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Applied and Environmental Microbiology, June 1999, p. 2317-2323, Vol. 65, No. 6
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
Chemoselective Nitro Group Reduction and Reductive Dechlorination
Initiate Degradation of 2-Chloro-5-Nitrophenol by Ralstonia
eutropha JMP134
Andreas
Schenzle,1,2,
Hiltrud
Lenke,1
Jim C.
Spain,3 and
Hans-Joachim
Knackmuss1,2,*
Fraunhofer-Institut für
Grenzflächen- und Bioverfahrenstechnik1
and Institut für Mikrobiologie der Universität
Stuttgart,2 D-70569 Stuttgart, Germany, and
Armstrong Laboratory, AFRL/MRLQ, Tyndall Air Force Base,
Florida 32403-53193
Received 25 November 1998/Accepted 29 March 1999
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ABSTRACT |
Ralstonia eutropha JMP134 utilizes
2-chloro-5-nitrophenol as a sole source of nitrogen, carbon, and
energy. The initial steps for degradation of 2-chloro-5-nitrophenol are
analogous to those of 3-nitrophenol degradation in R. eutropha JMP134. 2-Chloro-5-nitrophenol is initially reduced to
2-chloro-5-hydroxylaminophenol, which is subject to an enzymatic
Bamberger rearrangement yielding 2-amino-5-chlorohydroquinone. The
chlorine of 2-amino-5-chlorohydroquinone is removed by a reductive mechanism, and aminohydroquinone is formed. 2-Chloro-5-nitrophenol and
3-nitrophenol induce the expression of 3-nitrophenol nitroreductase, of
3-hydroxylaminophenol mutase, and of the dechlorinating activity. 3-Nitrophenol nitroreductase catalyzes chemoselective reduction of
aromatic nitro groups to hydroxylamino groups in the presence of NADPH.
3-Nitrophenol nitroreductase is active with a variety of mono-, di-,
and trinitroaromatic compounds, demonstrating a relaxed substrate
specificity of the enzyme. Nitrosobenzene serves as a substrate for the
enzyme and is converted faster than nitrobenzene.
 |
INTRODUCTION |
All living organisms are able to
reduce nitroaromatic as well as nitroheteroaromatic compounds. Research
on the fate of the compounds in eucaryotic systems has revealed
cytotoxic and mutagenic effects which are caused by reduction and
further transformation of the reduction products (14-17, 22, 24,
41). The majority of nitroreductases found in mammalian tissues
are oxygen sensitive (type II) (11). The enzymes, which are
also present in other organisms, initially catalyze a one-electron
reduction yielding a nitro anion radical (29, 36). The
radical spontaneously reacts with elementary oxygen to form the
superoxide radical, and the nitro group is regenerated. The phenomenon
is also called a "futile cycle" because reduced pyridine
nucleotides are oxidized without net reduction of the nitro group. In
the absence of oxygen, further reduction of the nitro anion radical,
yielding nitroso, hydroxylamino, and amino derivatives, takes place
(11, 29, 36). In contrast, oxygen-insensitive reductases
(type I) reduce nitroaromatic compounds by two-electron transfers
irrespective of the presence of oxygen. Thus, nitroso, hydroxylamino,
or amino derivatives can be products of the enzymatic reduction.
Oxygen-insensitive nitroreductases have been reported to be involved in
aerobic degradative pathways of nitrobenzene (34), 4-nitrotoluene (21, 37, 43), 3-nitrophenol (3NP) (31, 39), and 4-nitrobenzoate (19). The common
characteristic of these pathways is that the unique product of nitro
group reduction is the hydroxylamino derivative rather than the
aminoaromatic derivative. Characteristically, the arylhydroxylamines
are directly converted to ring cleavage substrates.
Following this mechanism, Ralstonia eutropha JMP134 degrades
3NP via 3-hydroxylaminophenol (3HAP) and aminohydroquinone. The reaction is catalyzed by a nitroreductase and a 3HAP mutase,
respectively (39, 40). Additionally, R. eutropha
JMP134 can grow with 2-chloro-5-nitrophenol (2C5NP) as the sole source
of nitrogen, carbon, and energy.
Most investigations on the degradation of chloronitroarenes have
revealed cometabolic transformations (33, 38, 45). In
contrast, Rhodococcus erythropolis HL 24-1 was shown to
utilize 2-chloro-4,6-dinitrophenol as a sole nitrogen, carbon, and
energy source (27). Another exception is
4-chloro-2-nitrophenol, which was mineralized by a mixed culture in a
coupled anaerobic-aerobic process (5). Interestingly, Bruhn
et al. (8) constructed 4-chloro-2-nitrophenol-assimilatory
bacteria by transferring the plasmid-encoded haloaromatic degrading
sequences from either R. eutropha JMP134 or
Pseudomonas sp. strain B13 into Pseudomonas sp.
strain N31. Before the conjugation experiment, the recipient strain was
able to remove the nitrogen from 4-chloro-2-nitrophenol as nitrite by a
monooxygenase but failed to further degrade the resultant
4-chlorocatechol.
In order to elucidate how R. eutropha JMP134 metabolizes
2C5NP and how the nitrogen and the chlorine are eliminated,
physiological investigations have been undertaken. This study reveals
the initial reactions of the degradative pathway and specifies the
nitroreductase involved.
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MATERIALS AND METHODS |
Growth of bacteria.
R. eutropha JMP134 (35)
was maintained on solid mineral media as described previously
(39). Additionally, the strain was grown on solid
nitrogen-free mineral medium (9) containing 3NP (0.5 mM) as
a nitrogen source and succinate (10 mM) as a carbon and energy source.
During tests of 2C5NP as a sole source of nitrogen, carbon, and energy,
the starting concentration of 2C5NP was 0.46 mM. After the substrate
was utilized, an additional 0.35 mM 2C5NP was added. In the control
medium, 2C5NP was omitted. The cultivation conditions reported for the
growth experiment with 3NP were chosen (39). Cell growth,
protein content in the growing cells, and ammonia concentrations were
determined as described previously (39).
Induction of cells.
R. eutropha JMP134 was grown with
0.5 mM 3NP and 10 mM succinate in nitrogen-free mineral medium
(9). Additional portions of 3NP (0.25 mM) were added after
exponential growth began. 2C5NP-induced cells were obtained in the same
way except that 3NP was replaced by 2C5NP in the growth medium.
Uninduced cells were obtained as described above but ammonium (1 mM)
replaced the nitroaromatic compounds. When the culture reached an
A546 of
0.5, the cells were harvested by
centrifugation, washed twice with 50 mM phosphate buffer (pH 7), and
suspended in the same buffer. The cells were used for resting-cell
experiments or for preparation of cell extracts.
Preparation of cell extracts.
Cells were disrupted as
described previously (39). For preparation of cell extracts
containing membrane-bound proteins, cell debris was removed by
centrifugation at 30,000 × g for 30 min at 4°C. Cell
extracts without membrane-bound proteins were obtained by
centrifugation at 100,000 × g for 60 min at 4°C.
Cell extracts were stored either on ice or frozen at
20°C until
they were used. The protein content of lysates or enzymes was
determined by the method of Bradford (7).
Partial purification of 3NP nitroreductase.
3NP
nitroreductase was partially purified by the same procedure and with
the same starting material (in 55 ml of phosphate buffer) as those
described for the purification of 3HAP mutase (40). 3NP
nitroreductase coeluted (30 ml) with 3HAP mutase from the DEAE CL-6B
(weak anion-exchange resin) column at a concentration of 0.21 M NaCl.
The enzymes were separated by using a butyl agarose (resin for
hydrophobic interactions with proteins) column that was equilibrated
with buffer containing ammonium sulfate (1 M). Whereas the mutase
adhered, the nitroreductase passed through the column. Fractions
containing 3NP nitroreductase activity (45 ml) were concentrated and
desalted by ultrafiltration with a Centriprep 30 filter unit (Amicon).
The filtrate containing 3NP nitroreductase (1.15 ml) was stored frozen
at
20°C until it was used for the experiments described below.
Experiments with resting cells, cell extracts, and enzyme
preparations.
Resting-cell experiments and experiments with cell
extracts or enzyme preparations were performed as described previously (39). Concentrations of substrates and cofactors, as well as cell densities or protein contents, are stated in the text. 3HAP mutase
was purified to homogeneity, and its activity was determined as
previously described (40). The activity of 3NP
nitroreductase was measured spectrophotometrically as described
previously (39).
Analytical methods.
Chloride ion concentration was
determined by ion chromatography (DX-100 Ion Chromatograph; Dionex,
Idstein, Germany) with a anion-exchange column (Ionpac AS14, guard
column AG14; Dionex) using a conductivity detector with a suppression
technique. The mobile phase consisted of an aqueous solution of
Na2CO3 (3.5 mM) and NaHCO3 (1.0 mM), and the flow rate was 1.2 ml/min. Samples for chloride analyses (1 to 2 ml) were incubated in a water bath at 80°C for at least 15 min.
Precipitated proteins or cells were removed by centrifugation prior to
analysis by high-pressure liquid chromatography (HPLC).
Analyses of 3NP, 2C5NP, nitrobenzene, and their metabolites were
performed with an HPLC system (Sykam, Gilching, Germany) equipped with
a diode array detector (Philips, Gilching, Germany). A reversed-phase
column (Lichrospher 100 RP8; 4.6 by 125 mm; Merck, Darmstadt, Germany)
was used for the separation of the compounds, and the flow rate was 1 ml/min. Conversion of 3NP was measured with a gradient system that
started with 10% solvent A (methanol containing hexane sulfonate [Pic
B6; Waters, Milford, Conn.]) and 90% solvent B (water containing
hexane sulfonate) and remained constant for 6 min. Then the ratio was
stepped up to 40% solvent A and 60% solvent B and remained constant
for 6 min. Conversion of 2C5NP or nitrobenzene was measured with a
gradient system that started with 10% solvent A and 90% solvent B and
remained constant for 7 min. Then the composition changed linearly
within 3 min to 50% solvent A and 50% solvent B, and the solvents
remained at this ratio for another 5 min. An isocratic system
consisting of 10% solvent A and 90% solvent B was used to compare
retention volumes and UV spectra of standards and metabolites that were formed upon experiments with 2C5NP and 3NP.
Chemicals.
2C5NP was a gift from Bayer AG (Leverkusen,
Germany). Hydroxylaminobenzene was kindly provided by Shirley Nishino
(Tyndall Air Force Base, Fla.). 2-Amino-5-chlorophenol was synthesized by reduction of 2C5NP. For that, 20 µl of HCl (18% [vol/vol]) was
added to 1 ml of aqueous 2C5NP (1 mM), and the reaction was started by
adding approximately 10 mg of zinc powder. The mixture was mixed
vigorously at room temperature until the yellow color completely
disappeared. The residual powder was removed by centrifugation, and the
supernatant was used as a standard solution for HPLC analysis. 2-Chloro-5-hydroxylaminophenol was synthesized by a method analogous to
that described for synthesis of 3HAP, aminohydroquinone was prepared
from dimethoxyaniline, and N-acetylamino-hydroquinone was
obtained by transformation of 3NP by resting cells of R. eutropha JMP134 as described previously (39). All other
chemicals were of the highest purity commercially available.
 |
RESULTS |
Induction of 3NP nitroreductase during growth on 2C5NP or 3NP.
The growth of R. eutropha JMP134 on 2C5NP as a sole source
of nitrogen, carbon, and energy in liquid culture was comparable with
that on 3NP (39). After a lag phase (2 h), the
A546 increased from 0.028 to 0.074 (for the
control without 2C5NP, the A546 increased from
0.028 to 0.035) within 8 h, which synced with an increase in cell
protein (11.5 µg/ml; control, 0.8 µg/ml) on the one hand and a
complete consumption of 2C5NP (1.1 mM) on the other hand. Higher cell
densities were obtained when more 2C5NP was added during exponential
growth or when 2C5NP only served as a nitrogen source for the cells.
Ammonia release during growth on 2C5NP indicated an initial reduction
of the nitro group. A 2C5NP-dependent NADPH-oxidizing
activity
comparable to that existent in 3NP-grown cells (
39)
was
found in lysates of 2C5NP-grown cells but not in extracts
from
NH
4+-succinate-grown cells. A cross-experiment
was carried out to
determine whether both activities resulted from the
induction
of the same nitroreductase (Table
1). The identical relative
rates
indicated that
R. eutropha JMP134 expressed the same
nitroreductase
during growth on either 3NP or 2C5NP.
Chemoselective reduction of aromatic nitro groups to the
corresponding hydroxylamino groups by 3NP nitroreductase.
3NP
nitroreductase was separated from 3HAP mutase to facilitate detailed
investigation of the action of the reductase (39, 40).
Separation of 3NP nitroreductase from 3HAP mutase could be achieved by
gel filtration or hydrophobic interaction chromatography but not by
anion-exchange chromatography. The activity of 3NP nitroreductase
always completely eluted as a single homogeneous band by all
purification methods used. This is consistent with only one
NADPH-dependent 3NP nitroreductase being present in extracts of induced
cells of R. eutropha JMP134.
Partially purified 3NP nitroreductase (Table
2) was used to analyze the selectivity of
the nitro group reduction of 3-NP
and 2C5NP and to identify the
products of 2C5NP and 3NP reduction.
The enzyme readily reduced 3NP to
3HAP in the presence of excess
NADPH under anaerobic conditions (Fig.
1A). Neither 3-nitrosophenol
nor
3-aminophenol could be detected in the medium, and the 3HAP
remained
stable after 3NP (0.51 mM) was completely transformed.
The reaction
consumed 2.2 mol of NADPH per mol of 3NP. The enzyme
was still active
after 40 min, as indicated by the fact that when
additional 0.5 mM 3NP
was added, it was instantly reduced to 3HAP
(data not shown). The
results indicated that 3NP nitroreductase
specifically reduced 3NP by
the transfer of four electrons to
yield 3HAP.

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FIG. 1.
Conversion of 3NP (A) and 2C5NP (B) to the corresponding
hydroxylamino derivatives by 3NP nitroreductase. (A) 3NP (0.51 mM),
NADPH (2.7 mM), and partially purified 3NP nitroreductase (63 mU/ml
[44 ng/ml of protein]) were incubated in 50 mM phosphate buffer (pH
7.5). (B) 2C5NP (0.96 mM), NADPH (3 mM), NADH (3 mM), and partially
purified 3NP nitroreductase (56 mU/ml [44 ng/ml of protein]) were
incubated in 62 mM phosphate buffer (pH 7). Both experiments were
carried out under an argon atmosphere at 30°C. Samples were analyzed
by HPLC.
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When 2C5NP and NADPH were incubated with the partially purified 3NP
nitroreductase (Fig.
1B), a single product (metabolite
A) was formed.
Metabolite A had a UV spectrum similar to that
of 3HAP (maxima at 203, 234, and 279 nm) but a larger retention
volume. Authentic
2-chloro-5-hydroxylaminophenol showed the same
UV absorption (maxima at
204, 240, and 288 nm) and chromatographic
properties as metabolite A. Reduction of both metabolite A and
the chemically synthesized standard
by zinc in HCl acidic solution
yielded 2-amino-5-chlorophenol, which
was identified by
HPLC.
Enzymes in cell extracts of
R. eutropha JMP134 did not
catalyze the reduction of 3NP, 2C5NP, or the hydroxylamino derivatives
to the corresponding amino derivatives. In contrast, traces of
3-aminophenol and 2-amino-5-chlorophenol were produced from 3NP
and
2C5NP by intact cells of JMP134. The constitutive activity
was
insignificant compared to that of 3NP nitroreductase in induced
cells.
3NP nitroreductase showed 94% of the NADPH-oxidizing activity when
nitrobenzene replaced 3NP as a substrate (Table
3). In
contrast, 3HAP mutase was much
less active (2.3%) toward hydroxylaminobenzene
than toward 3HAP as a
substrate (
40). In fact, anaerobic conversion
of
nitrobenzene (0.5 mM) by an extract from induced cells of
R. eutropha JMP134 led to a fast accumulation of
hydroxylaminobenzene,
which was slowly converted further to
2-aminophenol and 4-aminophenol.
Aniline was not formed although
excessive NADPH (2 mM) was added
into the reaction mixture, which
indicated that 3NP nitroreductase
specifically formed
hydroxylaminobenzene from nitrobenzene.
Conversion of nitrosobenzene by cell extracts.
The proposed
two-electron-transfer mechanism of oxygen-insensitive nitroreductases
presupposes a transient formation of the corresponding nitrosoarenes
during the enzymatic reaction (14). Therefore, nitrosoarenes
should serve as potential substrates for the enzymes. Although 3HAP was
the only detectable product during reduction of 3NP by 3NP
nitroreductase of R. eutropha JMP134, an intermediate
formation of 3-nitrosophenol could not be excluded. Since a standard of
3-nitrosophenol was not available and nitrobenzene was an alternative
substrate for 3NP nitroreductase, nitrosobenzene was tested as a
substrate for the enzyme in cell extracts.
The spontaneous reduction rate of nitrosobenzene (0.2 mM) by NADPH (0.2 mM) in 50 mM phosphate buffer (pH 7.2) was 42 µM min
1.
The corresponding reduction rate in the presence of an extract
from
uninduced cells of
R. eutropha JMP134 (0.115 mg of protein
per ml) was 53 µM min
1. In the presence of an extract
from 3NP-induced cells with the
same protein content, the rate was 124 µM min
1, demonstrating that nitrosobenzene served as a
substrate for
3NP nitroreductase. After the unspecific reduction rate
was subtracted,
the rate for conversion of nitrosobenzene was 3.4-fold
higher
than that for nitrobenzene as a substrate in the extract from
induced cells of
R. eutropha JMP134.
Substrate specificity and characteristics of 3NP
nitroreductase.
In Table 3, the nitroaromatic compounds tested as
substrates for 3NP nitroreductase are listed. Of 39 compounds, only 10 were not reduced at measurable rates, 9 were reduced slowly, and 20 were reduced at significant rates, demonstrating a relaxed substrate
specificity of the enzyme. Some of the compounds were previously tested
as substrates for the NADPH-oxidizing activity in cell extracts from
the 3NP-degrading Pseudomonas putida B2 (31), and
the resulting rates were comparable with those found in extracts of
R. eutropha JMP134. Both nitroreductases were inducible by
3NP and used NADPH as a cosubstrate. Therefore, the two enzymes seem to
be similar.
Storage of cell extracts in buffer systems other than phosphate did not
improve the stability of 3NP nitroreductase. The partially
purified
enzyme retained 74% of its original activity after 31
days when it was
stored frozen at

20°C in 50 mM phosphate buffer
(pH 7.5) or 89%
after storage on ice for 3 days. High concentrations
of ammonium
sulfate (

30% [wt/vol]) and low-pH conditions (<pH
7)
significantly decreased 3NP nitroreductase
activity.
Most bacterial oxygen-insensitive nitroreductases contain flavin
mononucleotide (FMN) as a prosthetic group and utilize NAD(P)H
as an
electron donor (
14). Incubation of an extract (0.56 mg/ml)
from induced cells of
R. eutropha JMP134 together with FMN,
flavin
adenine dinucleotide (FAD), or Fe
2+ (each at 0.1 mM)
for 20 min at room temperature did not affect
the activity of 3NP
nitroreductase. Fractions of the partially
purified enzyme exhibited no
characteristic visible absorption,
and no significant loss of activity
was observed during the purification
procedure. This, however, does not
rule out the possibility that
tightly bound cofactors exist. Some
nitroreductases additionally
require a metal cation as a cofactor
(
6). Incubation of a cell
extract containing 3NP
nitroreductase with Cu
2+ (1 mM) inhibited the activity
completely. Inhibition by Cu
2+ was also noticed for
2,4-dinitrophenol nitroreductase from
Rhodobacter capsulatus
(
6) and for 1-nitropyrene nitroreductase (NRase
I) from
Bacteroides fragilis (
25), which indicates the
presence
of a metal
cofactor.
Identification of aminohydroquinone and its acetyl derivative as
metabolites of 2C5NP.
When 2C5NP (1 mM) was incubated aerobically
with 2C5NP-induced resting cells (A546 = 9.8),
no organic metabolites were detected by HPLC analysis but chloride
(0.82 mM) was released. Therefore, the same experiment was repeated
under anaerobic conditions (A546 = 27), as
shown in Fig. 2. Here, complete
conversion of 2C5NP (0.65 mM) was also accompanied with a nearly
stoichiometric increase in the concentration of chloride (0.57 mM) in
the medium. One dominant metabolite, which exhibited the same
chromatographic properties and UV absorption as authentic
aminohydroquinone, was detected by HPLC. In fact, aminohydroquinone was
slowly converted further to N-acetylaminohydroquinone (data
not shown), which could be identified by comparing its chromatographic
properties and UV absorption with those of a biologically obtained
standard.

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FIG. 2.
Conversion of 2C5NP by induced resting cells of R. eutropha JMP134. 2C5NP (0.65 mM) and resting cells
(A546 = 27) were incubated in 50 mM phosphate
buffer (pH 7) under an argon atmosphere at 30°C. The decrease in
2C5NP ( ) and the formation of aminohydroquinone ( ) and chloride
( ) were determined by HPLC.
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Characterization of metabolites formed from 2C5NP by R. eutropha JMP134.
An unknown metabolite, designated
metabolite B, accumulated when an extract from 2C5NP-induced cells
(0.47 mg of protein per ml) was incubated anaerobically with 2C5NP (0.5 mM) and NADPH (3 mM). Aminohydroquinone was not formed even when the
corresponding extract (0.88 mg of protein per ml) contained
membrane-bound protein and NADH (1 mM) or glutathione (2.5 mM) as
alternative electron donors were added to the buffer. When samples with
metabolite B were exposed to air, an increasingly red color appeared in
the solution concomitant with the formation of a new product. The red
color disappeared instantly when NADH was added to the samples, and
metabolite B was regenerated. Metabolite B could be stabilized by
acidification of the sample with HCl. Exactly the same characteristics were observed with a sample containing aminohydroquinone and cell extract. The UV-absorption spectra of aminohydroquinone (maxima at 218 and 291 nm) and metabolite B (maxima at 200 and 299 nm) were similar,
but metabolite B eluted later from the reversed-phase column. The same
was noticed for the red oxidation products, which were probably the
quinone derivatives of aminohydroquinone (maxima at 210, 263, and 470 nm) and of metabolite B (maxima at 212, 285, and 485 nm). The results
suggested that metabolite B was 2-amino-5-chlorohydroquinone. Isolation
of metabolite B failed due its instability, which is comparable to that
of aminohydroquinone (39). Therefore, no mass spectrometry
and or nuclear magnetic resonance data are available for the compound.
When purified 3HAP mutase (
40) was added to a reaction
mixture in which 2C5NP had previously been converted to
2-chloro-5-hydroxylaminophenol
(Fig.
3)
it was instantly converted to metabolite B. 3-NP-grown
cells readily
dechlorinated metabolite B to aminohydroquinone,
confirming that it was
2-amino-5-chlorohydroquinone (Fig.
3, step
3). The observations
suggested that 3NP nitroreductase formed
2-chloro-5-hydroxylaminophenol, which was rearranged to
2-amino-5-chlorohydroquinone
by 3HAP mutase, and the dechlorination was
identified as the third
step in the pathway.

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FIG. 3.
Conversion of 2C5NP by 3NP nitroreductase (step 1), 3HAP
mutase (step 2), and 3NP-grown cells (step 3) of R. eutropha
JMP134. At time zero, partially purified 3NP nitroreductase (0.56 U)
was added to 62 mM phosphate buffer (pH 7) with 2C5NP (0.96 mM), NADPH
(3 mM), and NADH (3 mM). After 61.5 min purified 3HAP mutase (0.72 U)
was added, and after 170 min 3NP-grown cells (A546 = 13) were added. Incubation was carried out at 30°C under
anaerobic conditions. Concentrations of 2C5NP ( ),
2-chloro-5-hydroxylaminophenol ( ), 2-amino-5-chlorohydroquinone
( ), and aminohydroquinone ( ) were analyzed by HPLC. In order to
estimate the concentration of 2-amino-5-chlorohydroquinone,
aminohydroquinone was used as a standard.
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 |
DISCUSSION |
In natural microbial communities, nitroaromatic compounds are
subject to gratuitous and unspecific reductions of nitro groups. The
extent of reduction and the complexity of the reduction products formed
depend on the number of the nitro groups on the aromatic ring and the
redox potential of the culture. In contrast, nitro group reduction in
axenic cultures that harbor a productive and complete catabolic
sequence is highly selective. Thus, in R. eutropha JMP134,
an inducible and oxygen-insensitive nitroreductase uses NADPH as an
electron donor and catalyzes the reduction of aromatic nitro groups of
3NP and 2C5NP, which selectively stops at the level of the
hydroxylamino group. This unique chemoselective reaction was shown with
3NP, 2C5NP, and nitrobenzene as substrates. Previously, it was reported
that cell extracts from R. eutropha JMP134 containing 3NP
nitroreductase reduced 4-nitrobenzoate exclusively to
4-hydroxylaminobenzoate. Also, 4-nitrotoluene was converted to
4-hydroxylaminotoluene and 6-amino-m-cresol but not to
4-aminotoluene (40). These results confirm the high
chemoselectivity, albeit relaxed substrate specificity, of the 3NP
nitroreductase. An analogous nitroreductase from Pseudomonas pseudoalcaligenes JS45 was purified and characterized
(42). This enzyme catalyzed the reduction of nitrobenzene to
hydroxylaminobenzene, which is a metabolite of a complete degradative
pathway of nitrobenzene in this bacterium (23, 34). The
enzyme also transformed 2,4,6-trinitrotoluene to
4-hydroxylamino-2,6-dinitrotoluene and subsequently to
2,4-dihydroxylamino-6-nitrotoluene, demonstrating that the enzyme,
although highly chemoselective, exhibits relaxed substrate specificity
(18). Usually, nitroreductases from enteric bacteria have
not been tested for chemoselectivity. This was done only with NfnB from
Escherichia coli B, which specifically reduces the antitumor
agent 5-(aziridin-1-yl)-2,4-dinitrobenzamide (CB1954) to equimolar
amounts of its 2- and 4-hydroxylamino derivatives but not to the
corresponding amino derivatives (1).
Nitrosoaromatic derivatives have been proposed as metabolites in
catabolic pathways of mononitroaromatic compounds (19, 31,
42). It is unlikely that oxygen-insensitive nitroreductases release the nitroso intermediates during the reduction of nitroaromatic compounds. The reduction of a nitroso group yielding a hydroxylamino group does not require much activation energy, and therefore most nitrosoaromatic compounds spontaneously react with reduced pyridine and
flavin nucleotide cofactors (4, 28). Nitrosobenzene also served as a substrate for 3NP nitroreductase from R. eutropha JMP134 and was converted faster than nitrobenzene,
indicating that the initial two-electron transfer forming the nitroso
intermediate is the rate-limiting step of the complete reductive
sequence. Likewise, nitrosobenzene was shown to be a substrate for
nitrobenzene nitroreductase (42). In contrast to the enzyme
from R. eutropha JMP134, the corresponding rates for
conversion of nitrosobenzene and nitrobenzene were approximately the same.
Nitroreductases from Salmonella typhimurium (47),
Enterobacter cloacae (10, 12), and E. coli (32, 52) and a flavin reductase from Vibrio
fischeri (53) show high similarity in their amino acid
sequences and form a protein family. In contrast, the amino acid
sequences of the nitroreductase NfsA from E. coli and of the
flavin oxidoreductase from Vibrio harveyi are highly similar, but they are different from those of other enteric
nitroreductases (51) mentioned above. Nitrobenzene
nitroreductase from P. pseudoalcaligenes JS45 possesses an
N-terminal amino acid sequence that is different from all known
sequences of other nitroreductases (42). It remains to be
clarified whether this enzyme and other nitroreductases involved in the
catabolism of nitroaromatic compounds, including 3NP nitroreductase
from R. eutropha JMP134, represent an independent class of
specific nitroreductases. Nitroreductases presumably derive from
different flavin nucleotide-containing enzymes and are therefore a
heterogenous group of enzymes.
In addition to 3NP nitroreductase, cells of R. eutropha
JMP134 possess a constitutive, marginal activity for nitro group
reduction which converts 3NP and 2C5NP to the corresponding
aminophenols. The presence of several different nitroreductases in a
bacterial strain is not unusual. Kinouchi and Ohnishi (25)
likewise separated four different nitroreductases from a strain of
B. fragilis, each reducing 1-nitropyrene to 1-aminopyrene.
Kitamura et al. (26) found three enzymes in E. coli B/r that reduced methyl p-nitrobenzoate to
unidentified products. Bryant et al. (13) found three type I
enzymes in E. coli K-12, each reducing nitrofurazone to the open-chain nitrile. Peterson et al. (36) described a type I and a type II nitroreductase in E. coli K-12, each reducing
the nitro group of nitrofurazone, forming the open-chain nitrile and aminofurazone, respectively.
Characteristically, no organism has yet been found that degrades a
nitroaromatic compound via complete reduction of the nitroaryl to the
corresponding aniline, which is subsequently oxidized and assimilated
via catechol. This sequence would require at least one more reducing
equivalent than the pathways that include arylhydroxylamines as key
metabolites and is therefore less efficient for bacterial growth.
The hydroxylamino compound as the first metabolite of 2C5NP catabolism
is subject to an isomerization analogous to the acid-catalyzed Bamberger rearrangement. As recently described, the purification and
characterization of the 3-hydroxylaminophenol mutase from R. eutropha JMP134 clearly revealed that the conversion of
3-hydroxylaminophenol to aminohydroquinone is catalyzed by the single
enzyme. Correspondingly, the enzymatic reaction of
2-chloro-5-hydroxylaminophenol by the mutase leads to the formation of
2-amino-5-chlorohydroquinone as the second step in the degradative
pathway of 2C5NP.
As the third step of 2C5NP degradation by R. eutropha
JMP134, a reductive dechlorination of 2-amino-5-chlorohydroquinone to aminohydroquinone was observed. Reductive dechlorination at the aromatic ring by aerobic bacteria is rarely observed. The involvement of a hydride-Meisenheimer complex was proposed for reductive
dechlorination of 2-chloro-4,6-dinitrophenol to 2,4-dinitrophenol by
R. erythropolis HL 24-1 and R. erythropolis HL
PM-1 (27). Azotobacter chroococcum MSB-1 formed
4-chlorophenoxyacetate and chloride from 2,4-dichlorophenoxyacetate (3). Two different bacterial species were reported to
dehalogenate 2,4-dichlorobenzoate to yield 4-chlorobenzoate (46,
50). Different aerobic bacterial strains were shown to degrade
pentachlorophenol partly by reductive dechlorination (2, 20, 30,
44, 48, 49).
The proposed initial reactions of the degradative pathways of 3NP and
2C5NP are shown in Fig. 4. The first two
steps of 3NP and 2C5NP degradation by R. eutropha JMP134 are
analogous. The nitrophenolic compounds are reduced to the
hydroxylaminophenols, which then undergo an enzymatic Bamberger
rearrangement to yield aminohydroquinone or its chloro analogue. In the
case of 2-amino-5-chlorohydroquinone, a reductive dechlorination is
involved and aminohydroquinone is formed, which is therefore a common
metabolite in both pathways.
Recently, a catabolic sequence similar to 3NP was reported in
Mycobacterium sp. strain HL 4-NT-1, which degrades
4-nitrotoluene via 4-hydroxylaminotoluene and
6-amino-m-cresol by a nitroreductase and a mutase,
respectively. 6-Amino-m-cresol is subject to ring cleavage,
yielding 2-amino-5-methylmuconic semialdehyde, which is oxidized to
2-amino-5-methylmuconic acid (43). Meanwhile, the
deamination reaction in the pathway of nitrobenzene degradation in
P. pseudoalcaligenes JS45 has been characterized
(23). Here, nitrobenzene is reduced to hydroxylaminobenzene,
followed by rearrangement to 2-aminophenol, which then undergoes
meta ring cleavage to 2-aminomuconic semialdehyde. The
semialdehyde is oxidized to 2-aminomuconate, which is subsequently
deaminated to 2-hydroxymuconic acid. Considering these pathways,
aminohydroquinone is the most likely substrate for ring cleavage during
the degradation of 3NP and 2C5NP by R. eutropha JMP134.
 |
ACKNOWLEDGMENTS |
This work was sponsored by the Air Force Office of Scientific
Research, Air Force Systems Command USAF, under grant AFOSR-91-0237.
We thank C. M. Vogel for her interest and help in facilitating the
research project.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Institut
für Mikrobiologie der Universität Stuttgart, Allmandring
31, D-70569 Stuttgart, Germany. Phone: (49) 711 685 5487. Fax: (49) 711 685 5725. E-mail: imbhjk{at}po.uni-stuttgart.de.
Present address: DuPont Company, Central Research & Development
Dept., E328/B48a Experimental Station, Wilmington, DE 19898.
 |
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