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Applied and Environmental Microbiology, November 2006, p. 7413-7417, Vol. 72, No. 11
0099-2240/06/$08.00+0 doi:10.1128/AEM.01162-06
Copyright © 2006, American Society for Microbiology. All Rights Reserved.
Degradation of Fluorobenzene by Rhizobiales Strain F11 via ortho Cleavage of 4-Fluorocatechol and Catechol
Maria F. Carvalho,1,
Maria Isabel M. Ferreira,2,
Irina S. Moreira,1
Paula M. L. Castro,1* and
Dick B. Janssen2
Escola Superior de Biotecnologia, Universidade Católica Portuguesa, Rua Dr. António Bernardino de Almeida, 4200-072 Porto, Portugal,1
Department of Biochemistry, Groningen Biomolecular Sciences and Biotechnology Institute, University of Groningen, Nijenborgh 4, NL-9747 AG Groningen, The Netherlands2
Received 19 May 2006/
Accepted 5 September 2006

ABSTRACT
The aerobic metabolism of fluorobenzene by
Rhizobiales sp. strain
F11 was investigated. Liquid chromatography-mass spectrometry
analysis showed that 4-fluorocatechol and catechol were formed
as intermediates during fluorobenzene degradation by cell suspensions.
Both these compounds, unlike 3-fluorocatechol, supported growth
and oxygen uptake. Cells grown on fluorobenzene contained enzymes
for the
ortho pathway but not for
meta ring cleavage of catechols.
The results suggest that fluorobenzene is predominantly degraded
via 4-fluorocatechol with subsequent
ortho cleavage and also
partially via catechol.

INTRODUCTION
During the last decades, environmental contamination by fluorinated
organic compounds has received increasing attention because
of their use as herbicides, fungicides, surfactants, refrigerants,
intermediates in organic synthesis, solvents, and pharmaceuticals
(
11). Whereas the biodegradation of chlorinated compounds has
been studied quite extensively (
19), little is known about the
bacterial metabolism of fluoroaromatic compounds, even though
there have been several reports on the degradation of fluorobenzoic
acids (
5,
6,
7,
16). With chloroaromatics, most degradation
routes involve dioxygenase- and dehydrogenase-mediated conversion
to the corresponding chlorocatechols, which are further metabolized
by a dioxygenase that cleaves the aromatic ring. Dehalogenation
occurs during metabolism of the ring-cleavage products (
19).
Most described strains degrade chlorocatechols via the
ortho-cleavage
pathway (14,
18,
19,
20), but
meta cleavage of 3-chlorocatechol
can also occur (
13), even though the
meta-cleavage route is
often unproductive due to the formation of toxic or dead-end
products (
1,
19). Dehalogenation may in some cases occur prior
to ring cleavage. For example, mutants of
Pseudomonas sp. strain
B13 and
Alcaligenes eutrophus B9 that grow on 2-fluorobenzoate
use a dioxygenase to convert it to catechol, with concomitant
decarboxylation and defluorination (
5).
Pseudomonas putida strain
CLB 250, which can use three different 2-halobenzoates, also
converts these substrates by initial dehalogenating dioxygenation
(
6), and a defluorinating 4-fluorobenzoate monooxygenase has
been reported as well (
16).
The present paper describes a metabolic pathway for fluorobenzene (FB). Information about the bacterial metabolism of this compound is scarce, despite studies on its chlorinated analogue (13, 18). Lynch et al. (12) described the oxidation of FB to 3-fluorocatechol by a strain of Pseudomonas putida, but in this study FB was not used as a carbon source. Recently, FB was reported to be completely degraded by a bacterial consortium (2) and by a pure bacterial culture that utilized it as a sole carbon and energy source (3). This gram-negative bacterium, phylogenetically classified within the order Rhizobiales, was named strain F11 and was used here to investigate the metabolism of FB.

Intermediates produced during FB degradation.
In order to obtain information about the degradation pathway
of FB, we tested which intermediates accumulated upon incubation
of concentrated cell suspensions of strain F11 with FB. First,
cells were grown in sealed flasks on FB in mineral medium as
described previously (
3), harvested by centrifugation (10,000
x g for 15 min at 4°C), washed twice with mineral medium,
and resuspended in the same medium to give an optical density
at 600 nm of 0.3. Glucose (1 mM) was added, since it was found
in preliminary experiments that this enhanced degradation of
FB and stimulated accumulation of intermediates. The suspensions
were incubated in closed flasks with FB, and samples were taken
at appropriate times, centrifuged, and subjected to high-performance
liquid chromatography (HPLC), gas chromatography, and fluoride
measurements. Fluoride was measured with a Dionex Dx-120 ion
chromatograph equipped with an Allsep A-2 anion column from
Alltech, and the eluent was a mixture of NaHCO
3 and Na
2CO
3 in
deionized water. For FB analysis, culture samples were extracted
with diethylether and analyzed by gas chromatography as described
previously (
3). It was observed that whole cells of strain F11
completely removed 1.1 mM FB in 13 h, but stoichiometric fluoride
release was seen only after 29 h (Fig.
1). This indicates that
fluorinated intermediates did temporarily accumulate but that
there was no formation of high levels of fluorinated dead-end
metabolites.
Samples (20 µl) from the same culture fluid were also
analyzed by HPLC and liquid chromatography-mass spectrometry
(LC-MS). HPLC analysis was carried out on a Lichrospher 100
RP8 reversed-phase column in connection with Jasco PU-980 pumps,
a Jasco MD-910 diode array detector, and a Jasco UV-2075 detector.
Compounds were isocratically eluted at a flow rate of 1 ml/min
with a solution of water-acetonitrile (80:20) and 10 mM formic
acid. LC-MS was carried out with a Micromass ZMD detector equipped
with a XTerra MS, a SymmetryShield C8 column (4.6 mm by 150
mm), a 996 photodiode array detector, and a 2690 separations
module, all from Waters. While degradation proceeded, five metabolites
(compounds I to V) appeared in the culture medium (Table
1).
Four of these (compounds I, II, IV, and V) were completely consumed
during prolonged incubation. One minor metabolite (compound
III) remained in the culture supernatant even after incubation
for 48 h.
View this table:
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TABLE 1. HPLC retention times and absorption maxima of metabolic intermediates formed by F11 cells exposed to fluorobenzene in the presence of glucose
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Metabolite I, which appeared early, coeluted with catechol and
had a molecular mass (negative-mode MS) of
m/z = 109 (M-H
+).
Metabolite II was identified as 4-fluorocatechol on the basis
of cochromatography with a standard in HPLC analysis and its
negative-mode mass spectrum with
m/z = 126.91 (M-H
+). The dead-end
metabolite III was identified as
cis-dienelactone by cochromatography
and mass spectrometry (positive ionization,
m/z = 140.04 [M+H
+]).
Metabolites IV and V could not be identified, since no ionization
was obtained with LC-MS.
The occurrence of the two catechols during the initial 20 h of FB degradation (Fig. 1) suggests that strain F11 converts FB partially to catechol and partially to 4-fluorocatechol during the first metabolic step. Approximately 0.6 mM of the FB that was converted transiently appeared as 4-fluorocatechol, and about 0.3 mM was detected as catechol. This is in agreement with the observation that significant fluoride release is taking place already during the initial period of FB degradation, i.e., when catechol is formed but that fluoride release is only complete when the intermediate 4-fluorocatechol and possibly other fluorinated metabolites have been degraded. The formation of both catechol and 4-fluorocatechol from FB is also consistent with the ability of strain F11 to grow on both of these catechols. The fact that catechol remained in the medium for quite a long time even though it is a better growth substrate than 4-fluorocatechol suggests inhibition of the catechol pathway by the presence of 4-fluorocatechol.

Substrate-dependent oxygen consumption by whole cells.
In order to test the inducibility of FB transformation activity,
oxygen uptake measurements were done. Cells of strain F11 were
grown on FB, benzene, or citrate, harvested by centrifugation,
washed, resuspended to a density of 0.43 mg of cellular protein
per ml, and transferred to a stirred vessel that was equipped
with a fiber optic oxygen sensor (MOPS-1; ProSense BV, Hanover,
Germany). The rate of O
2 consumption was measured at room temperature
in the presence of different substrates (Table
2).
Cells grown on FB oxidized fluorobenzene and
cis-1,2-dihydrobenzenediol
as well as 4-fluorocatechol and were also highly induced for
the oxidation of catechol. Rapid oxidation of catechol, 4-fluorocatechol,
and
cis-1,2-dihydrobenzenediol was also obtained with cells
that were pregrown on benzene. With fluorobenzene and benzene,
these cells showed even higher oxygen uptake rates than cells
grown on FB. With cells grown on citrate, the aromatic substrates
were not oxidized, suggesting that the formation of the first
catabolic enzyme was induced during growth on the aromatic substrates
and repressed on citrate. The oxygen uptake rates with 3-fluorocatechol
were very low, independent of whether the cells were grown on
FB, benzene, or citrate. The patterns of oxygen consumption
show that oxidation of catechol, 4-fluorocatechol, and
cis-1,2-dihydrobenzenediol
was induced by FB and benzene, whereas 3-fluorocatechol was
never oxidized. When batch cultures of strain F11 growing with
1 mM of FB were supplemented with 0.1 mM of 3-fluorocatechol,
FB was no longer converted by the cells, and fluoride, measured
with a fluoride-selective electrode (
2), was not released.

Enzymes involved in the degradation of FB.
To investigate whether degradation of FB proceeds via
meta or
ortho cleavage, the presence of several enzymes involved in
these routes was tested (Table
3). Late exponential FB-grown
cells were harvested by centrifugation, washed twice with 0.1
M Tris-HCl buffer (pH 7.5) containing 0.1 mM 1,4-dithiothreitol,
and disrupted by sonication in the same buffer. After centrifugation
(90,000
x g for 60 min at 4°C) the clear supernatant was
used as the cell extract for enzyme assays. Its protein content
was determined with Coomassie brilliant blue using bovine serum
albumin as the standard.
Catechol 2,3-dioxygenase was measured by determining the formation
of 2-hydroxymuconic semialdehyde (

= 44,000 M
1 cm
1)
at 375 nm, according to the method of Nozaki (
15). (Fluoro)
catechol 1,2-dioxygenase activity was measured similarly, as
described by Dorn and Knackmuss (
4) (
cis,cis-muconate = 16,800
M
1,
2-fluoro-cis,cis-muconate = 14,900 M
1 cm
1,
3-fluoro-cis,cis-muconate = 14,900 M
1 cm
1). Muconate
cycloisomerase activity was measured by following the consumption
of
cis,
cis-muconate in an assay mixture containing 30 mM Tris-HCl
(pH 8.0), 1 mM MnCl
2, and 0.1 mM
cis,
cis-muconate. Dienelactone
hydrolase activity was determined by following at 280 nm (

=
17,000 M
1 cm
1) the decrease in the level of 0.1
mM
cis-dienelactone that was incubated with enzyme in 10 mM
histidine-HCl (pH 6.5). Maleylacetate was prepared on the day
of its use by alkaline hydrolysis of
cis-dienelactone (
8), and
the reductase was measured by following maleylacetate (0.1 mM)-dependent
NADH (0.2 mM) oxidation at 340 nm in 50 mM Tris-HCl (pH 7.5).
Activities were corrected for substrate-independent NADH oxidation.
3-Oxoadipate:succinyl-coenzyme A transferase was measured as
described by Mars et al. (
13). One unity of activity was defined
as the amount of enzyme required to convert 1 µmol of
substrate per min at 25°C.
Activities of the ortho pathway enzymes catechol 1,2-dioxygenase, muconate cycloisomerase, maleylacetate reductase, and 3-oxoadipate:succinyl-coenzyme A transferase were found in cell extracts of strain F11 grown on FB. Catechol 2,3-dioxygenase activity was not detected, indicating that strain F11 does not use a meta-cleavage pathway to degrade FB. A 1,2-dioxygenase activity was detected with both catechol and 4-fluorocatechol but was hardly detected with 3-fluorocatechol. Instead, the catechol 1,2-dioxygenase activity was reduced by 70% and 90% in the presence of 0.1 and 0.5 mM 3-fluorocatechol, respectively. A muconate cycloisomerase activity with respect to cis,cis-muconic acid was also detected. No activity was found for cis-dienelactone hydrolase in extracts of strain F11. These observed enzyme activities suggest that the catechols in the FB degradation pathway undergo ortho cleavage.
We judge it highly unlikely that 3-fluorocatechol is an intermediate in FB degradation pathway, since it was not used as a growth substrate and it strongly inhibited FB degradation and growth and since no dioxygenase activity with 3-fluorocatechol was detected in cell extracts of strain F11 grown on FB. This conclusion is in line with the previously described resistance of the expected product 2-fluoro-cis,cis-muconic acid to enzymatic cycloisomerization (23), although it is risky to generalize such a finding to other organisms. Furthermore, in mutants of Alcaligenes eutrophus B9 and Pseudomonas sp. strain B13 that use 2-fluorobenzoate for growth, the formation of toxic 3-fluorocatechol is prevented by loss of dihydrodihydroxybenzoate dehydrogenase activity, allowing growth on catechol that can be formed by initial dioxygenation of the aromatic ring (5). The absence of a 3-halocatechol intermediate clearly distinguishes the fluorobenzene pathway of strain F11 from chlorobenzene catabolic pathways, which proceed via 3-chlorocatechol (13, 17, 18). This could explain the lack of growth of strain F11 on chlorobenzene.

Pathway of FB degradation.
We propose the pathway for FB metabolism shown in Fig.
2. The
initial attack of FB by dioxygenase activity yields two different
fluorinated dihydrodiols. The 4-fluoro-
cis-benzene-1,2-dihydrodiol
that is produced is transformed into 4-fluorocatechol by a dihydrodiol
dehydrogenase. Conversion of the other product, 1-fluoro-
cis-benzene-1,2-dihydrodiol,
to catechol can proceed without involvement of dehydrogenase
that reduces a cofactor, since the electrons are transferred
to the fluoride that is being released (Fig.
2). Simultaneous
conversion of a fluorinated compound to catechol and a fluorinated
catechol was described earlier for the degradation of 2-fluorobenzoate
by
Pseudomonas sp. strain B13 and strain FLB300 (
5,
7).
The capability of strain F11 cells to use 4-fluorocatechol as
a growth substrate, its transient accumulation in cell suspensions
to higher levels than catechol, and the fact that 4-fluorocatechol
stimulated oxygen uptake by whole cells lead to the conclusion
that 4-fluorocatechol is the predominant intermediate. The occurrence
of 4-fluorocatechol as an intermediate has also been described
for the aforementioned

-proteobacterium strain FLB300, which
degrades both benzoate and all monofluorosubstituted benzoates
(
7). The metabolism of 4-fluorocatechol is proposed to proceed
through
ortho cleavage by a (fluoro)catechol 1,2-dioxygenase
that yields 3-fluoro-
cis,
cis-muconate. This product could be
transformed with concomitant defluorination into maleylacetate
via either 4-fluoromuconolactone or another lactone derivative.
ortho cleavage of 4-fluorocatechol is also a key step in the
metabolism of 3- and 4-fluorobenzoate by several bacterial strains
(
9,
21,
22,
24). These convert 4-fluorocatechol via 3-fluoro-
cis,
cis-muconate
and 4-fluoromuconolactone (
22,
24) or via a non-fluorinated
dienelactone intermediate (
24). If 4-fluorocatechol metabolism
in strain F11 proceeds in the same way, this could also explain
the accumulation of
cis-dienelactone since it can slowly be
formed as a side product during spontaneous or enzyme-catalyzed
dehydrodefluorination of 4-fluoromuconolactone (
23,
24). This
pathway would also allow formation of protoanemonin.
Maleylacetate can be channeled into the tricarboxylic acid cycle via 3-oxoadipate. Catechol, the minor product of the initial dioxygenation reaction, is proposed to be metabolized to cis,cis-muconate, converted to the lactone derivative, and then also channeled into the 3-oxoadipate route (Fig. 2).

ACKNOWLEDGMENTS
M.F.C. acknowledges a research grant from Fundação
para a Ciência e Tecnologia (FCT), Portugal (BD/21839/99),
and Fundo Social Europeu (III Quadro Comunitário de Apoio).
This work was supported in part by the European Community's
Human Potential Programme under contract HPRTN-CT-2002-00213
[BIOSAP] and by a grant from the European Science Foundation.
We thank Paolo De Marco for help in the preparation of cell extracts and Filip Kaminski for valuable discussions and a kind gift of protoanemonin. Both 4-fluorocatechol and cis-dienelactone were generous gifts of W. Reineke (Bergische Universität, Wuppertal, Germany). We thank Theodora Tiemersma for help with the LC-MS analysis.

FOOTNOTES
* Corresponding author. Mailing address: Escola Superior de Biotecnologia, Universidade Católica Portuguesa, Rua Dr. António Bernardino de Almeida, 4200-072 Porto, Portugal. Phone: 351 225580059. Fax: 351 225090351. E-mail:
plc{at}esb.ucp.pt.

Published ahead of print on 15 September 2006. 
M.F.C. and M.I.M.F. contributed equally to this work. 

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Applied and Environmental Microbiology, November 2006, p. 7413-7417, Vol. 72, No. 11
0099-2240/06/$08.00+0 doi:10.1128/AEM.01162-06
Copyright © 2006, American Society for Microbiology. All Rights Reserved.