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Journal of Bacteriology, January 2001, p. 752-757, Vol. 183, No. 2
0021-9193/01/$04.00+0 DOI: 10.1128/JB.183.2.752-757.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
Initiation of Anaerobic Degradation of p-Cresol by
Formation of 4-Hydroxybenzylsuccinate in
Desulfobacterium cetonicum
Jochen A.
Müller,*
Alexander S.
Galushko,
Andreas
Kappler, and
Bernhard
Schink
Fakultät für Biologie,
Universität Konstanz, 78457 Konstanz, Germany
Received 13 April 2000/Accepted 6 October 2000
 |
ABSTRACT |
The anaerobic bacterium Desulfobacterium cetonicum
oxidized p-cresol completely to CO2 with
sulfate as the electron acceptor. During growth,
4-hydroxybenzylsuccinate accumulated in the medium. This finding
indicated that the methyl group of p-cresol is activated by
addition to fumarate, analogous to anaerobic toluene,
m-xylene, and m-cresol degradation. In cell
extracts, the formation of 4-hydroxybenzylsuccinate from
p-cresol and fumarate was detected at an initial rate of 0.57 nmol min
1 (mg of protein)
1. This
activity was specific for extracts of p-cresol-grown cells. 4-Hydroxybenzylsuccinate was degraded further to
4-hydroxybenzoyl-coenzyme A (CoA), most likely via
-oxidation.
4-Hydroxybenzoyl-CoA was reductively dehydroxylated to
benzoyl-CoA. There was no evidence of degradation of
p-cresol via methyl group oxidation by
p-cresol-methylhydroxylase in this bacterium.
 |
INTRODUCTION |
The toxic aromatic compound
p-cresol (4-methylphenol) is a constituent of disinfectants
and preservatives and is used largely in the formulation of
antioxidants and in the fragrance and dye industries (1).
It originates mainly from coal gasification plants, fractionation of
coal tar, and a variety of synthetic processes. p-Cresol is
also formed from tyrosine by several anaerobic bacteria (16, 41,
44). Anaerobic degradation of p-cresol could be
demonstrated with pure cultures of nitrate-reducing, iron-reducing, and
sulfate-reducing bacteria and under methanogenic conditions (2,
7, 19, 25, 29, 37, 39, 43). It has been well established that
denitrifying bacteria metabolize p-cresol, cognate to its
degradation by aerobic bacteria (13 and references
therein), through a sequence of oxidation reactions leading to
4-hydroxybenzoate, with water as the oxygen source (7, 14,
34). In the initial step, the methyl group of
p-cresol is enzymatically oxidized, probably via formation
of a quinone methide intermediate (13, 20), to form
4-hydroxybenzylalcohol. The latter is further converted to
4-hydroxybenzaldehyde by the same enzyme,
p-cresol-methylhydroxylase (13, 22). The
standard redox potential (E0') of the couple
4-hydroxybenzylalcohol/p-cresol is in the range of +80
mV (calculated as described before [42]), and the
methylhydroxylase reaction is coupled with the reduction of a
c-type cytochrome with a midpoint potential of around
+230 mV (21, 22).
It has been proposed that sulfate-reducing bacteria degrade
p-cresol via methyl group oxidation, too (19, 28,
41). This would be surprising, since release of electrons at the
redox potentials mentioned above would be difficult for these bacteria:
transfer of electrons from the reduced cytochrome of
p-cresol-methylhydroxylase to either adenosine
5'-phosphosulfate (E0' =
60 mV
[42]) or sulfite (E0' =
116 mV
[42]) as the electron acceptor would require a
substantial energy input.
In the present study, we employed in vitro assays and physiological
studies to examine sulfidogenic p-cresol degradation by Desulfobacterium cetonicum. With this bacterium, it was
shown recently that anaerobic degradation of m-cresol
proceeded via addition of the methyl group of m-cresol to
fumarate to form 3-hydroxybenzylsuccinate (3-HBS) (32).
This reaction is analogous to the anaerobic activation of toluene
(4, 6, 33) and m-xylene (24) with
fumarate to form benzylsuccinate or 3-methylbenzylsuccinate,
respectively. The benzylsuccinate (derivative) is further converted in
a
-oxidation-like scheme to benzoyl-coenzyme A (CoA) or a derivative
thereof. The present results suggest that p-cresol is
degraded via formation of 4-HBS rather than via methyl group oxidation
by D. cetonicum.
 |
MATERIALS AND METHODS |
Bacterial strain and growth conditions.
D.
cetonicum 480 (17) (DSM 7267) was cultivated in a
sulfide-reduced bicarbonate-buffered mineral salt water medium. Medium composition and growth conditions have been described previously in
detail (23, 32). The amount of cell matter formed in
growth tests was calculated via a gravimetrically determined conversion factor (0.1 optical density unit at 660 nm [OD660] = 22.6 mg/liter).
Enzyme assays.
Cell harvesting and preparation of cell
extracts were carried out under anoxic conditions as reported before
(23, 32). Enzyme assays were carried out at 30°C, and
given activities are means of at least three independent measurements.
Formation of 4-HBS was monitored discontinuously in 2-ml Hungate vials
under an N2 atmosphere in 50 mM potassium phosphate (pH
7.2) supplemented with 2.5 mM dithioerythritol and 0.2 mM titanium
(III)-nitrilotriacetic acid (NTA) and containing 10.0 g of NaCl
and 1.75 g of MgCl2 · 6 H2O per
liter. Vials were sealed with butyl-rubber septa. The protein content
varied between 1 and 3 mg/ml. All substrate stock solutions were
prereduced with 2.5 mM dithioerythritol. The test was started by
addition of p-cresol (100 µM) or fumarate (5 mM) to the
assay mix (total volume, 1 ml). Samples were taken with gas-tight
syringes (Macherey-Nagel, Düren, Germany), diluted in ice-cold
100 mM phosphoric acid to stop the reaction, and analyzed by
high-pressure liquid chromatography (HPLC). 3-HBS-forming,
2-HBS-forming, and benzylsuccinate synthase activities were checked for
with the same assay except that p-cresol was replaced with
either m-cresol, o-cresol, or toluene. With benzylsuccinate synthase, the benzylsuccinate but not the toluene concentration was monitored over time. The oxygen sensitivity of
4-HBS-forming activity was checked by application of a gentle air
stream over the cell extract for 2 min and rendering the assay anoxic
again by flushing the gas phase for 5 min with N2 and by addition to Ti(III)-NTA (5 mM final concentration). Afterwards, the
test was started by addition of p-cresol to the vials.
p-Cresol methylhydroxylase (EC 1.17.99.1) activity was
checked under an N2 atmosphere according to Hopper
(20). The assay mixture contained degassed 50 mM potassium
phosphate (pH 7.2) containing 10.0 g of NaCl and 1.75 g of
MgCl2 · 6H2O, 0.2 mM
dichlorophenolindophenol, 0.3 mM phenazine methosulfate, 0.5 mM
p-cresol, and cell extract (50 to 150 µg of protein).
The catabolism of 4-HBS was studied in assays for 4-HBS formation
amended with a CoA source and/or a mixture of potential electron
acceptors. Succinyl-CoA (2 mM), acetyl-CoA (2 mM), and free CoASH (0.5 mM) plus ATP (5 mM) were tested as CoA sources and NAD, NADP, and
flavin adenine dinucleotide (FAD) (5 mM each) were added as electron
acceptors at various times to the assay. Substrate and product
concentrations were monitored by HPLC analysis. Samples were also
analyzed after an alkaline treatment (KOH [pH 12], 70°C, 20 min).
Dilution of substrate and product concentrations in the assays upon
addition of a CoA source, electron acceptor, or KOH was taken into consideration.
4-Hydroxybenzoyl-CoA reductase activity was measured discontinuously by
HPLC analysis (9). The reaction mixture contained 0.2 mM
chemically synthesized 4-hydroxybenzoyl-CoA, 100 µM methylviologen, and 50 mM formate in 100 mM potassium phosphate buffer (pH 7.2) containing 10.0 g of NaCl and 1.75 g of
MgCl2 · 6 H2O per liter, prereduced with
H2-Pd catalyst. The test was started by addition of either
4-hydroxybenzoyl-CoA or formate to the assay mixture. Methylviologen
was reduced in the formate-dehydrogenase reaction in the assay
(23).
Fumarate reductase (EC 1.3.1.6) was checked for as described by Beh et
al. (3).
Analytical methods.
The identification of 4-HBS in cultures
grown on p-cresol was carried out basically as described
earlier for the identification of 3-HBS in
m-cresol-converting cultures (32). In brief,
culture supernatant (1,000 ml) obtained by centrifugation was acidified to pH < 2 by addition of HCl (35%), degassed in order to remove hydrogen sulfide, and extracted thoroughly with diethyl ether. The
ether fraction was concentrated at room temperature, derivatized with diazomethane, and analyzed by gas chromatography-mass spectrometry (GC/MS) (32). In addition, culture supernatant was
analyzed by HPLC. Eluting compounds were scanned on-line with a
photodiode array detector (Beckman-Coulter, Munich, Germany)
in the wavelength range of 200 to 350 nm.
Other aromatic compounds and aliphatic acids were identified and
quantified by HPLC analysis as described previously (10, 18). Sulfide in growth experiments was determined by the
methylene blue formation reaction (11), and protein was
quantified by the method of Bradford (8).
Synthesis of 4-HBS.
4-HBS was synthesized via the Stobbe
reaction (40) essentially as described earlier for
synthesis of 3-HBS (32). First, 4-benzyloxybenzylidene
succinic acid was formed by condensation of 4-hydroxybenzaldehyde with
diethyl succinic acid in a methanolic solution of sodium methoxide.
4-Benzyloxybenzylidene succinic acid was identified by 1H
nuclear magnetic resonance (NMR) with spectra collected on a Bruker
AC250 instrument (Bruker Analytik, Rheinstetten, Germany) in
CD3SOCD3. Elemental analysis gave C = 68.8%, H = 5.2%; according to the formula
C18H16O5, C = 69.2% and
H = 5.1% would have been expected (melting point, 203 to
204°C). Subsequently, 4-benzyloxybenzylidene succinic acid was
catalytically reduced with H2 to form
4-hydroxybenzylsuccinic acid. The latter was identified by
1H-NMR in CD3SOCD3. Elemental
analysis gave C = 58.6%, H = 5.2%; according to the formula
C11H12O5, C = 58.9% and H = 5.4% would have been expected (melting point, 178 to 180°C).
Other chemicals.
4-Hydroxybenzoyl-CoA was synthesized
according to Wieland (15, 30) and purified by HPLC.
Titanium(III)-NTA stock solutions contained 100 mM Ti3+
chelated by 150 mM NTA and were prepared as described elsewhere (31). All other chemicals and gases used were of reagent
grade or better and from standard commercial sources.
 |
RESULTS |
Growth with p-cresol.
D. cetonicum
oxidized p-cresol completely to CO2 with sulfate
as the electron acceptor. Sulfide was produced concomitantly with
substrate utilization and increase in optical density. Sulfide recovery
was 96%, expressed as a percentage of theoretical production. After a
lag phase of several days, D. cetonicum grew with a doubling time of 5.1 days. Growth was exponential even in the presence of 1.5 mM
p-cresol. The in vivo substrate turnover rate was calculated to be 6.2 nmol min
1 (mg of protein)
1.
D. cetonicum also grew with 4-hydroxybenzoate and
4-hydroxybenzaldehyde, but did not use 4-hydroxybenzylalcohol,
o-cresol, o-, m-, or
p-xylene, or 2-hydroxybenzoate. Growth with toluene,
m-cresol, 3-hydroxybenzoate, and benzoate has been reported
before (17, 32).
Identification of 4-HBS.
In cultures growing with
p-cresol, a compound accumulated that was not detected while
this strain was growing with other aromatic substrates, as analyzed by
reversed-phase HPLC. The on-line UV spectrum of this compound (Fig.
1A) was similar to that of 3-HBS, which
is an intermediate of m-cresol degradation by this bacterium (32). This observation indicated that 4-HBS is formed
during degradation of p-cresol. Chemically synthesized 4-HBS
coeluted with the compound from culture supernatant in an HPLC run at
low methanol or acetonitrile concentrations (10%), and the UV spectra of these two substances were identical (Fig. 1A). After treatment of
ethereal extract of culture supernatant with diazomethane, a compound
was detected by GC/MS analysis which had an identical GC retention time
and displayed essentially the same mass spectrum as chemically
synthesized dimethyl ester of 4-methoxybenzylsuccinate (Fig. 1B and C).
The mass spectrum of the standard (Fig. 1B) exhibits the molecular ion
of derivatized 4-HBS at m/z 266 and apparently the methoxy
tropylium ion (C8H9O+) at
m/z 121. The overall pattern of fragment ions corresponds well with the described mass spectra of benzylsuccinate derivatives (4, 24, 32), taking the additional oxygen atom of 4-HBS into consideration. The spectrum of the compound from the culture supernatant (Fig. 1C) is basically the same as that of the standard, but two major additional peaks are observable at m/z 57 and
97. These might be attributed to coelution with another compound. Taken
together, these findings confirmed that 4-HBS is a metabolite of
p-cresol degradation by D. cetonicum and
suggested that p-cresol degradation proceeds analogously to
m-cresol degradation in this bacterium. A quantitative
analysis revealed that the accumulating 4-HBS made up less than 5% of
the overall p-cresol converted.

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FIG. 1.
Identification of 4-HBS in supernatants of
p-cresol-converting cultures of D. cetonicum. (A)
On-line UV spectra of chemically synthesized 4-HBS (A) and of 4-HBS
from culture supernatant (B) in acetonitrile (10%) and 10 mM potassium
phosphate buffer (pH 2.2). The maxima are at 232 and 278 nm. (B and C)
Mass analysis by GC/MS of chemically synthesized (B)
4-methoxybenzylsuccinate dimethyl ester and (C)
4-methoxybenzylsuccinate dimethyl ester obtained from culture
supernatant; mass units are daltons.
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|
In addition to detection of dimethyl ester of 4-methoxybenzylsuccinate
by GC/MS analysis, a compound was observed in diazomethane-treated extract of culture supernatant that was tentatively identified as the
dimethyl ester of 4-methoxyphenylitaconate (or a close analogue) by
its mass spectrum (not shown). This compound had an apparent mass of
264 Da. The presence of most of the major fragment ions in the spectrum
(m/z 249, 230, 219, 163, 145, 105, and 91) could be
explained by loss of methyl, methylene, and carbonyl group(s) of the
proposed parent compound. Due to lack of authentic standards, the
nature of this compound could not be further elucidated. Furthermore,
traces of 4-methoxybenzoic acid methyl ester were found by GC/MS
analysis. 4-Hydroxybenzylalcohol and 4-hydroxybenzaldehyde (or their
methylated derivatives) were not detected by HPLC or GC/MS analysis.
Formation of 4-HBS from p-cresol and fumarate.
In
anoxic cell extracts of p-cresol-grown cells, an activity
was measured that converted p-cresol and fumarate, forming
4-HBS (Table 1). In the absence of either
p-cresol or fumarate or with heat-denatured extract (90°C,
10 min), no formation of 4-HBS could be detected. A time course of a
discontinuous assay for 4-HBS formation from p-cresol and
fumarate is depicted in Fig. 2. During the reaction run, the activity decreased with time. The initial specific activity was 0.57 nmol min
1 (mg of
protein)
1, thus being about 9% of the in vivo turnover
rate. Formation of 4-HBS was observed only under strictly anoxic
conditions. Treatment of the cell extract with a weak air stream for 2 min resulted in complete loss of the activity, and the activity could
not be recovered by restoring reducing conditions. Applying a stream of
N2 gas instead of air had no significant effect.
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TABLE 1.
Specific activities of 4-HBS, 3-HBS, and benzylsuccinate
formation in cell extracts of D. cetonicum grown on
either p-cresol, m-cresol, or toluene
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|
The 4-HBS-forming activity was the only reaction detected converting
p-cresol. No indication of a p-cresol
methylhydroxylase was found.
Specificity of the reaction.
In cell extracts of D. cetonicum grown with either p-cresol,
m-cresol, or toluene, the formation of 4-HBS, 3-HBS, and
benzylsuccinate from fumarate and the respective aromatic compound was
determined. Formation of either one of the benzylsuccinate derivatives
was detected only in extracts of cells grown with the corresponding substrate (Table 1). We also checked for an activity in cell extracts
that reacted with o-cresol and fumarate to form 2-HBS. Regardless of the growth substrate, there was only a small decrease in
o-cresol concentration with time (less than 5 µM/h) in the presence or in the absence of fumarate. With HPLC analysis, formation of several peaks could be detected; however, none had a retention time
or on-line UV spectrum similar to that of either 4-HBS or 3-HBS.
Catabolism of 4-HBS.
The fate of 4-HBS was investigated in
cell extracts by HPLC analysis. Assays for 4-HBS formation were amended
with a CoA source (succinyl-CoA, acetyl-CoA, or free CoASH and ATP)
and/or a mixture of electron acceptors (NAD, NADP, and FAD). Without
the addition of a CoA source and electron acceptors, the 4-HBS detected
made up at least 94% of the p-cresol converted. In the
presence of succinyl-CoA and electron acceptors, significantly lower
relative amounts of 4-HBS were detected (64 to 72% of
p-cresol converted). Replacement of succinyl-CoA with
acetyl-CoA or of CoASH plus ATP or omission of either succinyl-CoA or
the electron acceptors led to a similar final concentration of 4-HBS
(>90% of p-cresol converted) as in assays without any
further addition. After addition of succinyl-CoA and electron
acceptors, two compounds were detected in the reaction mixture that
coeluted with 4-hydroxybenzoate and 4-hydroxybenzoyl-CoA. The on-line
UV spectrum of the peak coeluting with 4-hydroxybenzoate was identical
to that of authentic 4-hydroxybenzoate. Due to the small size of the
peak coeluting with 4-hydroxybenzoyl-CoA, a reliable UV spectrum could
not be recorded. However, after alkaline treatment of the sample, that
peak was no longer detectable and the concentration of
4-hydroxybenzoate in the sample increased slightly. The total amount of
4-hydroxybenzoate in alkaline-treated samples (up to 9 µM) accounted
for most of the difference in concentrations between
p-cresol converted and 4-HBS detected. The formation of free
4-hydroxybenzoate in untreated samples was probably due to hydrolysis
of 4-hydroxybenzoyl-CoA by the cell extract (19 nmol min
1
[mg of protein]
1).
In a separate assay, the reduction of 4-hydroxybenzoyl-CoA to
benzoyl-CoA was measured at an activity of 6.8 nmol min
1
(mg of protein)
1. The reaction was not complete due to
hydrolysis of 4-hydroxybenzoyl-CoA. Reduction of free 4-hydroxybenzoate
was not detected.
Growth with p-cresol in the presence of aliphatic
acids.
The influence of fumarate on the degradation of
p-cresol by growing cultures of D. cetonicum was
studied. In the presence of fumarate, growth with p-cresol
was biphasic (Fig. 3). In the first
phase, D. cetonicum metabolized p-cresol at a
rate of 7 nmol min
1 (mg of protein)
1. Per
mol of p-cresol, about 1 mol of fumarate was consumed (7.5 nmol min
1 [mg of protein]
1) and close to
1 mol of succinate accumulated in the medium (6.8 nmol
min
1 [mg of protein]
1). After
p-cresol depletion, D. cetonicum grew at the
expense of fumarate (11 nmol min
1 [mg of
protein]
1). Succinate was formed at a lower rate (4.6 nmol min
1 [mg of protein]
1) compared to
the first growth phase. During both growth phases, small amounts of
malate were excreted into the medium (not shown). In growth experiments
with succinate or acetate in the presence of p-cresol,
growth rates and yields were similar to those of cultures growing in
the absence of an aliphatic acid (Table
2). During growth with the putative
intermediate 4-hydroxybenzoate, there was no growth stimulation by
fumarate compared to controls with succinate or acetate. D. cetonicum did not grow with p-cresol or
4-hydroxybenzoate as the electron donor and fumarate as the sole
potential electron acceptor, and fumarate reductase was not detectable
in D. cetonicum.

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FIG. 3.
Degradation of p-cresol ( ) in the presence
of fumarate ( ). Formation of sulfide ( ) and succinate ( ) and
increase in OD ( ) are also shown. d, days.
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 |
DISCUSSION |
The present data strongly suggest that p-cresol
degradation by D. cetonicum is initiated by formation of
4-HBS. This reaction, an addition of fumarate to the methyl group of
p-cresol, and the proposed metabolism of 4-HBS to
4-hydroxybenzoyl-CoA through a
-oxidation-like scheme (Fig.
4) is analogous to anaerobic degradation of toluene (4, 6, 33), m-xylene
(24), and m-cresol (32) in
denitrifying and/or sulfate-reducing bacteria. Our results are
therefore contrary to earlier studies on p-cresol metabolism by sulfate-reducing bacteria (19, 28). In those reports,
it was proposed that these bacteria hydroxylate the methyl group of
p-cresol as the initial reaction step. The in vitro
formation of 4-hydroxybenzylalcohol or 4-hydroxybenzylaldehyde
as reaction products, however, was not demonstrated in these reports.
Our assumption that 4-HBS is a true intermediate of p-cresol
degradation by D. cetonicum is supported by three lines of
evidence.

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FIG. 4.
Proposed initial reactions of p-cresol
degradation by D. cetonicum. Compounds with a question mark
(4-hydroxyphenylitaconyl-CoA and 4-hydroxybenzoylsuccinyl-CoA) were not
identified.
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(i) In cell extract of D. cetonicum, the formation of 4-HBS
from p-cresol and fumarate could be detected at an initial
activity of 0.57 nmol min
1 (mg of protein)
1
which accounted for about 9% of the in vivo turnover rate of p-cresol. This activity was found only in extracts of
p-cresol-grown cells (Table 1), indicating that it is of
specific physiological relevance for this degradation pathway. There
was no evidence of the presence of p-cresol
methylhydroxylase in D. cetonicum.
It can be envisioned that 4-HBS formation proceeds in a similar manner
to formation of benzylsuccinate from toluene and fumarate. This
reaction is most likely initiated by abstraction of an H atom from the
methyl group of toluene by an enzyme-bound radical, to form benzyl
radical (4, 5, 12, 26). The benzyl radical adds to the
double bond of fumarate, and an H atom is donated back to the radical
to form benzylsuccinate. The catalyzing enzyme, benzylsuccinate
synthase, is irreversibly destroyed by molecular oxygen due to cleavage
of the radical-harboring peptide chain (26). Therefore, it
is not surprising that the 4-HBS-forming activity was also extremely
oxygen sensitive. Similar to benzylsuccinate formation in cell extracts
of the denitrifying bacterium Thauera aromatica and of
Desulfobacula toluolica (6, 33), there was a
severe loss of 4-HBS-forming activity with time (Fig. 2). This is
unlike the 3-HBS- and benzylsuccinate-forming activities in cell
extracts of D. cetonicum, which appeared to be rather
stable. Since the experimental procedures for measuring the respective activities in D. cetonicum were the same, this might argue
against inactivation by molecular oxygen as the sole reason for the
decrease in 4-HBS-forming activity. It was speculated that the loss of an activating factor or additional cosubstrate accounts for the loss in
benzylsuccinate-forming activity in T. aromatica and
D. toluolica (6, 33). Whether this could also
be the case in 4-HBS formation in cell extracts of D. cetonicum remains to be elucidated.
(ii) 4-HBS was metabolized further to 4-hydroxybenzoate and
4-hydroxybenzoyl-CoA in cell extracts in the presence of the electron acceptors NAD(P) and FAD and succinyl-CoA as a CoA source. The formation of 4-hydroxybenzoate was presumably due to hydrolysis of
4-hydroxybenzoyl-CoA by the cell extract. In assays in which succinyl-CoA was either omitted or replaced with acetyl-CoA or free
CoASH plus ATP, only a little 4-HBS was converted and no formation of
4-hydroxybenzoyl-CoA or 4-hydroxybenzoate, respectively, could be
detected. These findings indicate that 4-HBS is activated in a
succinyl-CoA transferase reaction to 4-HBS-CoA. For benzylsuccinate oxidation to benzoyl-CoA in T. aromatica, involvement of a
benzylsuccinate:succinyl-CoA CoA-transferase has already been reported
(27). Under standard conditions, the oxidation of
4-HBS-CoA to 4-hydroxybenzoyl-CoA with pyridine nucleotides and FAD as
electron acceptors is endergonic. In vitro, the reaction equilibrium
was shifted to the product side by the exergonic hydrolysis of
4-hydroxybenzoyl-CoA. In vivo, the reductive dehydroxylation of
4-hydroxybenzoyl-CoA to benzoyl-CoA might pull the reaction forward.
This reaction was reported to be irreversible in T. aromatica (9). The benzoyl-CoA formed is probably
reduced further to aliphatic products.
Furthermore, an intermediate of the proposed pathway,
4-hydroxyphenylitaconate (resp. the CoA ester), could be tentatively identified in supernatants of p-cresol-grown cultures. This
is equivalent to the identification of phenylitaconate in culture supernatants of toluene-grown cells (4).
(iii) Addition of fumarate to p-cresol-converting cultures
significantly stimulated growth (Table 2, Fig. 3). Assuming a pathway
of p-cresol degradation as outlined in Fig. 4, succinate has
to be reoxidized to fumarate for 4-HBS formation. This oxidation is
thermodynamically difficult for sulfate-reducing bacteria and might
involve an energy-driven reversed electron transport (36). Such energy investment is not necessary if externally provided fumarate
is used for 4-HBS formation. The increase in both growth rate and yield
upon addition of fumarate and the detection of succinate in the medium
strongly support the assumption of an energy-dependent oxidation of
succinate to fumarate during growth with p-cresol. With the
presumed intermediate 4-hydroxybenzoate, growth was not stimulated by
addition of fumarate, and succinate was not detected in the culture supernatant.
It has been pointed out recently that the terminal electron-accepting
system seems to largely influence the route by which various phenolic
compounds are degraded under anoxic conditions (35). This
also appears to be the case with anaerobic degradation of
p-cresol. Whereas nitrate-reducing bacteria use an oxidation reaction for attacking the substrate, sulfate-reducing bacteria would
have difficulties in disposing of electrons gained at a comparable high
redox potential in this reaction and therefore apply a different
degradation strategy via addition of the methyl group to fumarate.
 |
ACKNOWLEDGMENTS |
We thank A. M. Cook and coworkers for giving us the
opportunity to use their HPLC system, Malin Beil for carrying out the GC/MS measurement, and Sigrid Welte for providing 1H-NMR
data for 4-hydroxybenzylsuccinic acid and 4-benzyloxybenzylidene succinic acid.
This work was supported by grants from the Deutsche
Forschungsgemeinschaft, the Fonds der Chemischen Industrie, and the
University of Konstanz.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Department of
Civil and Environmental Engineering, Stanford University, Stanford, CA 94305-4020. Phone: (650) 723-0315. Fax: (650) 725-3162. E-mail: jmueller{at}stanford.edu.
 |
REFERENCES |
| 1.
|
Agency for Toxic Substances and Disease Registry.
1990.
Toxicological profile for cresols (draft). U.S.
Public Health Service, U.S. Department of Health and Human Services, Atlanta, Ga.
|
| 2.
|
Bak, F., and F. Widdel.
1986.
Anaerobic degradation of phenol and phenol derivatives by Desulfobacterium phenolicum sp. nov.
Arch. Microbiol.
146:177-180[CrossRef].
|
| 3.
|
Beh, M.,
G. Strauss,
R. Huber,
K.-O. Stetter, and G. Fuchs.
1993.
Enzymes of the reductive citric acid cycle in the autotrophic eubacterium Aquifex pyrophilus and in the archaebacterium Thermoproteus neutrophilus.
Arch. Microbiol.
160:306-311[CrossRef].
|
| 4.
|
Beller, H. R., and A. M. Spormann.
1997.
Anaerobic activation of toluene and o-xylene by addition to fumarate in denitrifying strain T.
J. Bacteriol.
179:670-676[Abstract/Free Full Text].
|
| 5.
|
Beller, H. R., and A. M. Spormann.
1998.
Analysis of the novel benzylsuccinate synthase reaction for anaerobic toluene activation based on structural studies of the product.
J. Bacteriol.
180:5454-5457[Abstract/Free Full Text].
|
| 6.
|
Biegert, T.,
G. Fuchs, and J. Heider.
1996.
Evidence that anaerobic oxidation of toluene in the denitrifying bacterium Thauera aromatica is initiated by formation of benzylsuccinate from toluene and fumarate.
Eur. J. Biochem.
238:661-668[Medline].
|
| 7.
|
Bossert, I. D., and L. Y. Young.
1986.
Anaerobic oxidation of p-cresol by a denitrifying bacterium.
Appl. Environ. Microbiol.
52:1117-1122[Abstract/Free Full Text].
|
| 8.
|
Bradford, M. M.
1976.
A rapid and sensitive method for the quantitation of microgram quantities of protein using the principle of protein-dye binding.
Anal. Biochem.
72:248-254[CrossRef][Medline].
|
| 9.
|
Breese, K., and G. Fuchs.
1998.
4-Hydroxybenzoyl-CoA reductase (dehydroxylating) from the denitrifying bacterium Thauera aromatica.
Eur. J. Biochem.
251:916-923[Medline].
|
| 10.
|
Brune, A., and B. Schink.
1990.
Pyrogallol-to-phloroglucinol conversion and other hydroxyltransfer reactions catalyzed by cell extracts of Pelobacter acidigallici.
J. Bacteriol.
172:1070-1076[Abstract/Free Full Text].
|
| 11.
|
Cline, J. D.
1969.
Spectrophotometric determination of hydrogen sulfide in natural waters.
Limnol. Oceanogr.
14:454-458.
|
| 12.
|
Coschigano, P. W.,
T. S. Wehrman, and L. Y. Young.
1998.
Identification and analysis of genes involved in anaerobic toluene metabolism by strain T1: putative role of a glycine free radical.
Appl. Environ. Microbiol.
64:1650-1656[Abstract/Free Full Text].
|
| 13.
|
Cunane, L. M.,
Z. W. Chen,
N Shamala,
F. S. Mathews,
C. N. Cronin, and W. S. McIntire.
2000.
Structures of the flavocytochrome p-cresol methylhydroxylase and its enzyme-substrate complex: gated substrate entry and proton relays support the proposed catalytic mechanism.
J. Mol. Biol.
295:357-374[CrossRef][Medline].
|
| 14.
|
Dangel, W.,
R. Brackmann,
A. Lack,
M. Mohamed,
J. Koch,
B. Oswald,
B. Seyfried,
A. Tschech, and G. Fuchs.
1991.
Differential expression of enzyme activities initiating anaoxic metabolism of various aromatic compounds via benzoyl-CoA.
Arch. Microbiol.
155:256-262[CrossRef].
|
| 15.
|
Decker, K.
1959.
Die aktivierte Essigsäure, p. 63-66.
Enke, Stuttgart, Germany.
|
| 16.
|
Elsden, S. R.,
M. G. Hilton, and J. M. Waller.
1976.
The end products of the metabolism of aromatic amino acids by Clostridia.
Arch. Microbiol.
107:283-288[CrossRef][Medline].
|
| 17.
|
Galushko, A. S., and E. P. Rozanova.
1991.
Desulfobacterium cetonicum sp. nov.: a sulfate-reducing bacterium which oxidizes fatty acids and ketones.
Microbiology (Engl. transl. of Mikrobiologiya)
60:742-746.
|
| 18.
|
Galushko, A. S.,
D. Minz,
B. Schink, and F. Widdel.
1999.
Anaerobic degradation of naphthalene by a pure culture of a novel type of marine sulfate-reducing bacterium.
Environ. Microbiol.
1:415-420[CrossRef][Medline].
|
| 19.
|
Häggblom, M. M.,
M. D. Rivera,
I. D. Bossert,
J. E. Rogers, and L. Y. Young.
1990.
Anaerobic biodegradation of p-cresol under three reducing conditions.
Microb. Ecol.
20:141-150.
|
| 20.
|
Hopper, D. J.
1976.
The hydroxylation of p-cresol and its conversion to p-hydroxybenzaldehyde in Pseudomonas putida.
Biochem. Biophys. Res. Commun.
69:462-468[CrossRef][Medline].
|
| 21.
|
Hopper, D. J.
1983.
Redox potential of the cytochrome c in the flavocytochrome p-cresol methylhydroxylase.
FEBS Lett.
161:100-102[CrossRef][Medline].
|
| 22.
|
Hopper, D. J.,
I. D. Bossert, and M. E. Rhodes-Roberts.
1991.
p-Cresol methylhydroxylase from a denitrifying bacterium involved in anaerobic degradation of p-cresol.
J. Bacteriol.
173:1298-1301[Abstract/Free Full Text].
|
| 23.
|
Janssen, P. H., and B. Schink.
1995.
Metabolic pathways and energetics of the acetone-oxidizing, sulfate-reducing bacterium, Desulfobacterium cetonicum.
Arch. Microbiol.
163:188-194[Medline].
|
| 24.
|
Krieger, C. J.,
H. R. Beller,
M. Reinhard, and A. M. Spormann.
1999.
Initial reactions in anaerobic oxidation of m-xylene by the denitrifying bacterium Azoarcus sp. strain T.
J. Bacteriol.
181:6403-6410[Abstract/Free Full Text].
|
| 25.
|
Kuever, J.,
J. Kulmer,
S. Jannsen,
U. Fischer, and K. H. Blotevogel.
1993.
Isolation and characterization of a new spore-forming sulfate-reducing bacterium growing by complete oxidation of catechol.
Arch. Microbiol.
159:282-288[CrossRef][Medline].
|
| 26.
|
Leuthner, B.,
C. Leutwein,
H. Schulz,
P. Hoerth,
W. Haehnel,
E. Schiltz,
H. Schraegger, and J. Heider.
1998.
Biochemical and genetic characterization of benzylsuccinate synthase from Thauera aromatica: a new glycyl radical enzyme catalysing the first step in anaerobic toluene metabolism.
Mol. Microbiol.
28:615-628[CrossRef][Medline].
|
| 27.
|
Leutwein, C., and J. Heider.
1999.
Anaerobic toluene-catabolic pathway in denitrifying Thauera aromatica: activation and beta-oxidation of the first intermediate, (R)-(+)-benzylsuccinate.
Microbiology
145:3265-3271[Abstract/Free Full Text].
|
| 28.
|
Londry, K. L.,
J. M. Suflita, and R. S. Tanner.
1999.
Cresol metabolism by the sulfate-reducing bacterium Desulfotomaculum sp. strain Groll.
Can. J. Microbiol.
45:458-463[CrossRef][Medline].
|
| 29.
|
Lovley, D. R., and D. J. Lonergan.
1990.
Anaerobic oxidation of toluene, phenol, and p-cresol by the dissimilatory iron-reducing organism GS-15.
Appl. Environ. Microbiol.
56:1858-1864[Abstract/Free Full Text].
|
| 30.
|
Merkel, S.,
A. E. Eberhard,
J. Gibson, and C. S. Harwood.
1989.
Involvement of coenzyme A thioesters in anaerobic metabolism of 4-hydroxybenzoate by Rhodopseudomonas palustris.
J. Bacteriol.
171:1-7[Abstract/Free Full Text].
|
| 31.
|
Moench, T. T., and J. G. Zeikus.
1983.
An improved preparation method for a titanium(III) media reductant.
J. Microbiol. Methods
1:199-202.
|
| 32.
|
Müller, J. A.,
A. S. Galushko,
A. Kappler, and B. Schink.
1999.
Anaerobic degradation of m-cresol by Desulfobacterium cetonicum is initiated by formation of 3-hydroxybenzylsuccinate.
Arch. Microbiol.
172:287-294[CrossRef][Medline].
|
| 33.
|
Rabus, R., and J. Heider.
1998.
Initial reactions of anaerobic metabolism of alkylbenzenes in denitrifying and sulfate-reducing bacteria.
Arch. Microbiol.
170:377-384[CrossRef].
|
| 34.
|
Rudolphi, A.,
A. Tschech, and G. Fuchs.
1991.
Anaerobic degradation of cresols by denitrifying bacteria.
Arch. Microbiol.
155:238-248[CrossRef][Medline].
|
| 35.
|
Schink, B.,
B. Philipp, and J. Müller.
2000.
Anaerobic degradation of phenolic compounds.
Naturwissenschaften
87:12-23[CrossRef][Medline].
|
| 36.
|
Schirawski, J., and G. Unden.
1998.
Menaquinone-dependent succinate dehydrogenase of bacteria catalyzes reversed electron transport driven by the proton potential.
Eur. J. Biochem.
257:210-215[Medline].
|
| 37.
|
Schnell, S.,
F. Bak, and N. Pfennig.
1989.
Anaerobic degradation of aniline and dihydroxybenzenes by newly isolated sulfate-reducing bacteria and description of Desulfobacterium anilini.
Arch. Microbiol.
152:556-563[CrossRef][Medline].
|
| 38.
|
Simon, E. J., and D. Shemin.
1953.
The preparation of S-succinyl-CoA.
J. Am. Chem. Soc.
75:2520.
|
| 39.
|
Smolenski, W. J., and J. M. Suflita.
1987.
Biodegradation of cresol isomers in anoxic aquifers.
Appl. Environ. Microbiol.
53:710-716[Abstract/Free Full Text].
|
| 40.
|
Stobbe, H.
1911.
Monoarylfulgensäuren und ihre Fulgide.
Liebigs Ann. Chem.
380:26-36.
|
| 41.
|
Stone, R. W.,
H. E. Machamer,
W. J. McAleer, and T. S. Oakwood.
1949.
Fermentation of tyrosine by marine bacteria.
Arch. Biochem.
21:217-223.
|
| 42.
|
Thauer, R. K.,
K. Jungermann, and K. Decker.
1977.
Energy conservation in anaerobic bacteria.
Bacteriol. Rev.
41:100-180[Free Full Text].
|
| 43.
|
Tschech, A., and G. Fuchs.
1987.
Anaerobic degradation of phenol by pure cultures of newly isolated denitrifying pseudomonads.
Arch. Microbiol.
148:213-217[CrossRef][Medline].
|
| 44.
|
Yokoyama, M. T., and J. R. Carlson.
1981.
Production of skatole and para-cresol by a rumen Lactobacillus sp.
Appl. Environ. Microbiol.
41:71-76[Abstract/Free Full Text].
|
Journal of Bacteriology, January 2001, p. 752-757, Vol. 183, No. 2
0021-9193/01/$04.00+0 DOI: 10.1128/JB.183.2.752-757.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
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