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Applied and Environmental Microbiology, June 1999, p. 2388-2395, Vol. 65, No. 6
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
Multiple Epoxide Hydrolases in Alternaria alternata f.
sp. lycopersici and Their Relationship to Medium Composition
and Host-Specific Toxin Production
Christophe
Morisseau,1
Barney L.
Ward,2
David G.
Gilchrist,2 and
Bruce
D.
Hammock1,*
Department of
Entomology1 and Department of Plant
Pathology,2 University of California, Davis,
California 95616
Received 7 December 1998/Accepted 23 March 1999
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ABSTRACT |
The production of Alternaria alternata f. sp.
lycopersici host-specific toxins (AAL toxins) and epoxide
hydrolase (EH) activity were studied during the growth of this
plant-pathogenic fungus in stationary liquid cultures. Media containing
pectin as the primary carbon source displayed peaks of EH activity at
day 4 and at day 12. When pectin was replaced by glucose, there was a
single peak of EH activity at day 6. Partial characterization of the EH
activities suggests the presence of three biochemically distinguishable
EH activities. Two of them have a molecular mass of 25 kDa and a pI of
4.9, while the other has a molecular mass of 20 kDa and a pI of 4.7. Each of the EH activities can be distinguished by substrate preference
and sensitivity to inhibitors. The EH activities present at day 6 (glucose) or day 12 (pectin) are concomitant with AAL toxin production.
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INTRODUCTION |
Alternaria alternata f.
sp. lycopersici is a fungal pathogen that causes the
Alternaria stem canker disease of tomatoes (17). During disease development and in liquid culture, the pathogen secretes
host-specific toxins (AAL toxins) which, in purified form, elicit cell
death patterns characteristic of the stem canker (36). The
ability of the pathogen to infect the leaves, stems, and green fruit of
tomatoes is limited to genotypes that are homozygous for the recessive
allele (asc/asc) of the Asc gene (11). The Asc
gene also regulates toxin sensitivity; thus, the toxins function as
chemical determinants of the stem canker disease (11).
Moreover, AAL toxins, which are members of the same class of
sphinganine analog mycotoxins as fumonisins, inhibit ceramide synthase
in rat hepatocytes (28) and induce apoptosis in monkey
kidney cells (41). Unlike the case with fumonisins
(24), the effects of chronic exposure to AAL toxins on
animal health are still unresolved. The first of the AAL toxins (toxin
A [TA]) was characterized in 1981 (7), and more recently
(8), new isomeric toxins were purified and characterized
(Fig. 1). The presence of one pair of
vicinal diols, free or esterified, in the structure of each of the AAL
toxins (Fig. 1) suggests the possible involvement of an epoxide
hydrolase (EH) in their synthesis. This hypothetical mechanism is
supported by the fact that one of the oxygen atoms of the diol came
from direct incorporation of atmospheric oxygen and the other came from
water (10).
EHs (EC 3.3.2.3) catalyze the hydrolysis of epoxides or arene oxides to
their corresponding diols by the addition of water (34).
Several members of this ubiquitous enzyme subfamily have been described
in organisms as diverse as mammals (21), plants (37), insects (13), and microorganisms
(16). Because of their involvement in the metabolism of
various xenobiotics (27, 42), many of which are suspected to
be carcinogenic, and natural oxylipins (29, 45), mammalian
enzymes have been extensively studied (see reference
21 for a review). Based on sequence similarity, most
EHs are members of the
/
hydrolase fold family (1). This family of enzymes hydrolyzes their substrates in a two-step mechanism involving the formation and hydrolysis of a covalent alkyl-enzyme intermediate formed with a nucleophilic aspartic acid
(4, 26, 40). In comparison with mammalian EHs, little is
known about EHs from other species, especially from filamentous fungi.
An EH induced by a cutin extract of plants has been partially characterized from Fusarium solani pisi (25).
This enzyme apparently is related to the ability of the mycelium to
infect some plants (44). More recently, fungal EHs have
attracted attention for their potential in asymmetric organic synthesis
(1). However, little is known of the physiological
significance of these enzymes. In the case of dematiaceous fungi, EH
activities are constitutively expressed coincident with secondary
metabolite pigment production in stationary phase or idiophase
(19).
In a preliminary study (35), AAL toxin production by
A. alternata f. sp. lycopersici was shown to
occur concomitant with the expression of an EH activity. Moreover, both
AAL toxin production and EH activity were enhanced by clofibrate, which
is well known to induce EH in mammals (19). However, some
questions have not been answered. Is there a direct link between the
enzyme and production of AAL toxins, i.e., is the EH involved in the
toxin metabolism? Is the increase in EH activity that is measured
following the administration of clofibrate due to increased production
of the same enzyme or production of a new form? To answer these
questions, we first investigated the effects of the pH, the carbon
source, the time of fermentation, and the presence of clofibrate on the production of EH activity and of toxin. Second, we characterized the EH
activities obtained under different culture conditions.
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MATERIALS AND METHODS |
Microorganisms and chemicals.
The single-conidium isolate
(12) of A. alternata f. sp.
lycopersici (AS27-3) used herein was originally isolated
from a field-infected tomato plant (17) and maintained in
the laboratory on cornmeal agar.
[14C]cis-9-10-epoxystearic acid (ESA),
[3H]trans-stilbene oxide (t-SO),
[3H]cis-stilbene oxide (c-SO),
[3H]trans-1,3-diphenylpropene oxide (t-DPPO),
and [3H]cis-1,3-diphenylpropene oxide (c-DPPO)
were previously synthesized in this laboratory (1, 18).
[3H]labeled-juvenile hormone III (JH-III) was purchased
from Amersham Life Science (Arlington Heights, Ill.). Unlabeled t-DPPO
was synthesized as described previously (1). Chalcone oxide
inhibitors were synthesized in the laboratory (32). Other
chemicals were purchased from Aldrich Chemicals (Milwaukee,
Wis.) and used without any further purification. The liquid
scintillation cocktail CytoScint was purchased from Fisher Scientific
(Fairlawn, N.J.). The bicinchoninic acid (BCA) reagent for protein
concentration determination was obtained from Pierce, Inc. (Rockford,
Ill.).
Media and culture conditions.
A. alternata f. sp.
lycopersici and A. alternata (black mold) were
grown on liquid media containing (in grams per liter): glycine, 0.75;
NaCl, 0.1; K2HPO4 · 3H2O,
1.31; MgSO4 · 7H2O, 0.5; CaCl2 · 2H2O, 0.13; yeast extract, 0.5;
malic acid 0.69; and pectin (P9135; Sigma), 22.3, or glucose, 20.7. Both media were adjusted to a final pH of 3.7 and inoculated at a final
concentration of 3.3 × 103 conidia/ml of medium, and
30-ml portions were dispensed into plastic petri dishes (three
replicates) and grown at room temperature (20 to 25°C) under
cool-white fluorescent lighting (12 h/day). For the pH study, the above
glucose medium was adjusted to the desired pH between 2.1 and 6.0 with
10 N NaOH or 5 N HCl, brought to volume, and inoculated, and 30-ml
portions were dispensed into plastic petri dishes (four replicates).
Cell culture filtrate and mycelium material were prepared by vacuum
filtration (Whatman no. 1) at 2 to 15 days after inoculation, according
to each experiment. The dry mass of mycelium was measured after drying
at 80°C under a vacuum to a constant weight (usually for 24 h).
Subcellular extract preparation.
The harvested mycelium was
resuspended in 100 mM sodium phosphate buffer (pH 7.4) containing 1 mM
phenylmethylsulfonyl fluoride (PMSF), EDTA, and dithiothreitol (DTT)
(buffer A) and was disrupted with a Polytron homogenizer (9,000 rpm for
2 min). The homogenate was centrifuged at 10,000 × g
for 20 min at 4°C. The protein concentration of the supernatant
(crude extract) was estimated by a BCA assay using bovine serum albumin
(BSA) as a standard.
Enzyme assays.
The EH activities of the crude extracts were
measured routinely by using t-DPPO (compound I) as described previously
(5). Briefly, 100 µl of cell extracts diluted in 100 mM
sodium phosphate buffer (pH 7.4) containing 0.1 mg of BSA/ml was
incubated at 30°C for 2 min. t-DPPO (1 µl of 5 mM solution in
dimethyl formamide [DMF]) was added (final concentration, 50 µM)
with a Hamilton repeating dispenser syringe; a standard deviation of
less than 5% in the amount added was observed. The mixture was
incubated at 30°C for 10 min. The reaction was quenched by the
addition of 60 µl of methanol. Iso-octane (200 µl) permitted the
extraction of the remaining epoxide (99%), while 91% of the diol
formed stayed in the aqueous phase (5). The quantity of diol
formed was determined by using a liquid scintillation counter (model
1409; Wallac, Gaithersburg, Md.) to quantify the radioactivity
contained in the aqueous phase. Assays were performed in triplicate.
One unit of EH corresponds to the amount of enzyme that catalyzed the
formation of 1 µmol of diol per min under the above conditions. The
linearity of the assay was verified versus the enzyme concentration (0 to 2 mU/ml) and the incubation time (0 to 30 min). The EH activities of
crude extracts were also measured by using c-DPPO (compound II), t-SO (compound III), c-SO (compound IV), JH-III (compound V), and ESA (compound VI) as described previously (1, 33, 42).
Inhibition studies.
To measure the effect of group-selective
reagents, 100 µl of enzyme extracts in phosphate buffer (pH 7.4; 0.5 mU/ml) was incubated at 30°C for 15 min with 1 µl of the inhibitor
solution in DMF or water (final concentration of inhibitor, 1 mM). The
remaining activity was then determined by using t-DPPO (compound I) as
described above. Results are generated from at least three separate
runs, each in triplicate. For the determination of the concentration of
inhibitor that reduces enzyme activity by 50% (IC50), 100 µl of enzyme extracts in phosphate buffer (pH 7.4; 0.5 mU/ml) was incubated at 30°C for 15 min with 1 µl of the inhibitor solution in
DMF (final concentration of inhibitor, 0.05 to 250 µM). The remaining
activity was then determined by using t-DPPO (compound I) as described
above. IC50s were determined by regression of at least five
datum points, with a minimum of two points in the linear region of the
curve on either side of the IC50. The curve was generated
from at least three separate runs, each in triplicate, to obtain the
standard deviation in Table 4. In at least one run, compounds of
similar potency were included to ensure the rank order of inhibitors.
Determination of the molecular weight and pI.
The molecular
weight associated with EH activity in the crude extract was estimated
from the elution profile on a gel filtration column. The enzyme extract
(0.5 ml) was applied to a Sephacryl-S100 (Pharmacia, Uppsala, Sweden)
column (1.5 by 100 cm), equilibrated with buffer A (flow rate, 10 ml/h;
fraction volume, 1 ml). The molecular weight was calculated by
comparing the elution constant (Kav) of the EH activity with that of
the following standard proteins: alcohol dehydrogenase (150 kDa), BSA
(66 kDa), ovalbumin (43 kDa), chymotrypsinogen A (25 kDa), and RNase A
(13.7 kDa). The void and exclusion volumes were determined by using
dextran blue and vitamin B12. Electrofocusing was performed
with pH 4.0 to 6.5 gradient gels by using the Pharmacia LKB Multiphor
system and standard Pharmacia procedures. After migration the gel was
cut in 5-mm slices from the anode to the cathode. The gel pieces were incubated in 0.5 ml of buffer A during 1 h at 4°C. The EH
activity in the buffer was then measured.
Measurement of toxin production.
The quantity of AAL toxins
present in the cell culture filtrate was determined by using an
indirect immunoassay method with sera from mouse 57 and coating
antigen-C-BSA (38). TA purified in our laboratory and shown
by 1H NMR to be at least 95% pure (9) was used
as an analytical standard.
 |
RESULTS |
Effect of pH.
Cells of A. alternata f. sp.
lycopersici were grown on glucose media that had a range of
pH values between 2.1 and 6.0. Based on results obtained in a
preliminary study to determine the kinetics of toxin production (data
not shown), cells were harvested after 6 days of culture. Mycelial
growth, EH activities, and AAL toxin production are dependent on the pH
of the medium (Table 1). Fungal growth is
not observed at day 6 in the lowest-pH medium; however, growth is
apparent in pH 2.6 medium and increases to a maximum (average, 4.3 g · liter
1) in media at pH 3.6 through pH 6.0. A
fivefold increase in both EH activity and AAL toxin production is
observed for cultures grown at pH 3.1 compared to pH 2.6. EH activity
increases another 2-fold, but AAL toxin levels decrease 20-fold, when
the pH of the medium is increased from 3.1 to 3.6. For higher pH
values, the EH activity and the AAL toxin production level off at
averages of 1.8 mU · mg
1 and 13 mg · liter
1, respectively. Our standard pectin medium
(35) has a final pH of 3.7, and no attempt was made to study
the effect of pH on pectin media for the following reasons: (i)
sterilization by autoclaving alters the initial pH of pectin media,
(ii) pectin strongly buffers the standard medium at pH 3.7, and (iii)
filter sterilization after autoclaving is impractical due to the
viscosity of pectin in the media. For the study of factors other than
pH, cultures were conducted at pH 3.7 for both glucose and pectin
media.
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TABLE 1.
Effect of the initial pH on the growth, EH activity, and
AAL toxin production of A. alternata f.
sp. lycopersicia
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Effect of the carbon source and of the presence of clofibrate.
In the absence of clofibrate, twofold-greater growth of the mycelium is
observed on pectin (11 g · liter
1 [Fig.
2A]) compared to glucose medium (7 g · liter
1 [Fig. 2B]) after 6 days of culture,
while nine- and four-fold-higher EH activity and AAL toxin production,
respectively, are observed on glucose medium. Interestingly, the
addition of clofibrate to the culture has different effects on fungal
growth in media with different carbon sources. On pectin media, at a
concentration of clofibrate higher than 0.25 mM, a significant decrease
in biomass production is observed, while significant increases in both
EH activity and toxin production are observed. For 1 mM and higher clofibrate concentrations, production of the AAL toxins levels off at
around 90 mg · liter
1, while the EH activity rises
more slowly to reach a value of 5.5 mU · mg
1 at 2 mM. These results are consistent with earlier observations (35) and are close to those obtained on glucose media
without clofibrate (Fig. 2B). When A. alternata f. sp.
lycopersici is grown on the glucose media, the addition of
clofibrate has no significant (
= 0.05) effect on mycelium
growth, EH activity, or AAL toxin production.

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FIG. 2.
Effect of clofibrate concentration on the growth, EH
activity, and toxin production of A. alternata f. sp.
lycopersici grown in petri dishes containing 30 ml of
medium. Clofibrate was added in ethanol (0.5% of the total volume of
culture) 2 days after culture inoculation; the mycelium and cell
culture filtrate were obtained on the 6th day of culture. (A) Pectin as
the carbon source; (B) glucose as the carbon source.
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Kinetics of growth, EH activity, and toxin production.
Culture
of A. alternata f. sp. lycopersici in pectin
medium was monitored over a 2-week period (Fig.
3). In the absence of clofibrate, an
exponential phase is observed between days 2 and 6, and cells reach a
biomass value of 11 g · liter
1. The addition of 1 mM clofibrate on the 2nd day of incubation (Fig. 3A) stops the growth
of the mycelium at around 3.5 g of dry biomass · liter
1. In the absence or presence of clofibrate, two
peaks of EH activities are observed (Fig. 3B): the first peak at around
3 days of culture (beginning of the exponential phase) and the second
peak at around 12 days (during the stationary phase). The clofibrate
decreases the first peak but increases the second peak twofold. A
similar pattern is observed for the total EH activity, expressed as
enzymatic units per gram of mycelium (data not shown). For both culture conditions, AAL toxin production starts on day 4 and continues over the
period sampled (Fig. 3C). However, in the presence of clofibrate, two
to three times more AAL toxins are synthesized.

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FIG. 3.
Kinetics of growth, EH activities, and AAL toxin
production by A. alternata f. sp. lycopersici
grown in petri dishes containing 30 ml of medium with pectin as the
carbon source and with ( ) or without ( ) 1 mM clofibrate.
Clofibrate was added on the 2nd day of culture (arrow). (A) Fungal
biomass; (B) EH specific activity with t-DPPO as the substrate; (C)
concentration of AAL toxin expressed as TA equivalents.
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On a glucose medium (Fig.
4), an
exponential phase of growth is observed between days 2 and 6, and
clofibrate, at 1 mM, has
little effect on the growth of
A. alternata f. sp.
lycopersici (Fig.
4A). Compared to
the pectin medium, most EH activity is
associated with the
exponential-growth phase of the glucose culture
and not with the
stationary phase (Fig.
4B). AAL toxin (Fig.
4C)
appears in the medium
on the 2nd day of culture (the same time
as the EH), and its
concentration increases almost linearly over
the 15 days of the study
(during the exponential and stationary
phases). Clofibrate slightly
decreases EH activity and AAL toxin
production (Fig.
4B and C). A
similar pattern is observed for
the total EH activity, expressed as
enzymatic units per gram of
mycelium (data not shown), indicating a
decrease in EH production
induced by the peroxisomal proliferator. AAL
toxins appear in
the medium at the same time that EH activity is first
detected
(on day 2) and continue to rise over the test period. As found
in previous work using pectin media (
35), the
non-toxin-producing
isolate,
A. alternata (black mold), has
only very low EH activities
(10-fold less than
A. alternata
f. sp.
lycopersici) (Fig.
4B),
and the EH activity remains
at this level over the sampling period.

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FIG. 4.
Kinetics of growth, EH activities, and AAL toxin
production by A. alternata f. sp. lycopersici
grown in petri dishes containing 30 ml of medium with glucose as the
carbon source and with ( ) or without ( ) 1 mM clofibrate.
Clofibrate was added on the 2nd day of culture (arrow). A. alternata (black mold) ( ) was grown under the same conditions
without any clofibrate added. (A) Fungal biomass; (B) EH specific
activity with t-DPPO as a substrate; (C) concentration of AAL toxin
expressed as TA equivalents.
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Molecular mass and pI determination.
Crude cell extracts were
prepared from A. alternata f. sp. lycopersici
grown on pectin medium at days 6 and 12 of culture in the absence or
presence of 1 mM clofibrate and on glucose media at pH 4.0 and 6.0 at
day 6.
The native molecular weights of the EH activities were determined by
gel filtration (Fig.
5). Only one peak of
activity was
observed for each extract. The elution profiles indicate
an approximate
molecular weight of the major form of EH activity
present in the
cell extracts (Table
2).
Based on these molecular weights, the
cell extracts could be separated
in two groups of EH activity:
the first (group A) at 20 kDa (pectin
control medium on days 6
and 12 and pectin medium with clofibrate on
day 6) and the second
(group B) at 25 kDa (glucose media at pH 4 and 6 and pectin medium
with clofibrate on day 12). However, the elution
profiles (Fig.
5) lack the resolution to exclude the presence of a
minor component,
and their shapes suggest the presence of at least two
different
molecular weight forms in all the extracts.

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FIG. 5.
Elution profiles from a Sephacryl-S100 column of EH
activities in cell extracts of A. alternata f. sp.
lycopersici grown in liquid culture. Pec., pectin medium;
Con., control; Clo., with clofibrate; Glu., glucose medium.
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TABLE 2.
Estimation of the major native molecular weights and pIs
of major EH activities from A. alternata f. sp.
lycopersici a
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The pIs of the EH activities were determined by isoelectric focusing
(Fig.
6). Only one peak of activity was
observed for
each extract. The elution profiles indicate an approximate
pI
of the major form of EH activity present in the cell extracts
(Table
2). Based on these values, the cell extracts could be
separated in the
same two groups of EH activity found with the
molecular weights: group
A at pI 4.7 and group B at pI 4.9. Moreover,
the 20-kDa enzyme from gel
permeation (group A) gave predominantly
pI of 4.7, while the 25-kDa
enzyme (group B) gave predominantly
a pI of 4.9. The shapes of the
activity profiles (Fig.
6) suggest
the presence of the two different EH
activity forms in all the
extracts. The ratio of the 4.7 pI to the 4.9 pI (Table
2) indicates
that the minor EH activity represents 5 to 20%
of the total activity.

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FIG. 6.
Profiles of EH activity of A. alternata f.
sp. lycopersici cell extracts from a 4.0 to 6.5 pH gradient
electrofocusing gel (Pharmacia LKB Multiphor System). Pec., pectin
medium; Con., control; Clo., with clofibrate; Glu., glucose medium.
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Substrate selectivity.
The EH activities of the six extracts
were measured for six substrates available in the laboratory: four
benzyl- or phenyl-substituted epoxides (compounds I to IV) and two
natural lipid epoxides (compounds V and VI). The relative rates of
hydration of the different substrates are shown in Table
3. The two groups (A and B) of EH
activities are significantly different (
= 0.05) from each other for
the six substrates. However, the six epoxides tested allow the
segregation of group A into two subgroups of similar activity: A1
(pectin control medium on day 6 and pectin medium with clofibrate on
day 6) and A2 pectin control medium on day 12). Groups A1 and A2 have relatively more activity for the JH-III and ESA substrates than group
B. Group B is more active on t-DPPO and c-DPPO. For all three groups,
only low activity is found on t-SO and c-SO. The high specific activity
obtained for the three groups with the terpenoid epoxide is surprising.
For most of the EHs studied, the turnover of such trisubstituted
epoxides is much lower than that of less-hindered compounds (31,
42).
Group-selective reagents and inhibitor specificity.
In a
second comparison, the effects of different inhibitors on the
activities of extracts were tested. At first, the effects of reagents
selective for functional groups on the protein were tested. Metal
chelators (EDTA and o-phenanthroline) as well as an
inhibitor of serine esterases and proteases (PMSF) showed no inhibition
of the six enzymatic extracts. Reducing reagents (DTT and cysteine) did
not have significant effects on the activities, while in contrast,
oxidants (m-chloroperbenzoic acid and
H2O2) were potent inhibitors. Similar results
were obtained with other EHs (14, 30, 42). Strong
sulfhydryl-modifying reagents (HgCl2 and
4-hydroxymercuribenzoate sodium) totally inhibited all the extracts,
while the three groups of enzyme give different results with weaker
sulfhyhydryl reagents (dithiodinitrobenzoic acid [DTNB] and
iodoacetamide). In the conditions tested, group A1 is slightly inhibited by DTNB (33 ± 3%) and iodoacetamide (18 ± 5%),
while group A2 is not inhibited by DTNB and is totally inhibited by iodoacetamide. Group B is strongly inhibited by DTNB (75 ± 5%) and slightly inhibited by iodoacetamide (33 ± 5%). These results suggest the presence of an exposed sulfhydryl group only on the B
enzyme, while the A2 enzyme should have an accessible disulfide bond.
An exposed sulfhydryl group was demonstrated on the mammalian soluble
EH (sEH) but not on the microsomal EH (mEH) (42). Under the
conditions tested, the histidine reagent (
-bromonitroacetophenone [
-Br-NPA]) gave significantly different levels of inhibition with
the three groups of enzyme: 63 ± 3, 41 ± 4, and 81 ± 5% inhibitions for A1, A2, and B enzymes, respectively. The three
fungal enzymes are only partially inhibited by
-Br-NPA, while under
similar conditions mammalian mEH and sEH are totally inhibited.
Moreover, for these mammalian enzymes,
-Br-NPA was shown to bind
covalently a histidine residue of the active site (14, 15).
The lower inhibition of the three fungal enzymes by
-Br-NPA may
simply reflect a difficulty for the compound to reach the catalytic
histidine, its reaction with other nucleophiles in the extract, or the
turnover of the alkylated enzyme.
In a separate study, the IC
50s of known EH inhibitors
(
21) were measured (Table
4).
Based on the distribution of the results
obtained, the six extracts
could be divided into the same three
groups of activities that were
found above with the substrate
selectivity study. Compounds 1, 2, and 9 are good inhibitors of
groups A1 and B but not of group A2. Compound 4 is a good inhibitor
of the B enzyme but not of the A1 and A2 enzymes.
Only group A2
is well inhibited by compound 6, which is not a very good
inhibitor
of the two other groups. Compounds 5, 7, and 8 are not
inhibitors
of the three fungal enzymes. Interestingly, compound 5 is
the
best inhibitor known for the mammalian sEH (
32), and
compound
7 is the best inhibitor known for the mEH (
21).
Moreover, like
the mammalian sEHs (
21), all the extracts are
more sensitive
to the
(2
S,3
S)-
para-nitrophenyl-glycidol
(compound 9) than to
the (2
R,3
R) enantiomer
(compound 8).
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TABLE 4.
Effect of competitive inhibitors on the EH activity of
extracts of A. alternata f. sp. lycopersici with
t-DPPO as a substrate a
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DISCUSSION |
This report describes the production and characterization of EH
activities from A. alternata f. sp. lycopersici
in relation to the production of AAL toxins. The results obtained
clearly show that the pH (Table 1) and the medium composition (Fig. 2) markedly influence AAL toxin production and EH activities by A. alternata f. sp. lycopersici. They are enhanced at
acidic pHs and by the use of glucose. The fungus displays very
different characteristics when the major carbon source of the medium is changed from pectin to glucose (Fig. 3 and 4). The use of glucose as a
carbon source resulted in a 10-fold increase in EH production in
comparison to that with pectin, a "natural" substrate. This was
surprising given that EH activities for F. solani pisi
(25) and Aspergillus niger (31) were
shown to be repressed in the presence of glucose. On the glucose
medium, the EH activity seems related to increases in fungal biomass. A
similar effect was found for A. niger (31).
However, it has been reported recently (20) that in the case
of Beauveria densa, a dematiaceous fungus, EH production is
coincident with a secondary pigment produced in stationary phase or
idiophase. We have not observed such a phenomenon, but the EH activity
might be, in vivo, related to the metabolism of some secondary fungal
chemical. On the pectin medium, two peaks of EH activities are produced
at different periods during mycelium growth. This result was quite
surprising given that only one peak of EH activity was demonstrated for
several other fungi (20, 25, 31). With pectin as a
substrate, the AAL toxins appear in the medium when the first peak of
EH activity disappears. This result suggests that this peak of EH
activity may not be directly related to AAL toxin production. Moreover,
AAL toxin production occurred in parallel with the appearance of the
second peak of EH activity (Fig. 3). With glucose as the carbon source,
the fact that EH activity and the production of AAL toxins appear at
the same time (2nd day [Fig. 4]) is consistent with the hypothesis that there is an epoxide hydration step in the biosynthetic pathway of
AAL toxins. However, the fact that EH activity and AAL toxin productions are not parallel throughout the growth period could be
explained in several ways which are consistent with this hypothesis. First, it is possible that the step catalyzed by EH is not rate limiting, and a perfect correlation of activity and AAL toxin production is not critical. A second possibility and caution is that
this study uses surrogate substrates and not the suspected precursors
to the AAL toxins. Thus, the assay could detect several EH activities,
while only one of the apparent minority activities could be more
closely associated with the toxin production. Moreover, the proposed
hypothesis is supported by the observation that the non-toxin producer,
A. alternata (black mold), has only very low EH activities
(10-fold less than the strain producing toxin) (Fig. 4B), and these EH
activities remain at this level over the sampling period.
All of these results obtained under different culture conditions
suggest the presence of more than one EH. To test the hypothesis of the
presence of more than one EH, EH activities obtained in different
culture conditions were characterized for molecular and enzymatic
properties. Results obtained for the molecular properties (Table 2)
suggest the presence of at least two different EH activities. One
(group A) displays a molecular mass of 20 kDa and a pI of 4.7, while
the other (group B) weighs approximately 25 kDa and has a pI of 4.9. The mass values found are smaller than the masses for most of the EHs
previously described: monomeric masses between 30 and 70 kDa are
generally found (31), but a 17-kDa bacterial EH has been
described recently (39). For all the EH activities described, pI values between 4.5 and 6.0 have been found
(31). Based on substrate and inhibitor spectra (Tables 3 and
4), group A could be subdivided in two distinguishable groups of
enzymatic activities (A1 and A2). However, one of course cannot
absolutely distinguish classes of enzymes based on substrate
selectivity and differential inhibition. The observed differences could
be due to the fact that in crude extracts, other proteins present can
affect substrate activities and inhibitor sensitivity. Based on
subcellular location and substrate selectivity, several EH activities
have been described in mammals (21), insects
(23), and plants (3). To our knowledge, it is the
first time that more than one EH activity has been reported in a microorganism.
The A1 enzyme activity, the first peak of activity produced on the
pectin medium, is probably not directly related to toxin production
because toxin production occurred only as this peak was decreasing. On
this medium, the second peak of activity produced is different in the
absence (group A2) and presence (group B) of clofibrate. The fact that
in the presence of clofibrate, twice as much of the AAL toxins is
produced suggests that the group B enzyme is related to AAL toxin
biosynthesis. This trend is consistent with the high level of toxin
production observed on the glucose medium, where the group B enzyme is
produced at much higher levels. Moreover, pI determinations (Fig. 6 and
Table 2) show that on pectin media with or without clofibrate, at least
20% of the EH activity characterized at day 6 is from the group B
enzyme. This result indicates that, as observed on the glucose medium,
on pectin media the group B enzyme is produced at the same time the
toxin is produced, strongly suggesting that the group B enzyme is
associated with the production of AAL toxins. Recently, EH activities
in yeast and bacteria have been described in relation to the presence of carotenoid pigments as secondary metabolites (6) or
related to the metabolism of limonene (39). In A. alternata f. sp. lycopersici, all the EH fractions show
very high catalytic activity on JH-III, especially the A2 enzyme. Such
a result is consistent with the possible involvement of the fungal EH
activities in the metabolism of terpenes. In mammals, the sEH
hydrolyzed juvenile hormone and other terpenoic epoxides
(22). The competitive inhibitors tested herein (Table 4) are
substrates of the mammalian sEH with low turnover (21). If a
similar mode of action occurs with the fungal EHs, such compounds would
be of limited utility in evaluating these enzymes in vivo. However, the
determination of the inhibitory potency of different chalcone oxides
will allow us to develop new affinity matrices for the purification of
the fungal enzymes, as was done for the mammalian EHs (43),
and to develop new, potent inhibitors. These new tools will allow us to
better understand the role of these enzymes in the metabolism of the
AAL toxins and possibly, in the future, to block AAL toxin production
in infected plants.
 |
ACKNOWLEDGMENTS |
This work was supported in part by NIEHS grant R01-ES02710, NIEHS
Superfund Basic Research Program ES04699, NIEHS Center for Environmental Health Sciences grant 1P30-ES05707, and UC Davis EPA
Center for Ecological Health Research grant CR819658.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Departments of
Entomology and Environmental Toxicology, University of California, One Shields Ave., Davis, CA 95616. Phone: (530) 752-7519. Fax: (530) 752-1537. E-mail: bdhammock{at}ucdavis.edu.
 |
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