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Journal of Bacteriology, October 1999, p. 6403-6410, Vol. 181, No. 20
Environmental Engineering and Science,
Department of Civil and Environmental Engineering, Stanford
University, Stanford, California 94305-4020
Received 29 March 1999/Accepted 9 August 1999
The initial enzymatic steps in anaerobic m-xylene
oxidation were studied in Azoarcus sp. strain T, a
denitrifying bacterium capable of mineralizing m-xylene via
3-methylbenzoate. Permeabilized cells of m-xylene-grown
Azoarcus sp. strain T catalyzed the addition of
m-xylene to fumarate to form (3-methylbenzyl)succinate. In the presence of succinyl coenzyme A (CoA) and nitrate,
(3-methylbenzyl)succinate was oxidized to
E-(3-methylphenyl)itaconate (or a closely related isomer)
and 3-methylbenzoate. Kinetic studies conducted with permeabilized cells and whole-cell suspensions of m-xylene-grown
Azoarcus sp. strain T demonstrated that the specific rate
of in vitro (3-methylbenzyl)succinate formation accounts for at least
15% of the specific rate of in vivo m-xylene consumption.
Based on these findings, we propose that Azoarcus sp.
strain T anaerobically oxidizes m-xylene to 3-methylbenzoate (or its CoA thioester) via (3-methylbenzyl)succinate and E-(3-methylphenyl)itaconate (or its CoA thioester) in a
series of reactions that are analogous to those recently proposed for anaerobic toluene oxidation to benzoyl-CoA. A deuterium kinetic isotope
effect was observed in the (3-methylbenzyl)succinate synthase reaction
(and the benzylsuccinate synthase reaction), suggesting that a
rate-determining step in this novel fumarate addition reaction involves
breaking a C-H bond.
Benzene, toluene, ethylbenzene, and
the xylene isomers, collectively known as BTEX, are some of the most
water-soluble constituents of gasoline (14). Due to improper
handling and disposal of gasoline, BTEX are frequently found as soil
and groundwater contaminants in the United States (33). BTEX
have been known to be readily degraded by microorganisms under aerobic
conditions (19). Under these conditions, well-characterized
oxygenases catalyze the initial enzymatic step of BTEX degradation with
molecular oxygen as a cosubstrate (19, 31). However,
subsurface environments are frequently rendered anaerobic as a result
of indigenous microorganisms consuming the available molecular oxygen
(13). Under anaerobic conditions, bacteria face the
biochemical challenge of activating aromatic hydrocarbons in the
absence of molecular oxygen.
Within the past decade, substantial research has been conducted to
elucidate the biochemical pathways of anaerobic BTEX degradation, with
particular interest focused on the initial activation reactions (reviewed in references 22 and
23). Thus far, most of the research in this field
has been conducted on anaerobic toluene degradation (reviewed in
reference 23). The initial steps of anaerobic
toluene degradation were recently elucidated by in vitro studies
conducted with two denitrifying species, Thauera aromatica K172 (11) and Azoarcus sp. strain T
(6) (which was previously identified as a
Pseudomonas sp. [16]). These in vitro
studies demonstrated that toluene is activated by addition to fumarate to form benzylsuccinate (BS) (6, 11). BS is subsequently oxidized to E-phenylitaconate (E-PI) (or its
coenzyme A [CoA] thioester) (6) and benzoyl-CoA (6,
11). Benzoyl-CoA, a known central intermediate in anaerobic
oxidation of numerous aromatic compounds, including toluene, is
eventually oxidized to acetyl-CoA and carbon dioxide (22).
Compared to toluene, anaerobic mineralization of the xylene isomers
does not appear to occur as readily and is not as well characterized.
While more than 20 pure cultures have been isolated that mineralize
toluene (reviewed in reference 23), only 5 pure cultures have been isolated that mineralize m-xylene
(16-18, 21, 29), and only one pure culture has been
isolated that mineralizes o-xylene (21). One pure
culture has been reported to mineralize p-xylene, but no
conclusive evidence such as carbon mass and electron balances was
presented (32). An enrichment culture, however, has been
shown to mineralize p-xylene (20).
Although a pathway for anaerobic m-xylene mineralization had
not yet been established, recent findings suggested that
m-xylene may be mineralized by a pathway analogous to the
one demonstrated for toluene (6, 11). Metabolic studies
conducted with Azoarcus sp. strain T demonstrated that
m-xylene is oxidized to carbon dioxide (16) via
3-methylbenzoate (30) under denitrifying conditions. In
addition, preliminary studies conducted with Azoarcus sp.
strain T provided evidence suggesting that the 3-methyl homologs of BS
and E-PI (or a closely related isomer) are formed during m-xylene metabolism (4, 30). Since BS (6,
11) and E-PI (6) had recently been
demonstrated to be intermediates of anaerobic toluene oxidation to
benzoyl-CoA (see above), we hypothesized that the 3-methyl homologs of
BS and E-PI (or a closely related isomer) are transient
intermediates of anaerobic m-xylene oxidation to
3-methylbenzoate (or its CoA thioester).
In this report, we demonstrate that permeabilized cells of
m-xylene-grown Azoarcus sp. strain T catalyze the
addition of m-xylene to fumarate to form
(3-methylbenzyl)succinate (3-MeBS) (see Fig. 1) at specific activities
that can account for in vivo anaerobic m-xylene
mineralization in Azoarcus sp. strain T. We also demonstrate that 3-MeBS is oxidized to E-(3-methylphenyl)itaconate
(E-3-MePI) (or a closely related isomer) and
3-methylbenzoate in the presence of succinyl-CoA and nitrate. Based on
these findings, we propose that the initial reactions in anaerobic
m-xylene mineralization in Azoarcus sp. strain T
are the oxidation of m-xylene to 3-methylbenzoate (or
3-methylbenzoyl-CoA) via 3-MeBS and E-3-MePI (or
E-3-MePI-CoA) (Fig. 1). Since the initial reactions
demonstrated here for anaerobic m-xylene oxidation closely
resemble those of anaerobic toluene oxidation (6, 11), we
conducted preliminary biochemical studies to infer whether any of the
analogous initial reactions in the m-xylene and toluene
pathways are catalyzed by the same enzyme. The findings from these
studies will be discussed.
Chemicals.
The chemicals used in this study included
m-xylene ( Growth of bacteria.
Azoarcus sp. strain T (DSM 9506;
previously identified as a Pseudomonas sp.), a bacterium
capable of mineralizing m-xylene and toluene under
denitrifying conditions (16), was obtained from the Deutsche
Sammlung von Mikroorganismen (Braunschweig, Germany). Cultures of
Azoarcus sp. strain T were grown anaerobically in a
bicarbonate-buffered mineral salts medium as described previously (6). m-Xylene or toluene was amended to the
medium as the sole carbon and electron source, while nitrate was
amended as the sole electron acceptor. During growth, neat
m-xylene or toluene and sodium nitrate (from a 1 M stock
solution) were repeatedly added to the cultures to avoid substrate
depletion. Liquid concentrations of m-xylene and toluene
were kept below 320 µM to avoid toxicity effects from the respective
solvents, while that of nitrate was kept below 2 mM to avoid toxicity
effects from nitrite. Liquid concentrations of m-xylene and
toluene were calculated by using published data for Henry's law
constants (26).
0021-9193/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
Initial Reactions in Anaerobic Oxidation of
m-Xylene by the Denitrifying Bacterium Azoarcus
sp. Strain T

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ABSTRACT
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References
![]()
INTRODUCTION
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References
![]()
MATERIALS AND METHODS
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References
99%; Aldrich Chemical Co., Inc. Milwaukee,
Wis.); m-xylene-d6 (
98 atom%; Isotech, Inc., Miamisburg, Ohio); toluene (99.8% high-performance liquid chromatography grade; Aldrich);
toluene-d8 (
99 atom%; Aldrich);
o-xylene-d10 (>99 atom%; Aldrich);
p-xylene-d10 (
99 atom%; Aldrich);
DL-benzylsuccinic acid (Sigma Chemical Co., St. Louis,
Mo.); DL-3-MeBS (
99%, custom synthesized; Radian
International LLC, Austin, Tex.); E-PI (
99%, custom
synthesized; Radian); CoA, sodium salt (96%; Sigma); succinyl-CoA,
sodium salt (92%; Sigma); ATP, disodium salt (grade I, 99%; Sigma);
titanium(III) chloride (1.9 M solution in 2.0 M HCl; Aldrich);
DL-dithiothreitol (DTT; 99%; Sigma). Initially, an
authentic E-PI standard synthesized by Migaud et al.
(27) was graciously provided by J. Tiedje, J. Frost, and
coworkers (Michigan State University).
Permeabilized cell assays. Unless otherwise indicated, permeabilized cell assays were conducted with cells of Azoarcus sp. strain T grown under denitrifying conditions with m-xylene as the sole carbon and electron source. These assays were conducted in a similar fashion to that described previously (6). Briefly, cells from 2-liter batch cultures of Azoarcus sp. strain T in late exponential growth phase were harvested anaerobically by centrifugation (15,000 × g, 20 min, 4°C), washed once in degassed morpholinopropanesulfonic acid (MOPS) buffer (20 mM MOPS plus mineral salts as described previously [6], pH 7.2; designated as buffer A), resuspended in a final volume of 3 to 5 ml of buffer A, and then permeabilized by addition of Triton X-100 (2% [vol/vol] final concentration) for ca. 30 min. Assays were performed in 5-ml glass vials sealed with Mininert valves. The anoxic assay mixtures (final volume, 1 ml) contained buffer A, 200 µM titanium(III) chloride, permeabilized cells corresponding to 3 to 3.5 mg of protein, and particular substrates, depending on the assay. Reactions were started by addition of permeabilized cells, and mixtures were incubated for 1 h at room temperature in an anaerobic glove box while agitated on an orbital shaker. Reactions were ended by acidification with 1 M HCl to pH <2.
Reaction mixtures were then adjusted to ca. pH 7 and treated with 60 µg of DNase I for 30 min at 4°C. Following DNase treatment, the reaction mixtures, unless noted otherwise, were alkaline treated to hydrolyze any CoA thioesters that may have formed. The pH of these samples was adjusted to
13 with 5 M KOH. The alkaline-treated reaction mixtures, following incubation for 1.5 to 2 h at room temperature, and the non-alkaline-treated reaction mixtures, directly following the DNase I treatment, were then acidified to pH
2 with
concentrated HCl and extracted three times with diethyl ether (Ultra
Resi analyzed, distilled in glass; J. T. Baker, Inc.,
Phillipsburg, N.J.). The ether extracts were dried with anhydrous
sodium sulfate, derivatized with ethereal diazomethane to convert
carboxylic acids into methyl esters, exchanged into
CH2Cl2 (Ultra Resi analyzed, distilled in
glass; J. T. Baker), and analyzed by gas chromatography-mass spectrometry (GC/MS) (9).
Assays conducted to collect kinetic data were performed as described
above with the following exceptions: (i) assay mixtures contained
permeabilized cells corresponding to 0.7 to 0.9 mg of protein; (ii)
they were conducted in 2.8-ml vials to minimize head-space volume;
(iii) they were stopped at shorter defined time intervals (e.g., 5, 10, or 15 min); and (iv) they were not alkaline treated prior to being
acidified and extracted.
Dialyzed cell extract assays. m-Xylene-grown cells of Azoarcus sp. strain T were harvested anaerobically and washed in buffer A as described above. The washed cells were resuspended in a final volume of ca. 2 ml of buffer A that had been amended with 900 µg of DNase I. Cells were broken anoxically by four passages through a French pressure cell at 138 MPa. Unbroken cells and cell debris were removed by centrifugation (27,000 × g, 15 min, 4°C). The supernatant, defined as the cell extract, was dialyzed by using membrane tubing with a molecular mass cutoff of 12 to 14 kDa for ca. 16 h against 1 liter of anaerobic buffer (buffer A amended with 1 mM DTT).
Assays were performed and treated as described above for the permeabilized cell assays, except that the assay mixtures contained dialyzed cell extract corresponding to ca. 3 mg of protein instead of permeabilized cells.Identification and quantification of reaction products by GC/MS. BS, 3-MeBS, E-PI, benzoate, and 2-, 3-, and 4-methylbenzoate were identified as methyl esters based on comparisons of GC retention times and mass spectra to authentic standards and were quantified based on their respective response factors. The 2- and 4-methyl homologs of BS, and the 2-, 3-, and 4-methyl homologs of E-PI, none of which are commercially available, were tentatively identified based on mass spectral similarities to authentic BS and E-PI standards (dimethyl esters), respectively, and were semiquantified based on the response factors of BS and E-PI standards (dimethyl esters), respectively. BS and its methyl homologs were quantified based on the abundance of the tropylium ion (m/z 91, in unlabeled BS) and the methyltropylium ion (m/z 105, in unlabeled methyl BS homologs), respectively. E-PI and its methyl homologs and benzoate and its methyl homologs were quantified based on the abundance of their base peak. Recoveries of BS and 3-MeBS tested in the absence of permeabilized cells ranged from 75 to 90%.
Cell suspension studies. Cells of m-xylene-grown Azoarcus sp. strain T were harvested anaerobically and washed in buffer A as described above. The washed cells were resuspended in a final volume of ca. 3 to 6 ml of buffer A. Assays were performed in 40-ml glass vials sealed with Mininert valves. The anoxic cell suspension mixture (total volume, 30 ml) contained buffer A, 200 µM titanium(III) chloride, ca. 200 µM m-xylene (ca. 7 µmol, total), 2.5 mM sodium nitrate, and whole cells corresponding to 4 to 6 mg of protein. The reaction was started by addition of cells. The reaction vials were incubated at room temperature in an anaerobic glove box while they were agitated on an orbital shaker. At defined time intervals, headspace samples were taken and analyzed for m-xylene by capillary GC and photoionization detection as described elsewhere (5), except that the analyses were conducted at the isothermal temperature of 110°C.
Protein determination. Protein concentrations of cell suspensions were determined by using a modified Bradford assay (Bio-Rad Laboratories, Hercules, Calif.). Bovine serum albumin was used as the standard. Whole-cell suspensions were boiled for 15 min in 3 M NaOH prior to protein determination.
Sequence analysis of the 16S rRNA gene of strain T. Strain T genomic DNA was isolated by the chloroform-phenol extraction method as described by Avery and Kaiser (3). The 16S rRNA gene was amplified by PCR with the set of primers fD1 and rD1 as described by Weisburg et al. (34), but modified by removing the linker sequences that contained restriction sites. The modified forward and reverse primers were 5'-AGAGTTTGATCCTGGCTCAG-3' and 5'-AAGGAGGTGATCCAGCC-3', respectively.
PCR was conducted according to standard methods and was carried out by using a GeneAmp PCR system 2400 (Perkin-Elmer Corp., Norwalk, Conn.). The amplified DNA fragment was purified by using the QIAquick PCR Purification kit protocol (Qiagen Inc., Chatsworth, Calif.). The purified PCR product was sequenced in both directions by the dideoxy chain termination method with labeled dideoxynucleoside triphosphates. Sequencing of the 16S rRNA gene was performed by the PAN facility (Stanford University, Stanford, Calif.), and the sequences were assembled with programs in the GCG software package (Wisconsin Package version 10.0; Genetics Computer Group, Madison, Wis.). The assembled sequence was analyzed by searching the DNA databases (GenBank, EMBL, and DDBJ) by using the BLAST (Basic Local Alignment Search Tool; release 2.0.8) server at the National Center for Biotechnology Information (1).Nucleotide sequence accession number. The 16S rRNA gene sequence of Azoarcus sp. strain T was deposited in the GenBank database under accession no. AF129465.
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RESULTS |
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Phylogenetic position of strain T.
Sequence analysis of the
16S rRNA gene of strain T (previously identified as a
Pseudomonas sp. [16]) revealed a close
similarity to several Azoarcus species (data not shown). The
closest known relative of strain T was Azoarcus evansii
KB740 (99% identity), a denitrifying bacterium capable of oxidizing a
variety of aromatic compounds under both aerobic and denitrifying
conditions (2, 12). However, unlike strain T, A. evansii KB740 is unable to degrade toluene under denitrifying
conditions (2), and its ability to degrade
m-xylene has not been reported. Strain T, however, was found
to be closely related (98 to 99% identity) to many Azoarcus spp. capable of degrading toluene (e.g., Azoarcus sp. strain
ToN1 [29] and Azoarcus tolulyticus strains
Td-3, 17, 19, and 21 [18]) and one Azoarcus
sp. capable of degrading toluene and m-xylene (A. tolulyticus Td-15 [18]). To date, denitrifying
bacteria capable of anaerobic alkylbenzene degradation appear to
cluster in the two genera Azoarcus and Thauera,
both of which are members of the
-subclass of the
Proteobacteria (2, 23, 24, 35).
In vitro anaerobic oxidation of m-xylene to 3-methylbenzoate. Under denitrifying conditions, Azoarcus sp. strain T oxidizes m-xylene to carbon dioxide (16) via 3-methylbenzoate as a transient intermediate (30). We used permeabilized cells of m-xylene-grown Azoarcus sp. strain T to investigate whether m-xylene is oxidized to 3-methylbenzoate via 3-MeBS and E-3-MePI (Fig. 1). Anoxic assays were conducted as described in Materials and Methods. Following incubation for 1 h, reaction products were acidified, derivatized to methyl esters, extracted, and then analyzed by GC/MS.
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3-MeBS synthase reaction: retention of the abstracted H atom from the m-xylene methyl carbon in 3-MeBS. Close inspection of the mass spectrum of deuterium-labeled 3-MeBS (dimethyl ester) (Fig. 2B) formed from m-xylene-d6 and fumarate revealed that the H atom abstracted from the methyl carbon of m-xylene during addition to fumarate is retained in the succinyl moiety of 3-MeBS. Retention of the abstracted H atom from m-xylene in 3-MeBS can be observed by comparing the mass/charge ratios of the molecular and methyltropylium ions of the unlabeled and labeled dimethyl esters of 3-MeBS (Fig. 2). For a more detailed explanation of how such a mass spectrum can be interpreted to illustrate the retention of the abstracted H atom in 3-MeBS, see Beller and Spormann (6). The H atoms abstracted from the methyl carbon of toluene (6), o-xylene (6), and p-xylene (data not shown) during analogous fumarate addition reactions were also found to be retained in the corresponding BS homologs, suggesting that the mechanism of these reactions may be similar.
Specific rate of in vitro 3-MeBS formation.
Five separate
kinetic experiments were conducted to determine the specific rate of in
vitro 3-MeBS formation in assay mixtures containing
m-xylene-d6 (300 nmol, total; 200 µM, liquid concentration), fumarate (500 µM), and permeabilized
cells of m-xylene-grown Azoarcus sp. strain T
(ca. 0.8 mg of protein). The average specific rate of 3-MeBS formation
was 1.5 nmol · min
1 · (mg of
protein)
1 (standard deviation [SD] = 0.4). Figure
4 depicts the results from one such
experiment.
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Primary kinetic isotope effect in the 3-MeBS synthase
reaction.
Since the 3-MeBS synthase reaction involves the transfer
of an H atom from the methyl carbon of m-xylene to the
product, 3-MeBS, we investigated whether a kinetic isotope effect is
associated with this reaction. The specific rates of in vitro 3-MeBS
formation from unlabeled m-xylene and from deuterium-labeled
m-xylene (m-xylene-d6) were determined in two parallel experiments conducted with the same
batch of permeabilized cells. Each experiment contained fumarate (500 µM), permeabilized cells (ca. 0.8 mg of protein), and either (i)
unlabeled m-xylene (300 nmol, total; 200 µM, liquid
concentration) or (ii) deuterium-labeled m-xylene
(m-xylene-d6; 300 nmol, total; 200 µM, liquid concentration). The specific rates of 3-MeBS formation from unlabeled and deuterium-labeled m-xylene were found to
be 3 and 1 nmol · min
1 · (mg of
protein)
1, respectively (Fig.
5). Thus, 3-MeBS formation from unlabeled m-xylene was ca. 3 times faster than that from
deuterium-labeled m-xylene. A kinetic isotope effect with a
similar magnitude
(kobs,H/kobs,D = ca.
3) was also observed in assays that initially contained equimolar
concentrations of unlabeled m-xylene (150 nmol, total; 100 µM, liquid concentration) and deuterium-labeled m-xylene
(m-xylene-d6; 150 nmol, total; 100 µM, liquid concentration), as well as fumarate (500 µM), and
permeabilized cells (ca. 0.8 mg of protein) (data not shown).
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Specific rate of in vivo m-xylene consumption.
To
compare the specific rate of in vitro 3-MeBS formation with the
specific rate of in vivo m-xylene consumption, four separate kinetic experiments were conducted with cell suspensions of
m-xylene-grown Azoarcus sp. strain T. These
experiments were amended with m-xylene (7 µmol, total; 200 µM, liquid concentration), nitrate (2 mM), and whole cells (4 to 6 mg
of protein). The average specific rate of m-xylene
consumption by whole-cell suspensions was 20 nmol · min
1 · (mg of protein)
1 (SD = 6). This range of rates is comparable to that calculated for
m-xylene consumption by cells of Azoarcus sp.
strain T growing under denitrifying conditions with m-xylene
as the sole carbon and electron source (10 to 25 nmol · min
1 · (mg of protein)
1 at a
doubling time of 27 h [data not shown]). It should be noted that
the doubling time of Azoarcus sp. strain T growing under similar conditions has ranged from 16 to 27 h (data not shown). Variable growth rates for Azoarcus sp. strain T were also
observed by Dolfing et al. (16).
In vitro anaerobic oxidation of toluene and o- and
p-xylene to the corresponding benzoate homologs.
We
investigated whether permeabilized cells of m-xylene-grown
Azoarcus sp. strain T could transform methylbenzenes other
than m-xylene. Each permeabilized cell assay was amended
with fumarate, succinyl-CoA, nitrate, and one of the following
methylbenzenes, toluene or o- or p-xylene. Assays
amended with toluene yielded BS, E-PI, and benzoate (Table
3). Assays amended with
p-xylene yielded products tentatively identified as the
4-methyl homologs of BS and E-PI, as well as
4-methylbenzoate (Table 3). And assays amended with o-xylene
yielded the tentatively identified 2-methyl homologs of BS and
E-PI (Table 3). 2-Methylbenzoate was detected in the
o-xylene assays, but the concentration was too low to
quantify (i.e., less than 1 nmol) (Table 3).
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In vitro anaerobic oxidation of m-xylene to 3-methylbenzoate by toluene-grown cells. We investigated whether toluene-grown cells of Azoarcus sp. strain T could also transform m-xylene to 3-methylbenzoate via 3-MeBS and E-3-MePI. An assay mixture containing m-xylene-d6 (360 nmol, total; 170 µM, liquid concentration), fumarate (500 µM), succinyl-CoA (300 µM), nitrate (2 mM), and permeabilized cells of toluene-grown Azoarcus sp. strain T (ca. 3 mg protein) yielded the following deuterium-labeled products: 3-MeBS (150 nmol), E-3-MePI (15 nmol), and 3-methylbenzoate (40 nmol). When 3-MeBS (150 nmol) was substituted for m-xylene and fumarate in a similar assay mixture, 3-MeBS was transformed to E-3-MePI (20 nmol) and 3-methylbenzoate (15 nmol). These findings indicate that enzymatic activities for anaerobic oxidation of m-xylene to 3-methylbenzoate via 3-MeBS and E-3-MePI (Fig. 1) are also present in toluene-grown cells of Azoarcus sp. strain T.
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DISCUSSION |
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We investigated the enzymatic steps in anaerobic m-xylene oxidation to 3-methylbenzoate in permeabilized cells and dialyzed cell extracts of m-xylene-grown Azoarcus sp. strain T. Based on the following experimental evidence, we propose that Azoarcus sp. strain T oxidizes m-xylene to 3-methylbenzoate (or its CoA thioester) via the transient intermediates, 3-MeBS and E-3-MePI (or its CoA thioester) (Fig. 1). Permeabilized cells of Azoarcus sp. strain T catalyzed the transformation of deuterium-labeled m-xylene to deuterium-labeled 3-MeBS by the addition of m-xylene-d6 to fumarate (Table 1 and Fig. 2B). Furthermore, when succinyl-CoA and nitrate were amended to assays containing m-xylene-d6 and fumarate, permeabilized cells catalyzed the transformation of m-xylene-d6 to E-3-MePI and 3-methylbenzoate in addition to 3-MeBS (Table 1). All three transformation products, 3-MeBS, E-3-MePI, and 3-methylbenzoate, were labeled with deuterium atoms originating from m-xylene-d6. Permeabilized cells also catalyzed the oxidation of 3-MeBS to E-3-MePI and 3-methylbenzoate (Table 1), suggesting that 3-MeBS is an intermediate in anaerobic m-xylene oxidation to 3-methylbenzoate.
Although we could not directly demonstrate the presence of the CoA thioesters of E-3-MePI and 3-methylbenzoate, circumstantial evidence suggests that they are formed. E-3-MePI (or its CoA thioester) formation was found to be dependent on a source of activated CoA (e.g., succinyl-CoA or CoA plus ATP) (Table 2), and the CoA thioester of benzoate was formed from toluene (6, 11) in a series of reactions analogous to those demonstrated for anaerobic m-xylene oxidation to 3-methylbenzoate (or 3-methylbenzoyl-CoA).
Assuming that the CoA thioesters of E-3-MePI and
3-methylbenzoate are formed, we postulate that 3-MeBS is oxidized to
3-methylbenzoyl-CoA via the following reactions. 3-MeBS is activated to
its CoA thioester, which is subsequently oxidized to
E-3-MePI-CoA via steps resembling
-oxidation of fatty
acids. E-3-MePI-CoA is then oxidized to 3-methylbenzoyl-CoA via one of two pathways recently proposed for E-PI-CoA
oxidation to benzoyl-CoA (6, 11).
Several lines of evidence suggest that the reactions demonstrated here
for anaerobic m-xylene oxidation to 3-methylbenzoate (or
3-methylbenzoyl-CoA) (Fig. 1) are the initial steps in anaerobic m-xylene mineralization in Azoarcus sp. strain T. First, permeabilized cells of Azoarcus sp. strain T were
found to transform 3-MeBS to 3-methylbenzoate, which is a known
transient intermediate of anaerobic m-xylene mineralization
in Azoarcus sp. strain T (30). Second, 3-MeBS and
E-3-MePI have been tentatively identified by GC/MS as
transformation products of an m-xylene-metabolizing culture of Azoarcus sp. strain T (4). Third, kinetic
studies demonstrated that the specific rate of in vitro 3-MeBS
formation (ca. 3 nmol · min
1 · [mg of
protein]
1) (Fig. 5) can account for greater than 15% of
the average specific rate of in vivo m-xylene consumption
(ca. 20 nmol · [mg of protein]
1).
While 15% is significant in itself, it is a conservative estimate
because it is based on a rate of 3-MeBS formation that is presumed to
be at the low end of the range of rates representative of different
cell batches. This assumption is based on the fact that the rate of
3-MeBS-d6 formation determined in a parallel experiment using the same batch of permeabilized cells was found to be
1.25 SDs less than the average rate determined from five separate
experiments (1.5 nmol · min
1 · mg of
protein
1 [SD = 0.4]). Furthermore, the 3-MeBS
synthase activity is extremely oxygen sensitive. Considering these
factors, our results suggest that the putative 3-MeBS synthase (or BS
synthase) is present in Azoarcus sp. strain T at specific
activities that are sufficient to account for in vivo anaerobic
m-xylene mineralization. As anaerobic m-xylene
mineralization is studied in more bacterial species, it will be
interesting to observe whether the pathway demonstrated here (Fig. 1)
is a general pathway for anaerobic m-xylene mineralization or whether it is unique to Azoarcus sp. strain T.
Although the prevalence of this pathway in other m-xylene-mineralizing bacteria is not yet known, findings from our study in combination with those from previous studies of toluene mineralization suggest that the fumarate addition reaction may be a general metabolic strategy for activating methylbenzenes in the absence of molecular oxygen. Toluene-mineralizing, denitrifying (6, 11, 28), and sulfate-reducing (7, 28) bacteria were shown to activate toluene by a fumarate addition reaction analogous to the one demonstrated for m-xylene. The mechanism of these fumarate addition reactions is not yet fully understood; however, they are believed to involve a glycyl radical (8, 15, 23, 25).
Observations of a kinetic deuterium isotope effect in the 3-MeBS synthase reaction (kobs,H/kobs,D = ca. 3) (Fig. 5) and the BS synthase reaction (conducted with toluene-d8 and fumarate; kobs,H/kobs,D = ca. 3) (data not shown) suggest that cleavage of a C-H bond contributes measurably to the overall rate of reaction. Based on a recently proposed radical reaction mechanism for the BS synthase reaction (8), one or two of the rate-determining steps in such fumarate addition reactions may be (i) abstraction of the H atom from the methyl carbon of m-xylene (or toluene) by the free radical-containing enzyme and/or (ii) abstraction of the H atom from the enzyme intermediate. However, it cannot be ruled out that introduction of deuterated methyl groups in m-xylene and toluene may have altered the rate-determining step(s) in the respective 3-MeBS and BS synthase reactions and thereby produced the observed kinetic isotope effect.
Since the reactions demonstrated here for anaerobic m-xylene
oxidation to 3-methylbenzoate (or its CoA thioester) (Fig. 1) are
analogous to those of anaerobic toluene oxidation to benzoyl-CoA (6, 11), we conducted preliminary studies to investigate whether any of the corresponding initial reactions in the oxidation of
m-xylene and toluene may be catalyzed by the same enzyme.
The catalytic activity and specificity of enzymes induced during
anaerobic growth on m-xylene or toluene were characterized
and compared in an attempt to differentiate between enzymes involved in
the two pathways. However, regardless of whether Azoarcus
sp. strain T was grown on m-xylene or toluene, permeabilized
cells catalyzed both the 3-MeBS and the BS synthase reactions, and they
did so at similar specific activities. The average specific rates of 3-MeBS-d6 formation by m-xylene-grown
and toluene-grown cells were 1.5 nmol · min
1
· (mg of protein)
1 (this study) and 1.6 nmol · min
1 · (mg of protein)
1 (data not
shown), respectively. The specific rates of
BS-d8 formation by m-xylene-grown and
toluene-grown cells were 4.1 nmol · min
1 · (mg of protein)
1 (data not shown) and 4.9 nmol · min
1 · (mg of protein)
1
(6), respectively.
Permeabilized cells of m-xylene-grown and toluene-grown Azoarcus sp. strain T also catalyzed an analogous fumarate addition reaction with o- or p-xylene as the substrate, forming the corresponding BS homolog (this study, data not shown, and reference 6). We also investigated whether m-xylene- and toluene-grown cells of Azoarcus sp. strain T could transform toluene and o- and m-xylene beyond the BS homologs to the corresponding E-PI and benzoate homologs. Again, regardless of whether cells of Azoarcus sp. strain T were grown on m-xylene or toluene, they catalyzed the same reactions. Permeabilized cells of m-xylene- and toluene-grown Azoarcus sp. strain T catalyzed the transformation of toluene and m-xylene to their respective homologs of BS, E-PI, and benzoate, and they catalyzed the transformation of o-xylene to the tentatively identified 2-methyl homologs of BS and E-PI (this study and reference 6).
Since no differences were observed in the specific activities or substrate specificities of the enzymes induced during anaerobic growth on m-xylene or toluene, the corresponding initial reactions in the proposed pathways of anaerobic m-xylene oxidation to 3-methylbenzoate (or 3-methylbenzoyl-CoA) and anaerobic toluene oxidation to benzoyl-CoA may be catalyzed by either (i) the same enzyme, (ii) distinct enzymes specific for each pathway, but induced during growth on either m-xylene or toluene, or, (iii) a combination of possibilities i and ii for the individual initial reactions. Molecular and genetic experiments in our laboratory are currently in progress to differentiate between these possibilities. Although genetic analysis is required to elucidate this matter, circumstantial evidence suggests that the same enzymes may catalyze the corresponding initial reactions in anaerobic oxidation of m-xylene and toluene to their respective benzoate (or benzoyl-CoA) homologs. Although T. aromatica is unable to grow on m-xylene, it too has the enzymatic capability to oxidize m-xylene to 3-methylbenzoate (or 3-methylbenzoyl-CoA), as demonstrated in dense suspensions of toluene-grown cells (10).
| |
ACKNOWLEDGMENTS |
|---|
Funding for this study was provided by the National Science Foundation (MCB-9733535 and MCB-9723312), by an OTL Research Incentive Fund (Stanford University), and by the U.S. Department of the Navy, under agreement N-47408-96-C-3342. Additional support was provided through fellowships to C.J.K. from the Stanford-NIH Graduate Training Program in Biotechnology and from Achievement Rewards for College Students (ARCs).
We thank J. Tiedje, J. Frost, J. Chee-Sanford, and M. Migaud (Michigan State University) for providing authentic E-PI. We thank Bettina Rosner for technical advice.
| |
FOOTNOTES |
|---|
* Corresponding author. Mailing address: Environmental Engineering and Science, Department of Civil and Environmental Engineering, Stanford University, Stanford, CA 94305-4020. Phone: (650) 723-3668. Fax: (650) 725-3164. E-mail: spormann{at}ce.stanford.edu.
Present address: Lawrence Livermore National Laboratory, Livermore,
CA 94551.
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