the P. stutzeri OX1 PH might be a multicomponent enzyme
system. Southern hybridization analyses of pJEX159 were thus performed
using the dmp genes coding for the subunits of the
Pseudomonas sp. strain CF600 multicomponent PH
(16) as probes. Hybridization signals were detected when pJEX159 was probed with dmpL, dmpN, dmpO, and
dmpP but not when the probes were dmpK and
dmpM (data not shown).
Sequencing of approximately 1,000 nucleotides (accession no.
AJ309239)
at the 5' end of the PH locus revealed a sequence
identical to the

12,

24 consensus of
54-dependent promoters followed
by a putative open reading frame
(ORF) (nucleotides 247 to 507) whose
deduced amino acid sequence
shared 62.6% identity (74% similarity) to
the
Pseudomonas sp.
strain CF600 PH DmpK subunit. The map
obtained is depicted in
Fig.
2 and evidenced a conserved gene order
with respect to that
of the
Pseudomonas sp. strain CF600 PH
gene cluster (
16). In
the
Pseudomonas sp.
strain CF600 PH, DmpK is dispensable for the
enzyme activity in vitro
and it was suggested to play a role in
assembly of the active form of
the enzyme (
20). In pJSX148,
which expresses a high level
of PH activity, the DmpK-like ORF
is partially deleted, suggesting that
its integrity is not essential
for the enzyme to be assembled correctly
enough to
function.
The
P. stutzeri meta operon putative promoter is located in
the 1.1-kb
EcoRI fragment deleted in pFB1036 (Fig.
1), and
its
deletion may explain the scarce and delayed production of extradiol
ring fission products observed in cells carrying pFB1036 and
touR in
trans and exposed to
o-cresol.
PH and C2,3O are controlled by TouR.
The ability of pFB1021 to
direct the conversion of phenols into ring cleavage products when in
trans with pRZ7085 (Fig. 1) together with the presence of a
putative
54-dependent promoter upstream from the
PH-encoding genes (Fig. 2) suggested that the expression of the
identified meta pathway genes could also be controlled by
TouR, the phenol-responsive regulator of the tou upper
operon (1). The regulatory gene touR was thus
integrated in the Pseudomonas putida PaW340 chromosome by
means of minitransposon (8, 11), and the recombinant
strain was transformed with pFB3411. Upon induction with
o-cresol, the specific activities of PH and C2,3O increased
30- and 8-fold, respectively, in comparison to uninduced samples (Table
3). The inability of P. putida
PaW340(pFB3411) to convert phenolic compounds into ring cleavage
products (3) can thus be ascribed to the absence of a
suitable transcriptional activator.
Conclusive remarks.
The P. stutzeri OX1 genes
coding for toluene and o-xylene catabolism are organized
into at least two operons, one coding for the
toluene-o-xylene-monooxygenase (4) and another
for phenol catabolism, the latter organized as the
Pseudomonas sp. strain CF600 dmp operon in which
the multicomponent PH genes are followed by C2,3O, HMSH, and HMSD
encoding genes (19). Both operons are inducible by phenols
under the control of a
54-dependent promoter and TouR.
The presence of a dmp-like operon together with a
phenol-responsive regulator in the P. stutzeri OX1 genome
suggests that, in this strain, the toluene and o-xylene catabolic pathway evolved by vertical expansion of a preexisting route
for phenol catabolism through the incorporation of the ToMO gene
cluster (Fig. 3). In this perspective,
the redundancy between the hydroxylation of phenols catalyzed by ToMO
and the PH activity can be fortuitous due to the acquisition of a
monooxygenase endowed with a very broad range of substrates. The scarce
specificity of
54-dependent promoters (13),
which makes the PToMO promoter activatable by
TouR, may be a factor that contributed to the successful acquisition of
the ToMO gene cluster.

View larger version (15K):
[in this window]
[in a new window]
|
FIG. 3.
A model for the evolution of the toluene and
o-xylene catabolic pathway in P. stutzeri OX1.
See text for details. The arrows indicate the direction of
transcription. tnp, transposase-like ORF (4).
|
|
P. stutzeri OX1 is the first toluene-degrading strain in
which the toluene monooxygenase-encoding operon has been found
associated
to a
dmp-like operon. Toluene monooxygenases
similar to the
P. stutzeri OX1 ToMO have been found in other
bacterial strains (
7,
31), but they are associated with
very different lower pathways
(
12,
29). These observations
further confirm the modular organization
of aromatic hydrocarbon
catabolic pathways and suggest that the
toluene monooxygenase operon
represents an independent
module.
 |
ACKNOWLEDGMENTS |
This work was supported by the Consiglio Nazionale delle Ricerche
(Rome), grant no. CT99.00287.PF49 of the Target Project on
Environmental Biotechnology, and by the Ministero
dell'Università e della Ricerca Scientifica e Tecnologica (Rome)
under the Programma di Ricerca di Interesse Nazionale, contract
"Characterization of biodegradative enzymatic systems: oxidases and
oxygenases" to P.B.
We are grateful to V. De Lorenzo and V. Shingler, who kindly provided
the mini-Tn5 transposition systems and the dmp probes, and
to V. Valota and R. Macchi for collaboration on the experimental work.
We also thank G. Baggi for providing 3,4-dimethylcatechol.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Dip. Genetica e
Biologia dei Microrganismi, Via Celoria 26, 20133 Milano, Italy. Phone: 39-02.26605227. Fax: 39-02.2664551. E-mail:
Paola.Barbieri{at}unimi.it.
 |
REFERENCES |
| 1.
|
Arenghi, F. L. G.,
M. Pinti,
E. Galli, and P. Barbieri.
1999.
Identification of the Pseudomonas stutzeri OX1 toluene-o-xylene monooxygenase regulatory gene (touR) and of its cognate promoter.
Appl. Environ. Microbiol.
65:4057-4063[Abstract/Free Full Text].
|
| 2.
|
Barbieri, P.,
L. Palladino,
P. Di Gennaro, and E. Galli.
1993.
Alternative pathways for o-xylene or m-xylene and p-xylene degradation in a Pseudomonas stutzeri strain.
Biodegradation
4:71-80.
|
| 3.
|
Bertoni, G.,
F. Bolognese,
E. Galli, and P. Barbieri.
1996.
Cloning of the genes for and characterization of the early stages of toluene and o-xylene catabolism in Pseudomonas stutzeri OX1.
Appl. Environ. Microbiol.
62:3704-3711[Abstract].
|
| 4.
|
Bertoni, G.,
M. Martino,
E. Galli, and P. Barbieri.
1998.
Analysis of the gene cluster encoding toluene/o-xylene monooxygenase from Pseudomonas stutzeri OX1.
Appl. Environ. Microbiol.
64:3626-3632[Abstract/Free Full Text].
|
| 5.
|
Blatny, J. M.,
T. Brautaset,
H. C. Winther-Larsen,
K. Haugan, and S. Valla.
1997.
Construction and use of a versatile set of broad-host-range cloning and expression vectors based on the RK2 replicon.
Appl. Environ. Microbiol.
63:370-379[Abstract].
|
| 6.
|
Burlage, R. S.,
S. W. Hooper, and G. S. Sayler.
1989.
The TOL (pWW0) catabolic plasmid.
Appl. Environ. Microbiol.
55:1323-1328[Free Full Text].
|
| 7.
|
Byrne, A. M.,
J. J. Kukor, and R. H. Olsen.
1995.
Sequence analysis of the gene cluster encoding toluene-3-monooxygenase from Pseudomonas pickettii PKO1.
Gene
154:65-70[CrossRef][Medline].
|
| 8.
|
De Lorenzo, V., and K. M. Timmis.
1994.
Analysis and construction of stable phenotypes in Gram-negative bacteria with Tn5- and Tn10-derived minitransposons.
Methods Enzymol.
235:386-405[Medline].
|
| 9.
|
Franklin, F. C. H., and P. A. Williams.
1980.
Construction of a partial diploid for the degradative pathway encoded by the TOL plasmid (pWW0) from Pseudomonas putida mt-2: evidence for a positive nature of the regulation by the xylR gene.
Mol. Gen. Genet.
177:321-328[CrossRef][Medline].
|
| 10.
|
Haigler, B. E.,
C. A. Pettigrew, and J. C. Spain.
1992.
Biodegradation of mixtures of substituted benzenes by Pseudomonas sp. strain JS150.
Appl. Environ. Microbiol.
58:2237-2244[Abstract/Free Full Text].
|
| 11.
|
Herrero, M.,
V. De Lorenzo, and K. M. Timmis.
1990.
Transposon vectors containing non-antibiotic resistance selection markers for cloning and stable chromosomal insertion of foreign genes in gram-negative bacteria.
J. Bacteriol.
172:6557-6567[Abstract/Free Full Text].
|
| 12.
|
Kukor, J. J., and R. H. Olsen.
1991.
Genetic organization and regulation of a meta cleavage pathway for catechols produced from catabolism of toluene, benzene, phenol, and cresols by Pseudomonas pickettii PKO1.
J. Bacteriol.
173:4587-4594[Abstract/Free Full Text].
|
| 13.
|
Leahy, J. G.,
G. R. Johnson, and R. H. Olsen.
1997.
Cross-regulation of toluene monooxygenases by the transcriptional activators TbmR and TbuT.
Appl. Environ. Microbiol.
63:3736-3739[Abstract].
|
| 14.
|
Lutolf, V. F.,
R. Prewo,
J. H. Bieri,
P. Ruedi, and C. H. Eugster.
1985.
Synthesen von Dibenzo[b,e][1,4]dioxin-2,3-chinonen, einschliesslich der Ecklonochinone A and B sowie der Isoecklonochinone A and B'.
Helv. Chim. Acta
68:860-881[CrossRef].
|
| 15.
|
Martin, R. W.
1949.
Rapid colorimetric estimation of phenol.
Anal. Chem.
21:1419-1420[CrossRef].
|
| 16.
|
Nordlund, I.,
J. Powlowski, and V. Shingler.
1990.
Complete nucleotide sequence and polypeptide analysis of multicomponent phenol hydroxylase from Pseudomonas sp. strain CF600.
J. Bacteriol.
172:6826-6833[Abstract/Free Full Text].
|
| 17.
|
Nozaki, M.,
S. Kotani,
K. Ono, and S. Seno.
1970.
Metapyrocatechase. Substrate specificity and mode of ring fission.
Biochim. Biophys. Acta
220:1419-1420.
|
| 18.
|
Olsen, R. H.,
J. J. Kukor, and B. Kaphammer.
1994.
A novel toluene-3-monooxygenase pathway cloned from Pseudomonas pickettii PKO1.
J. Bacteriol.
176:3749-3756[Abstract/Free Full Text].
|
| 19.
|
Powlowski, J., and V. Shingler.
1994.
Genetics and biochemistry of phenol degradation by Pseudomonas sp. CF600.
Biodegradation
5:219-236[CrossRef][Medline].
|
| 20.
|
Powlowski, J.,
J. Sealy,
V. Shingler, and E. Cadieux.
1997.
On the role of DmpK, an auxiliary protein associated with multicomponent phenol hydroxylase from Pseudomonas sp. strain CF600.
J. Biol. Chem.
272:945-951[Abstract/Free Full Text].
|
| 21.
|
Sala-Trepat, J. M.,
K. Murray, and P. A. Williams.
1972.
The metabolic divergence in the meta cleavage of catechols by Pseudomonas putida NCIB 10015. Physiological significance and evolutionary implications.
Eur. J. Biochem.
28:347-356[Medline].
|
| 22.
|
Shields, M. S.,
S. O. Montgomery,
P. J. Chapman,
S. M. Cuskey, and P. H. Pritchard.
1989.
Novel pathway of toluene catabolism in the trichloroethylene-degrading bacterium G4.
Appl. Environ. Microbiol.
55:1624-1629[Abstract/Free Full Text].
|
| 23.
|
van der Meer, J.,
W. M. de Vos,
S. Harayama, and A. J. Zehnder.
1992.
Molecular mechanisms of genetic adaptation to xenobiotic compounds.
Microbiol. Rev.
56:677-694[Abstract/Free Full Text].
|
| 24.
|
Vieira, J., and J. Messing.
1982.
The pUC plasmid, an M13mp7-derived system for insertion mutagenesis and sequencing with synthetic universal primers.
Gene
19:259-268[CrossRef][Medline].
|
| 25.
|
Wackett, L. P.
1990.
Toluene dioxygenase from Pseudomonas putida F1.
Methods Enzymol.
188:39-45[Medline].
|
| 26.
|
Wellr, D. D., and E. P. Stirchak.
1983.
Quassinoid synthesis via o-quinone Diels-Alder reactions.
J. Org. Chem.
48:4873-4879[CrossRef].
|
| 27.
|
Whited, G. M., and D. T. Gibson.
1991.
Separation and partial characterization of the enzymes of the toluene-4-monooxygenase catabolic pathway in Pseudomonas mendocina KR1.
J. Bacteriol.
173:3017-3020[Abstract/Free Full Text].
|
| 28.
|
Williams, P. A., and J. R. Sayers.
1994.
The evolution of pathways for aromatic hydrocarbon oxidation in Pseudomonas.
Biodegradation
5:195-217[CrossRef][Medline].
|
| 29.
|
Wright, A., and R. H. Olsen.
1994.
Self-mobilization and organization of the genes encoding the toluene metabolic pathway of Pseudomonas mendocina KR1.
Appl. Environ. Microbiol.
60:235-242[Abstract/Free Full Text].
|
| 30.
|
Yanish-Perron, C.,
J. Vieira, and J. Messing.
1985.
Improved M13 phage cloning vector and host strains: nucleotide sequences of the M13mp18 and pUC19 vectors.
Gene
33:103-119[CrossRef][Medline].
|
| 31.
|
Yen, K. M.,
M. R. Karl,
L. M. Blatt,
M. J. Simon,
R. B. Winter,
P. R. Fausset,
H. S. Lu,
A. A. Harcourt, and K. K. Chen.
1991.
Cloning and characterization of a Pseudomonas mendocina KR1 gene cluster encoding toluene-4-monooxygenase.
J. Bacteriol.
173:5315-5327[Abstract/Free Full Text].
|
| 32.
|
Zylstra, G. J.,
W. R. McCombie,
T. D. Gibson, and B. A. Finette.
1988.
Toluene degradation by Pseudomonas putida F1: genetic organization of the tod operon.
Appl. Environ. Microbiol.
54:1498-1503[Abstract/Free Full Text].
|
Applied and Environmental Microbiology, July 2001, p. 3304-3308, Vol. 67, No. 7
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.7.3304-3308.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
This article has been cited by other articles:
-
Lalucat, J., Bennasar, A., Bosch, R., Garcia-Valdes, E., Palleroni, N. J.
(2006). Biology of Pseudomonas stutzeri. Microbiol. Mol. Biol. Rev.
70: 510-547
[Abstract]
[Full Text]
-
Nakatsu, C. H., Carmosini, N., Baldwin, B., Beasley, F., Kourtev, P., Konopka, A.
(2005). Soil Microbial Community Responses to Additions of Organic Carbon Substrates and Heavy Metals (Pb and Cr). Appl. Environ. Microbiol.
71: 7679-7689
[Abstract]
[Full Text]
-
Maruyama, T., Ishikura, M., Taki, H., Shindo, K., Kasai, H., Haga, M., Inomata, Y., Misawa, N.
(2005). Isolation and Characterization of o-Xylene Oxygenase Genes from Rhodococcus opacus TKN14. Appl. Environ. Microbiol.
71: 7705-7715
[Abstract]
[Full Text]
-
Cafaro, V., Notomista, E., Capasso, P., Di Donato, A.
(2005). Regiospecificity of Two Multicomponent Monooxygenases from Pseudomonas stutzeri OX1: Molecular Basis for Catabolic Adaptation of This Microorganism to Methylated Aromatic Compounds. Appl. Environ. Microbiol.
71: 4736-4743
[Abstract]
[Full Text]
-
Cafaro, V., Notomista, E., Capasso, P., Di Donato, A.
(2005). Mutation of Glutamic Acid 103 of Toluene o-Xylene Monooxygenase as a Means To Control the Catabolic Efficiency of a Recombinant Upper Pathway for Degradation of Methylated Aromatic Compounds. Appl. Environ. Microbiol.
71: 4744-4750
[Abstract]
[Full Text]
-
Solera, D., Arenghi, F. L. G., Woelk, T., Galli, E., Barbieri, P.
(2004). TouR-Mediated Effector-Independent Growth Phase-Dependent Activation of the {sigma}54 Ptou Promoter of Pseudomonas stutzeri OX1. J. Bacteriol.
186: 7353-7363
[Abstract]
[Full Text]
-
Tropel, D., van der Meer, J. R.
(2004). Bacterial Transcriptional Regulators for Degradation Pathways of Aromatic Compounds. Microbiol. Mol. Biol. Rev.
68: 474-500
[Abstract]
[Full Text]
-
Cafaro, V., Izzo, V., Scognamiglio, R., Notomista, E., Capasso, P., Casbarra, A., Pucci, P., Di Donato, A.
(2004). Phenol Hydroxylase and Toluene/o-Xylene Monooxygenase from Pseudomonas stutzeri OX1: Interplay between Two Enzymes. Appl. Environ. Microbiol.
70: 2211-2219
[Abstract]
[Full Text]
-
Jeong, J. J., Kim, J. H., Kim, C.-K., Hwang, I., Lee, K.
(2003). 3- and 4-alkylphenol degradation pathway in Pseudomonas sp. strain KL28: genetic organization of the lap gene cluster and substrate specificities of phenol hydroxylase and catechol 2,3-dioxygenase. Microbiology
149: 3265-3277
[Abstract]
[Full Text]
-
Merkx, M., Lippard, S. J.
(2002). Why OrfY?. CHARACTERIZATION OF MMOD, A LONG OVERLOOKED COMPONENT OF THE SOLUBLE METHANE MONOOXYGENASE FROM METHYLOCOCCUS CAPSULATUS (BATH). J. Biol. Chem.
277: 5858-5865
[Abstract]
[Full Text]