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Applied and Environmental Microbiology, September 1998, p. 3305-3312, Vol. 64, No. 9
Institut für Biochemische
Pflanzenpathologie1 and
Institut
für Ökologische Chemie,2
GSF
Received 13 March 1998/Accepted 12 June 1998
Phanerochaete chrysosporium ATCC 34541 has been
reported to be unable to mineralize 3,4-dichloroaniline (DCA). However,
high mineralization is now shown to occur when a fermentation
temperature of 37° and gassing with oxygen are used.
Mineralization did not correlate with lignin peroxidase activity. The
latter was high under C limitation and low under N limitation, whereas
the reverse was true for mineralization. The kinetics of DCA metabolism
was studied in low-N and low-C and C- and N-rich culture media by metabolite analysis and 14CO2
determination. In all cases, DCA disappeared within 2 days, and a novel
highly polar conjugate termed DCAX accumulated in the growth
medium. This metabolite was a dead-end product under C and N
enrichment. In oxygenated low-C medium and in much higher yield in
oxygenated low-N medium, DCAX was converted to DCA-succinimide and then mineralized. DCAX was purified by high-performance liquid chromatography and identified as
N-(3,4-dichlorophenyl)- In 1985, it was discovered that the
white fungus Phanerochaete chrysosporium ATCC
24725 has a unique ability to mineralize free and lignin-bound
chloroanilines (1). The fungus produced about the same high
yield of 14CO2 regardless of whether the
14C label was in the lignin-bound chloroaniline, the
natural lignin subunit (coniferyl alcohol), or the free chlorinated
anilines. The unique capability of P. chrysosporium for mineralization of xenobiotics was also
discovered for polychlorinated biphenyls (7) as well as
TCDD, DDT, benzo[a]pyrene, and chlorinated biphenyls (6). Numerous reports on the successful mineralization of
additional xenobiotics have since appeared (for reviews, see
references 4, 12, and 26). The
initial report on the mineralization of free and lignin-bound
chloroanilines was further confirmed by studies on the
mineralization of a chloroaniline-lignin metabolite fraction from wheat
(2). A fungal lignin peroxidase preparation was found to
react rapidly with chlorinated anilines, but the main reaction was
oligomerization rather than ring opening. The highly toxic
3,4,3',4'-tetrachloroazobenzene and other condensation products were
formed (23, 23a). More complex condensation products of 3,4-dichloroaniline (DCA) have been characterized from another white
rot fungus (16). In addition, fungi are known to
transform anilines to the N-formyl, N-malonyl,
N-acetyl, N-succinyl,
N-hydroxyglutaryl, and N-glucosyl conjugates
(11, 27, 28) as well as to unusual cyclic succinimides
(3). More recently, chlorinated anilines and herbicides
tightly complexed with native plant cell wall components were found to
be mineralized in high yield (20). P. chrysosporium was successfully used in a two-stage
fermentation system to clean soil heavily contaminated with polycyclic
hydrocarbons (19).
Our initial results have been confirmed with the same strain 24725 (21) as well as with P. chrysosporium 32629 (10). However, our
earlier work has also been attributed to experimental artifacts, and
P. chrysosporium ATCC 34541 was reported to
be unable to mineralize DCA (11). It has been postulated
that P. chrysosporium is no different
from other soil fungi, which generally have only a low capability for the mineralization of chloroanilines (24,
27).
The initial purpose of the present work was to define optimal
fermentation conditions. In addition, a new intermediate of mineralization was discovered when the kinetics of mineralization were
studied. This metabolite, termed DCAX, is now identified as
N-(3,4-dichlorophenyl)- Chemicals.
All chemicals used in this study were of
analytical grade. The high-performance liquid chromatography (HPLC)
solvents used were from Riedel-de-Haën.
3,4-Dichloro[U-14C]aniline was obtained and purified as
previously described (1, 20). Reference substances were
generally from our laboratory collection (3, 23, 23a, 28).
Fungal strains and kinetic fermentation studies.
P.
chrysosporium ATCC 24725 and 34541 were maintained on
malt extract agar (1) and grown under the previously
described conditions in either static culture (2.0-liter Fernbach flask with 100 ml of medium and no detergent or veratryl alcohol added [1, 11]) or agitated cultures (250-ml Erlenmeyer flask
with 0.1% [wt/vol] Tween 80 and 1.5 mM veratryl alcohol added [cf. reference 20]). The composition of the N-limited,
C-limited, and C- and N-rich growth media were as described previously
(1, 14). A fungal spore suspension was used for inoculation
with 1.3 · 106 spores/100 ml of medium. The agitated
cultures were shaken (150 rpm, 37°C) for 3 days to allow the fungal
mycelium to develop. The culture medium was then reduced from 100 to 40 ml, and the agitation speed was set to 60 rpm. The
14C-labelled test chemical was added, and incubation was
continued, with flushing with pure oxygen twice per week.
14CO2 development was monitored as described
previously (1, 20). All kinetic experiments were performed
with 100 µM [14C]DCA (1.5 · 106
dpm). Immediately following flushing with oxygen, 1 ml of growth medium
was removed. A sample of 500 µl was directly employed for HPLC
analysis of metabolites. Radioactivity (1, 20) and lignin peroxidase activity (20) were also determined. One unit of
lignin peroxidase activity is defined as catalyzing the oxidation of 1.0 µmol of veratryl alcohol/min. The growth media were directly extracted with ethyl acetate to obtain DCASI as a major product (cf.
reference 3). Prior acidification with
KH2PO4 also allowed extraction of DCAX with
ethyl acetate (28). General fermentation conditions were as
previously reported (1, 20). Total radioactivity associated
with the mycelium was determined by combustion.
Metabolite isolation.
Because of the rapid decline in
N-limited cultures (26, 28), C- and N-rich medium (40 ml)
was selected for isolation of DCAX. For this purpose,
[U-14C]DCA (38.5 kBq, 4.0 µmol, 23 days of incubation),
nonradioactive DCA (4.0 µmol, 10 day of incubation), or
nonradioactive DCASA (53.4 µmol, 10 days of incubation) was applied
to 3-day-old cultures of P. chrysosporium.
Incubation was at 39°C and 70 rpm, with oxygen flushing every 2 days.
Medium samples of 500 µl were analyzed by HPLC to monitor the
formation of DCAX.
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
A New Intermediate in the Mineralization of
3,4-Dichloroaniline by the White Rot Fungus
Phanerochaete chrysosporium

and
Forschungszentrum für Umwelt und Gesundheit GmbH,
D-85764 Oberschleißheim, Germany
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ABSTRACT
Top
Abstract
Introduction
Materials & Methods
Results
Discussion
References
-ketoglutaryl-
-amide by
high-performance liquid chromatography and mass spectroscopy, gas
chromatography and mass spectroscopy, and nuclear magnetic resonance
spectroscopy. The formation of conjugate intermediates is proposed to
facilitate mineralization because the sensitive amino group of DCA
needs protection so that ring cleavage rather than oligomerization can
occur.
![]()
INTRODUCTION
Top
Abstract
Introduction
Materials & Methods
Results
Discussion
References
-ketoglutaryl-
-amide by
isolation from C- and N-rich medium and by standard spectroscopic
techniques. A hypothetical mechanism for the formation of this
metabolite and its conversion to the succinimide is given. Some of the
results have been described briefly (26, 29).
![]()
MATERIALS AND METHODS
Top
Abstract
Introduction
Materials & Methods
Results
Discussion
References
18°C. The
conversion rates of DCA to DCAX were 84% (23 days) and 62% (10 days),
and that of DCASA was 9.6% (10 days).
Thin-layer chromatography (TLC). Precoated fluorescent silica gel G 60F254 plates (Merck no. 5554) were used with an ethyl acetate-2-propanol-water solvent system (6:2:1 [by volume]). Rf values were 0.11 for DCAX, 0.50 for DCASA, 0.57 for N-glucosyl-DCA, 0.76 for DCASI, and 0.80 for DCA.
HPLC.
Samples (500 µl each) from the incubation medium of
the kinetic experiments were analyzed by reversed-phase HPLC (see
reference 20) on a Lichrosphere RP8 column (16 by
250 mm). The gradient for the analysis of metabolites was formed
between solvent system A (water containing 100 µl · 1
1 trifluoroacetic acid) and solvent B
(acetonitrile-water containing 100 µl · liter of
trifluoroacetic acid
1 [9:1 by vol]). Over a total
time period of 24 min, a stepwise elution program from 100% solvent
system A to 100% solvent B was applied. UV detection was at 210 and
245 nm. Radioactivity was monitored with an LB503 radiomonitor
(Berthold, Wildbach, Germany). The column was calibrated with authentic
reference compounds. The following retention times were obtained: for
N-glucosyl-DCA, 12.2 min; for N-malonyl-DCA, 16.2 min; for DCA-succinimide, 17.6 min; for N-acetyl-DCA, 18.2 min; and for DCA, 18.3 min. DCAX appeared at a retention time of 11.6 min.
Metabolite purification.
The lyophilized culture medium was
dissolved in 5 ml of water and passed through an RP18 cartridge (500 mg; Merck no. 1.19849.001). DCAX remained stable in this solution when
stored at 4°C. Reversed-phase HPLC was carried with a Spherisorb
C8 column (125 by 4.6 mm in diameter) connected to a
C8 guard column (28 by 4.6 mm in diameter) (particle size,
5 µm; Bischoff). The eluent was formed between solvent A (water) and
solvent B (89.4% acetonitrile and 0.6% methanol in water) according
to the following program (1 min 10% B, 2 min 10% B, 5 min 20% B, 8 min 40% B, 13 min 45% B, 15 min 50% B, 20 min 60% B, 24 min 100%
B, 28 min 100% B, and 30 min 0% B) at a flow rate of 0.6 ml/min. The
column had been calibrated for analysis with the following authentic
samples: N-(3,4-dichlorophenyl)glucoside (retention time
[Rt], 10.4 min),
N-(3,4-dichlorophenyl)-
-ketoglutaryl-
-amide (DCAKGA; Rt, 12.1 to 13.7 min),
N-(3,4-dichlorophenyl)-succinamide (DCASA;
Rt, 15.7 to 16.2 min),
N-(3,4-dichlorophenyl)-succinimide (DCASI;
Rt, 19.5 to 21.2 min),
N-(3,4-dichlorophenyl)-acetanilide (Rt, 22.1 to 22.2 min), and free
3,4-dichloroaniline (DCA; Rt, 22.6 to 22.9 min).
For comparison, the Rt values of the authentic samples on a Spherisorb ODSII C18 column (125 by 4.6 mm in
diameter; particle size, 5 µm; Knauer) without a precolumn were
also determined for the same gradient as follows: for
N-(3,4-dichlorophenyl)-glucoside, 11.3 min; for DCAKGA, 13.3 min; for DCASA, 14.6 min; for DCASI, 19.8 min; for
N-(3,4-dichlorophenyl)-acetanilide, 20.7 min; and for free
DCA, 22.0 min. The UV signal was detected at 250 nm (UV detector model
757; Applied Biosystems), and the radioactivity signal was monitored
on-line with a solid yttrium glass scintillator (HPLC radioactivity
detector model LB 505; Berthold, Wildbad, Germany). Samples of 500 µl
of undiluted culture medium or the enriched DCAX solution (see above)
were injected into the HPLC system.
Chemical syntheses. N-(3,4-Dichlorophenyl)-acetanilide, DCASA, and N-(3,4-dichlorophenyl)-succinimide were synthesized essentially as described previously (2, 11, 28).
Synthesis of
N-(3,4-dichlorophenyl)-
-ketoglutaryl-
-amide.
The
synthesis of DCAKGA was performed in two steps. First,
-ketoglutaric
anhydride was synthesized in a manner analogous to succinic anhydride
synthesis (9, 22). In the second step, DCAKGA was
synthesized from
-ketoglutaric anhydride and DCA. In a closed
system, 12 mmol of
-ketoglutaric acid was suspended in 10 ml of dry
benzene and 24 mmol of acetic acid anhydride was slowly added. The
-ketoglutaric acid crystals slowly dissolved under warming and
occasional shaking. The solution was then transferred to an ice bath.
Dry petrol ether (40 to 60°C) was added in small amounts until an
amorphous solid mass precipitated. The latter was washed several times
with dry petrol ether (40 to 60°C), with dry benzene added in order
to remove excess acetic acid and acetic acid anhydride. The amorphous
solid mass was dried in vacuo at ambient temperature and finally dried
under a stream of nitrogen. In the second step, the crude
-ketoglutaric anhydride was dissolved in 45 ml of dry dioxane and
6.2 mmol of DCA was added portionwise. The solution was stirred at
ambient temperature for 3 days. After 3 days, the solution was
concentrated in vacuo at ambient temperature to ca. 5 ml. Precipitation
of DCAKGA was induced by the addition of dry diethyl ether-petrol ether
(40 to 60°C), 1:2 (vol/vol). The precipitate was washed with dry
diethyl ether in order to remove
-ketoglutaric anhydride as well as
DCA and DCA-acetanilide. The crystalline solid mass was dried under
nitrogen and stored under nitrogen at
18°C. The yield of DCAKGA
(melting point, 204 to 205°C) was about 62%, as shown by HPLC. In
addition, DCA-acetanilide (27%) was detected by HPLC and
1H-nuclear magnetic resonance (NMR) spectroscopy. This
compound appeared to be formed from residual acetic anhydride. The
investigation of the reaction product with 2D-HH-COSY-NMR spectroscopy
allowed us to separate the signals of the main product (DCAKGA) from
those of the by-product (DCA-acetanilide). The authenticity of DCAKGA was further demonstrated by HPLC-mass spectrometry-mass spectrometry (MS-MS) (see Results).
Combined HPLC-MS. Combined HPLC-MS was conducted with a single quadrupole (Fisons, Mainz, Germany) as well as a triple-stage quadrupole MS system (TSQ 7000; Finnigan MAT, Bremen, Germany). When coupled with HPLC, an acid-free acetonitrile-water gradient on a reversed-phase C18 column (250 by 4.6 mm in diameter [Fisons] and 150 by 4.5 mm in diameter [Finnigan MAT]) was used. The column was connected to the MS system via an electrospray interface. All mass spectra were acquired in the negative ion mode at a typical scan rate of 110 to 167 amu/s. By triple-quadrupole MS, the fragmentation of DCAX and DCASA was achieved with argon as a collision gas (1 mTorr) and atmospheric pressure ionization-collision-induced dissociation at the upfront, whereas synthetic DCAKGA was fragmented by atmospheric pressure ionization-chemical ionization. The collision-induced dissociation spectra of DCASA, DCAKGA, and DCAX were obtained at energies of 35, 50, and 50 eV, respectively. The atmospheric pressure ionization-chemical ionization mass spectrum of synthetic DCAKGA was available at 5 eV energy, and the daughter ion (m/z, 288) mass spectrum of DCAKGA was available at 18 eV.
Combined GC-MS.
The experimental conditions of the combined
GC-MS were as follows. GC was done with a 30 m by 0.25 mm MS
select (fused silica ITP-Pro, DB-5) column, an injector temperature of
250°C, an initial oven temperature of 80°C and an initial hold of 3 min, a final temperature of 260°C at an increment of 30°C per
minute, and a final hold of 10 min. MS was done with a source
temperature of 150°C, a source emission current of 400 mA, 70 eV of
electron energy, and CI-reagent gas methane at 10
6 Torr
in the source. The mass spectrometer (TSQ 7000; Finnigan MAT) was run
in the negative mode.
1H-NMR spectroscopy.
1H-NMR spectra
were obtained with a Bruker-AC 400 NMR spectrometer (400.13 MHz) at
30°C in acetone-d6 (
= 2.04 ppm) and/or methanol-d4 (
= 3.30 ppm) at 303 K with a 5-mm inverse
geometry probe (90° = 8.5 µs).
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RESULTS |
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Optimal fermentation conditions. The original work of the efficient mineralization of DCA was carried out with P. chrysosporium ATCC 24725 (1). However, P. chrysosporium strain ATCC 34541 was reported to be unable to mineralize DCA (11). Hallinger et al. (11) attributed the earlier mineralization results to experimental artifacts. No data that could resolve the controversy have been published since. ATCC strains 24725 and 34541 have now been compared in the two reported fermentation regimes which both use the standard N-limited growth medium (14). The time courses of 14CO2 development from 3,4-dichloro[U-14C]aniline are shown in Fig. 1. Both fungal strains were effective mineralizers under the original conditions (1), i.e., 37°C and gassing with pure oxygen in 2.0-liter flasks. It made no difference whether 14CO2 was collected after passage through a polyurethane plug in 2-aminoethanol (1, 2) or in 1 M NaOH (11). Both strains were inactive under the conditions described by Hallinger et al. (11), i.e., at 27°C and gassing with air in 0.2-liter flasks. When an inactive culture was transferred to 37°C and aerated with oxygen, there was a rapid development of mineralization activity. A similar observation was made with static C-limited cultures that exhibited a low mineralization rate. When C limitation was ended by the addition of 5 mM D-glucose, there was an immediate increase in 14CO2 development (28). Therefore, inactive fungal cultures remain competent for mineralization when transferred to optimal conditions.
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Lignin peroxidase production.
Lignin peroxidase production in
low-N cultures began between fermentation days 2 and 4 (cf. reference
20). Optimal induction in shake cultures has been
reported to require C limitation and the addition of veratryl alcohol
as well as the detergent Tween 80 (18). This could be
confirmed in our study (28). Lignin peroxidase activity
(units · liter
1 in agitated cultures) were 40 ± 20 (mean ± standard deviation) under N limitation, 150 ± 30 under C limitation, and <10 in C- and N-rich medium. Total lignin
peroxidase activity did not correlate with the extent of mineralization
in the three different growth media, since mineralization was high
under N limitation and very low under C limitation (see below). These
results did not exclude the possibility that mineralization required a
low amount of basal lignin peroxidase activity.
Intermediates of mineralization. Incubation of an N-limited static culture with [U-14C]DCA led upon ethyl acetate extraction to the succinimide conjugate as the main soluble metabolite (3). A systematic comparison of N-limited, C-limited, and C- and N-rich growth media has now been performed with HPLC metabolite analysis as shown in Fig. 2. In all three growth media, DCA disappeared within 2 days of application, with the concomitant appearance of a highly polar metabolite that was termed DCAX (Rt, 11.6 min). The time courses determined in the three growth media are shown in Fig. 3. The HPLC profiles obtained with N-limited growth medium showed that DCAX was high after 2 days (Fig. 2). This was followed by a rapid decline (Fig. 3) with a concomitant rise of DCASI, which reached a maximum at day 10. DCASI then declined in favor of CO2 development. In C-limited and even more in C- and N-rich medium, DCAX remained high as a dead-end metabolite up to day 21. There were much lower amounts of DCASI, and CO2 formation was very low (C limitation) or not detectable (C- and N-rich medium). Smaller amounts (<20%) of additional metabolites were detected (unidentified products as well as N-glucosyl-DCA [cf. reference 30] and DCASA [cf. reference 3]). These minor metabolites could not be correlated with 14CO2 development and are not documented here. Mean total recoveries of 14C over the nine time points per kinetic experiment were 99.9% ± 11.3% (N limitation), 98.6% ± 8% (C limitation), and 100.0% ± 5.1% (C- and N-rich medium). The representative test series shown in Fig. 3 was reproduced three times under slightly different experimental conditions. Treatment of incubation medium with ethyl acetate led to the selective extraction of DCASI (cf. reference 3). After acidification with KH2PO4, DCAX could also be extracted with ethyl acetate, but it decomposed slowly to material chromatographing near the DCASI standard (Rf, 0.7; TLC analysis [28]). Fungal mycelium never contained more than 2 to 5% of applied radioactivity. In the case of N limitation, DCASI was the main mycelial component (TLC analysis [28]).
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Isolation of DCAX.
The new intermediate DCAX was labile upon
solvent extraction, even though it was quite stable in C- and N-rich
growth medium at pH 4 to 5 (26, 28). Therefore, no solvent
extraction of DCAX from the C- and N-rich culture medium with organic
solvents was performed. Instead, DCAX from the C- and N-rich cultures
was purified by lyophilization and HPLC with a step-wise gradient from
water to organic solvent. The collected fraction
(Rt, 12.1 min) was dried under a stream of
N2 and could be stored under N2 at
18°C for
several weeks without significant decomposition.
Chemical structure of DCAX.
DCAX and synthetic DCAKGA
had the same Rts of 12.1 and 13.3 min upon
C8 and C18 reversed-phase HPLC, respectively.
The purified DCAX fraction was analyzed by combined HPLC-MS after being
dissolved in CH3CN-MeOH (1:1). A main product at an
Rt of 10.9 min and a by-product at an
Rt of 17.45 min appeared upon combined HPLC-MS (electrospray ionization, negative mode). The UV analog signals (at 250 nm) agreed with the mass scan maxima at the calculated values of
m/z 288 ([M-H]
; DCAKGA;
Rt, 10.9 min] and m/z 260 ([M-H]
; DCASA; Rt, 17.45 min).
Both peaks showed the isotope cluster for two chlorine atoms. This
result was confirmed by three independent HPLC-MS systems (data not
shown). The mass spectra obtained with the [14C]DCAX
sample and with synthetic DCAKGA are shown in Fig.
4. The proposed fragmentation pattern is
indicated. The fragment with an m/z of 288 led to major
daughter ions at m/z of 160, 216 and 244. The latter
fragments corresponded to the 3,4-dichloroaniline fragment and to
fragments due to the loss of the -COOH and -CO-COOH groups. Incubation
of the fungus with DCASA (instead of DCA) in C- and N-rich medium also
led to the formation of DCAX, which was identified by direct HPLC-MS
analysis showing a mole peak at m/z 288 ([M-H]
) with an isotope cluster for two chlorine atoms.
Fungal mycelium was found to contain arylacylamidase activity for DCASA
(0.73 pkat/mg of soluble protein) (data not shown). The presence of a
COOH group in DCAX was further demonstrated by methylation and HPLC on
the reversed-phase C8 column (Rt,
11.2 min). The mass spectra of methylated DCAX and DCAKGA were
identical and indicated that the -NH- and the -CO2H groups
had both been methylated (Fig. 5).
Synthetic DCAKGA was further characterized by its 1H-NMR
spectrum (Fig. 6 and Table
1). The spectrum showed an intact 3,4-dichloroaniline ring system as well as the expected side-chain protons.
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Decomposition products of DCAKGA.
During purification by HPLC,
DCAX as well as DCAKGA partially decomposed into DCASA and smaller
amounts of DCASI. DCASA and DCASI were identified by HPLC retention
times on C8 and C18 columns and by
1H-NMR spectroscopy (Table 1). When DCAX was transferred
from a pH of 4 to 5 to a pH of 5.5, 6.0, or 6.5, complete conversion to
a distinctly more polar, unidentified product occurred. It seems likely
that the known reversible isomerization of
-ketoglutaric acid to
2-hydroxy-5-oxo-tetrahydrofuran-2-carboxylic acid (8) had
occurred.
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DISCUSSION |
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Optimal fermentation conditions. The previous failure to obtain mineralization of DCA with P. chrysosporium strain 34541 can now be explained by the inadequate fermentation conditions used. The use of smaller flasks and gassing with air rather than oxygen both reduced the oxygen partial pressure. The latter is well known to be crucial for mineralization of lignin (13, 17). In addition, room temperature was used instead of the optimal growth temperature of 37°C. Inactive fungal cultures are shown here to gain full mineralization activity upon an increase of oxygen pressure and a shift in temperature to 37°C or upon the addition of D-glucose to a C-limited culture. Mineralization activity is known to appear in the transition from exponential to stationary growth phase and to be optimal under N limitation and after the addition of an inducer such as veratryl alcohol (13, 17). These various ways of optimizing mineralization may be useful tools in studies of differential gene expression. The enzymes and transcripts that are involved in ring cleavage and mineralization reactions of lignin or of xenobiotics are still largely unknown.
Detection of a new intermediate.
Addition of
[U-14C]DCA to cultures of P. chrysosporium is shown here to lead within 2 days to a
yield of up to 90% of a novel, highly polar intermediate termed DCAX.
In agreement with the previous comparison of N-limited,
C-limited, and C- and N-rich growth media (1),
significant mineralization occurred only under N-limited growth
conditions. These conditions also led to a near-stoichiometric conversion of DCAX to DCASI (Fig. 2 and 3). Extraction of DCAX with
ethyl acetate required prior acidification. This observation and
the low Rf value upon TLC led to the proposal of
DCAX being the anilide of a dicarboxylic acid (28). The
chemical lability of DCAX was consistent with a
-keto-acyl
structure.
-Ketoadipic acid is a known intermediate of aromatic ring
cleavage in P. chrysosporium (cf. reference
25), and its terminal anilide could conceivably rearrange to yield DCASI. However, the above-mentioned
detailed structural studies have shown that DCAX is the
-anilide of
-ketoglutaric acid.
Structure of the new intermediate.
The comparison between DCAX
and synthetic DCAKGA by HPLC retention times, HPLC-MS, and GC-MS gave
unequivocal evidence for the identity of both compounds.
Analogous to the spontaneous formation of DCASA from DCA and
succinyl-S-coenzyme A (3), one would expect the new compound
to form from DCA and
-ketoglutaryl-
-S-coenzyme A. The latter
could be formed by a broad-specificity coenzyme A ligase. The derived
structure of DCAX contrasts with that of
-hydroxy-glutaryl-S-coenzyme A, which is activated at the vicinal rather than the distal carboxyl group (22). Hallinger et al. (11) also placed DCA at the vicinal carboxyl group of their
-hydroxyglutaryl conjugate, but no direct experimental evidence was
presented.
-ketoglutaryl-dehydrogenase-type reaction
leads to the formation of the activated coenzyme A ester of DCASA,
which can then spontaneously cyclize to yield DCASI. In model
reactions, chemical activation of DCASA to either
[N-(2,3,4-6-tetra-O-acetyl)-glucosyl]-DCASA or
the anhydride between DCASA and formic acid led to the spontaneous formation of DCASI at a >90% yield (data not shown). The need for
chemical activation is consistent with a previous study in which DCASA
by itself failed to cyclize to DCASI (3).
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-Keto acids are known to
be unstable. No attempts were made here to elucidate the pathways of
decomposition. The newly derived metabolic sequence of Fig. 7 seems
important to understand how P. chrysosporium uses its normal biochemistry to
mineralize exotic foreign chemicals. The free amino group of DCA
is easily attacked by lignin peroxidases (23, 23a) and other
oxidative enzymes (24, 27) that lead to highly toxic dimers
and to oligomers of DCA. Formation of DCAX and the succinimide prevents
these oxidative conversions. This protective effect has been suggested
to be a prerequisite for oxidative ring cleavage reactions and
mineralization of xenobiotics as well as lignins (26). Such
a role has also been proposed for xylosyl conjugation (15).
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ACKNOWLEDGMENTS |
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We gratefully acknowledge the cooperation of B. Meßner and the assistance of Fisons, Perkin-Elmer, and Finnigan MAT in HPLC-MS.
This work has been supported by BStMLU, Munich, Germany, and in part by Fonds der Chemischen Industrie, Frankfurt, Germany.
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FOOTNOTES |
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*
Corresponding author. Mailing address:
GSF
Forschungszentrum für Umwelt und Gesundheit GmbH, Institut
für Biochemische Pflanzenpathologie, Ingolstädter
Landstraße 1, D-85764 Oberschleißheim, Germany. Phone:
49-89-3187-2285. Fax: 49-89-3187-3383. E-mail:
sandermann{at}gsf.de.
Present address: GSF
Forschungszentrum für Umwelt und
Gesundheit GmbH, Institut für Hydrologie, D-85764
Oberschleißheim, Germany.
Present address: GBF
Bereich Mikrobiologie, D-38124
Braunschweig, Germany.
§
Present address: GSF
Forschungszentrum für Umwelt und
Gesundheit GmbH, Projektträgerschaft (PT-UKF),
81543 München, Germany.
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REFERENCES |
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| 1. | Arjmand, M., and H. Sandermann. 1985. Mineralization of chloroaniline/lignin conjugates and of free chloroanilines by the white rot fungus Phanerochaete chrysosporium. J. Agric. Food Chem. 33:1055-1060. |
| 2. | Arjmand, M., and H. Sandermann. 1986. Plant biochemistry of xenobiotics. Mineralization of chloroaniline/lignin metabolites from wheat by the white-rot fungus, Phanerochaete chrysosporium. Z. Naturforsch. 41c:206-214. |
| 3. | Arjmand, M., and H. Sandermann. 1987. N-(Chlorophenyl)-succinimides: a novel metabolite class isolated from Phanerochaete chrysosporium. Pestic. Biochem. Physiol. 27:173-181. |
| 4. | Barr, D. P., and S. D. Aust. 1994. Mechanisms white rot fungi use to degrade pollutants. Environ. Sci. Technol. 28:79A-87A. |
| 5. | Blau, K., and J. M. Halkett (ed.). 1993. Handbook of derivatives from chromatography. J. Wiley and Sons, Chichester, England. |
| 6. |
Bumpus, J. A.,
M. Tien,
D. Wright, and S. D. Aust.
1985.
Oxidation of persistent environmental pollutants by a white rot fungas.
Science
228:1434-1436 |
| 7. | Eaton, D. C. 1985. Mineralization of polychlorinated biphenyls by Phanerochaete chrysosporium: a ligninolytic fungus. Enzyme Microb. Technol. 7:194-196. |
| 8. | Falbe, J., and M. Regitz (ed.). 1995. Römpp Chemie Lexikon, 9th ed., p. 3176. Georg-Thieme-Verlag, Stuttgart, Germany. |
| 9. | Gattermann, L., and T. Wieland. 1982. Die Praxis des organischen Chemikers, p. 310. Walter de Gruyter, Berlin, Germany. |
| 10. | Haider, K. M., and J. P. Martin. 1988. Mineralization of 14C-labelled humic acids and of humic acid bound 14C-xenobiotic by Phanerochaete chrysosporium. Soil Biol. Biochem. 20:425-429. |
| 11. | Hallinger, S., W. Ziegler, P. R. Wallnöfer, and G. Engelhardt. 1988. Verhalten von 3,4-Dichloranilin in wachsenden Pilzkulturen. Chemosphere 17:543-550. |
| 12. | Higson, F. K. 1991. Degradation of xenobiotics by white rot fungi. Rev. Environ. Contamin. Toxicol. 122:111-151[Medline]. |
| 13. | Kirk, T. K., and R. L. Farrell. 1987. Enzymatic "combustion". The microbial degradation of lignin. Annu. Rev. Microbiol. 41:277-285. |
| 14. | Kirk, T. K., E. Schultz, W. J. Connors, L. F. Lorenz, and J. G. Zeikus. 1978. Influence of culture parameters on lignin metabolism by Phanerochaete chrysosporium. Arch. Microbiol. 177:277-285. |
| 15. |
Kondo, R.,
H. Yamagami, and K. Sakai.
1993.
Xylosylation of phenolic hydroxyl groups of the monomeric lignin model compounds 4-methylguaiacol and vanillyl alcohol by Coriolus versicolor.
Appl. Environ. Microbiol.
59:438-441 |
| 16. | Kremer, S., and O. Sterner. 1996. Metabolism of 3,4-dichloroaniline by the basidiomycete Filoboletus species TA 9054. J. Agric. Food Chem 44:1151-1159. |
| 17. | Leisola, M. S. A., and A. Fiechter. 1985. New trends in lignin biodegradation. Adv. Biotechnol. Process. 5:59-89. |
| 18. | Leisola, M. S. A., U. Thanei-Wyss, and A. Fiechter. 1985. Strategies for production of high ligninase activities by Phanerochaete chrysosporium. J. Biotechnol. 3:97-107. |
| 19. | May, R. G., P. Schröder, and H. Sandermann. 1997. An ex-situ process for treating PAH contaminated soil with Phanerochaete chrysosporium. Environ. Sci. Technol. 31:2626-2633. |
| 20. | May, R. G., I. Sparrer, E. Hoque, and H. Sandermann. 1997. Mineralization of native pesticidal plant cell-wall complexes by the white-rot fungus, Phanerochaete chrysosporium. J. Agric. Food Chem. 45:1911-1915. |
| 21. | Morgan, P., S. T. Lewis, and R. J. Watkinson. 1991. Comparison of abilities of white-rot fungi to mineralize selected xenobiotic compounds. Appl. Microbiol. Biotechnol. 34:693-696. |
| 22. | Müller, U., and W. Buckel. 1995. Activation of (R)-2-hydroxyglutaryl-CoA dehydratase from Acidaminococcus fermentans. Eur. J. Biochem. 230:698-704[Medline]. |
| 23. | Pieper, D.-H., R. Winkler, and H. Sandermann. 1992. Bildung eines toxischen Dimerisierungsproduktes aus 3,4-Dichloranilin durch Lignin-Peroxidase von Phanerochaete chrysosporium. Angew. Chem. 104:60-61. |
| 23a. | Pieper, D.-H., R. Winkler, and H. Sandermann. 1992. Formation of a toxic dimerization product of 3,4-dichloroaniline by lignin peroxidase from Phanerochaete chrysosporium. Angew. Chem. Int. Ed. Engl. 31:68-70. |
| 24. | Pothuluri, J., J. A. Hinson, and C. E. Cerniglia. 1991. Propanil: toxicological characteristics, metabolism, and biodegradation potential in soil. J. Environ. Qual. 20:330-347. |
| 25. |
Rieble, S.,
D. K. Joshi, and M. H. Gold.
1994.
Purification and characterization of a 1,2,4-trihydroxybenzene 1,2-dioxygenase from the basidiomycete Phanerochaete chrysosporium.
J. Bacteriol.
176:4838-4844 |
| 26. | Sandermann, H., D.-H. Pieper, and R. Winkler. 1993. Mineralization of lignin-bound and free xenobiotics by the white-rot fungus, Phanerochaete chrysosporium, p. 499-503. In J. F. Kennedy, G. O. Phillips, and P. A. Williams (ed.), Cellulosics: pulp, fibre and environmental aspects. Ellis Horwood, New York, N.Y. |
| 27. | Still, G.G., and R.A. Herett. 1976. Methylcarbamates, carbanilates and acylanilides, p. 609-664. In P. C. Kearney, and D. D. Kaufman (ed.), Herbicides: chemistry, degradation and mode of action. Marcel Dekker, Inc., New York, N.Y. |
| 28. | Winkler, R. 1991. Metabolisierung von Chloranilinen in Weizen (Triticum aestivum L.) und Soja (Glycine max [L.] Merril) und im Weißfäule-Pilz Phanerochaete chrysosporium Burds. Ph.D. thesis. Faculty of Biology, Ludwig-Maximilians University, Munich, Germany. |
| 29. | Winkler, R., and H. Sandermann. 1990. Mineralization of 3,4-dichloroaniline by the white-rot fungus, Phanerochaete chrysosporium Burds, abstr. 06C-03, p. 191. In Book of Abstracts. Seventh International Congress of Pesticide Chemistry. IUPAC, Hamburg, Germany. |
| 30. | Winkler, R., and H. Sandermann. 1992. N-Glucosyl conjugates of chlorinated anilines: spontaneous formation and cleavage. J. Agric. Food Chem. 40:2008-2012. |
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