Nutrition influences growth and virulence of the insect-pathogenic fungus Metarhizium anisopliae
Investigations on the destruxin production of the entomopathogenic fungus Metarhizium anisopliae
-
Upload
independent -
Category
Documents
-
view
2 -
download
0
Transcript of Investigations on the destruxin production of the entomopathogenic fungus Metarhizium anisopliae
Journal ofINVERTEBRATE
Journal of Invertebrate Pathology 85 (2004) 168–174
PATHOLOGY
www.elsevier.com/locate/yjipa
Investigations on the destruxin productionof the entomopathogenic fungus Metarhizium anisopliae
Chengshu Wang,* Anke Skrobek, and Tariq M. Butt
School of Biological Sciences, University of Wales Swansea, Singleton Park, Swansea SA2 8PP, UK
Received 23 December 2003; accepted 24 February 2004
Abstract
The dynamics of cyclic peptide destruxins (dtxs) produced byMetarhizium anisopliae strains V245 and V275 were monitored both
on solid and in liquid media. The results showed that both strains did not produce dtxs in large-scale fermenter cultures or solid
Czapek Dox (CD) agar. Production of the major dtxs A and B could be determined in both strains when grown on rice for up to 10–
30 days. The main dtxs A, B, E, and E diol were detected in CD liquid culture filtrate from both strains after three days post-
inoculation on. Parallel decrease of dtx E and increase of E diol in the culture medium were found, indicating that the latter is the
hydrolytic product from the former. Production of dtxs A and B was significantly positively correlated. A negative correlation was
observed between the production of the metabolites and pH value of the medium. The influence of different nutrient sources on dtx
production was evaluated by using media with different carbon and nitrogen ratios as well as with different insect homogenates. The
findings showed that the amount of dtxs A, B, and E increased with the increasing content of peptone in the medium. When insect
homogenate was used as single nutrient source or added to CD medium, no toxins were detected in the culture filtrate. The potential
risk posed by the toxic metabolites during mass production is discussed.
� 2004 Elsevier Inc. All rights reserved.
Keywords: Metarhizium anisopliae; Destruxin; Carbon/nitrogen ratio; Toxin production
1. Introduction
The entomopathogenic fungus Metarhizium anisop-
liae is one of the most studied and applied species
amongst fungal biocontrol agents, several commercial
products have been developed and registered for the
control of different insect pests (Butt et al., 2001). The
insecticidal cyclic depsipeptides, destruxins (dtxs), pro-
duced by M. anisopliae have been suggested to be an
important virulence factors to accelerate the demise of
infected insects (Brousseau et al., 1996; Dumas et al.,1994; Kershaw et al., 1999). Since the first report of the
discovery of dtxs A and B from M. anisopliae by Ko-
daira (1961), a large number of analogues in this family
have been identified of which dtxs A, B, and E are
predominant (>70%) in submerged culture filtrates
(Loutelier et al., 1996; Pedras et al., 2002; Strasser et al.,
* Corresponding author. Fax: +44-1792-295447.
E-mail address: [email protected] (C. Wang).
0022-2011/$ - see front matter � 2004 Elsevier Inc. All rights reserved.
doi:10.1016/j.jip.2004.02.008
2000). Destruxins A and E were proven to be more in-
secticidal than others (Dumas et al., 1994).
The mechanism of dtx biosynthesis in M. anisopliae
has not been well documented. The multifunctional non-
ribosomal peptide synthetases (PES) have been sup-
posed to function (Bailey et al., 1996; Jegorov et al.,
1993; Marahiel, 1992; Zuber, 1991), however, there is no
confirmative evidence so far. Both in vivo and in vitro
studies showed that the diffusion of dtxs, albeit in dif-
ferent ratios, is a very rapid process from endogenous
mycelia (Amiri-Besheli et al., 2000; Butt et al., 1994;Loutelier et al., 1996). The production of dtxs differed
not only between different strains of M. anisopliae
(Amiri-Besheli et al., 2000; Hsiao and Ko, 2001; Ker-
shaw et al., 1999), but was also highly influenced by the
component type and ratio, usually carbon and nitrogen,
in the culture media (Liu et al., 2000).
In this study, toxin production dynamics of M. ani-
sopliae strains V245 and V275 were monitored both onsolid and in liquid media to meet the requirements
for developing these strains as potential commercial
C. Wang et al. / Journal of Invertebrate Pathology 85 (2004) 168–174 169
mycoinsecticides. The influence of the culture mediumon dtx secretion was evaluated by using liquid media
with different carbon and nitrogen ratios as well as with
different insect homogenates. The relationships between
the productions of main dtxs, pH, and biomass were
analysed and discussed. The results in this study addi-
tionally provide useful information to assess the poten-
tial risks of fungal toxic metabolites during the mass
production of M. anisopliae.
2. Materials and methods
2.1. Fungal culture and maintenance
The strains V245 and V275 of M. anisopliae were
originally isolated from hay field soil and Carpocapsa
pomonella in Finland and Austria, respectively. The
propagules of strains were preserved in 30% glycerol
under )80 �C for long-term storage and for experiments,
the cultures were grown on potato dextrose agar (PDA,
Difco) at 25 �C in the dark. Plates were kept at 4 �Cwhen fully covered with spores, usually after 14 days.
2.2. Solid cultivation
Petri dishes (£ 9 cm) were charged with 20ml auto-
claved Czapek Dox (CD) medium (K2HPO4, 1 g/L;
MgSO4�H2O, 0.5 g/L; KCl, 0.5 g/L; and FeSO4, 0.01 g/
L) containing 5% mycological peptone and 2% agar and
lined with Whatman No. 1 glass microfibre filter paper
after the medium had solidified. On each plate, conidial
suspension (0.5ml, 108 conidia/ml) was inoculated andspread evenly. After incubation at 25 �C in the dark, two
plates were taken out every three days and the microfi-
bre filter papers with fungal propagules were carefully
peeled off. The agar medium was sliced and soaked in
100ml dichloromethane:ethyl acetate (1:1, v/v) in a
250ml conical flask over night. Crude extracts were
harvested by evaporating the organic solvent and anal-
ysed by HPLC to determine the production of toxicmetabolites. The experiment was repeated twice.
Investigations on toxin production on rice grain were
conducted for comparison. Fifty grams of ‘‘American
Prefluffed Rice’’ (EasyCook, UK) were soaked over
night in 50ml deionised water in a 500ml conical flask.
The autoclaved rice was inoculated with 1ml spore
suspension (107 conidia/ml) and incubated at 25 �C in
the dark. Nine replicates were prepared for both strains.After 10, 20, and 30 days of incubation, the weight of
three batches per strain was determined and each batch
was divided into two equal parts. One part was sus-
pended in 1000ml aq. Tween 80 (0.05 %, v/v) and the
spore concentration was determined with a Rosenthal
haemocytometer. The colonised rice kernels from the
other part were crushed in liquid nitrogen and then ex-
tracted three times for 30min in 100ml ethyl ace-tate:dichloromethane (1:1, v/v) in a sonicator. After
extraction, the mixture was filtered through Whatman�sNo. 1 filter paper, the organic phases were pooled and
washed with 300ml deionised water and the crude ex-
tracts were harvested by evaporating the solvents in
vacuo. Two independent assessments with three repli-
cates each were conducted.
2.3. Submerged cultivation
2.3.1. Toxin production in large-scale fermentation
Metabolite production in fermenter cultures was as-
sessed for both strains. The fungi were pre-cultured in
1000ml conical flasks with 250ml sabouraud dextrose
broth (SDB, Difco) for five days at 23 �C and 150 rpm
and then 100ml were transferred to a 10L fermenterwith 9000ml SDB, growing for seven days at pH 6,
500 rpm, 23 �C and 150L/h air flow. The culture filtrate
was harvested over a CEPA separator with 10,000 rpm
and then filtered. Three replicates of 300 ml were ex-
tracted twice with 300ml dichloromethane:ethyl acetate
(1:1, v/v) for 6 h. Extracts were diluted in metha-
nol:acetonitrile (1:1, v/v) and analysed by HPLC de-
scribed below.
2.3.2. Influence of incubation time on toxin production
Conical flasks (250ml) were charged with 100ml CD
liquid medium containing 5% mycological peptone.
Each flask was inoculated with 0.5ml spore suspension
(108 conidia/ml). The flasks were incubated in dark at
24 �C and 110 rpm on a rotary shaker (Sanyo Gallenk-
amp). Every three days, the cultures from the duplicatedflasks were taken out and filtered through two layers of
Kimwipes and then through Whatman�s No. 1 filter
paper and the filtrate was extracted to determine the
dynamics of toxin production. The variations in pH and
biomass throughout the incubation time were deter-
mined. Correlations between the production of different
dtxs as well as pH and biomass were analysed by cal-
culating Pearson�s correlation coefficient with the pro-gram SPSS 11.0.0 (SPSS Inc.).
2.3.3. Influence of different carbon and nitrogen ratios and
insect homogenates on toxin production
The impact of different nutrient components on the
level of toxic metabolite secretion was evaluated by
growing fungal cultures in media with different ratios of
glucose and peptone as carbon and nitrogen sources(Table 3). Different amounts of insect homogenates
from Tenebrio molitor adults and from the cockroach
Blaberus discoidalis were also used as nutrient sources
for evaluations (Table 3). The adults of Tenebrio and
cockroach were frozen to death for 30min at )80 �C and
homogenised under liquid nitrogen. The homogenates
were dried in oven under 60 �C for 48 h. Additions of
Table 1
Destruxin productions in rice cultures from M. anisopliae strains V245 and V275 over time
Days post-inoculation Dtx yield in mg per 100 g rice (dry weight)
V245 V275
Dtx A Dtx B Dtx E Dtx A Dtx B Dtx E
10 5.4� 1.0 5.8� 0.8 n.d. 8.2� 2.2 0.8� 0.16 n.d.
20 17.6� 0.44 7.6� 1.0 n.d. 9.6� 2.0 6.4� 2.4 n.d.
30 28.6� 3.8 14.2� 2.4 n.d. 1.8� 1.8 34.0� 4.2 n.d.
Mean� SE; n.d., not detected.
170 C. Wang et al. / Journal of Invertebrate Pathology 85 (2004) 168–174
both insect homogenates to CD CN3 (C:N¼ 50:50)
were included to compare the induction effect on toxinproduction. Culture filtrates were harvested after incu-
bating for eight days. The putative toxins were extracted
as described above. Each treatment had two replicates.
2.4. Analytical analysis
The chromatographic profiles of above crude extract
samples were detected with a Dionex HPLC system asdescribed before (Wang et al., 2003). Briefly, the mobile
phase was a linear gradient of double-deionised water
and acetonitrile at a flow rate of 1ml/min. Twenty-five
microlitres of each sample (50 ll in case of extracts from
rice cultures) were injected and monitored at 215 nm.
Dtxs were identified by comparison with standard
chromatograms and by mass spectrometry. Electrospray
ionisation (ESI) was carried out on a MicromassQuattro II triple quadrupole instrument by loop injec-
tion using a Hewlett-Packard 1050 LC autosampler into
a methanol:water (1:1, v/v) stream. Low-resolution
electronic ionisation (EI)/chemical ionisation (CI) mass
measurements were carried out on the same instrument
using a Fisons AS 200 autosampler injecting onto a
dedicated automated roboprobe system into a stream of
methanol:water (1:1, v/v).
Fig. 1. Toxin production dynamics of strains V245 (A) and V275 (B) in
Czapek Dox liquid medium.
3. Results
3.1. Toxin production in solid cultivation
No cyclic peptide metabolites were detected in CD
solid medium from both strains after different incuba-tion periods (data not shown) by HPLC analysis. Con-
idia and dtx production of strains V245 and V275 grown
on rice were compared over time. The spore yield from
strain V275 was lower compared to that of strain V245
at 30 days post-inoculation (dpi). The production of
dtxs A and B could be determined in rice cultures from
both strains in an increasing trend with the elongated
incubation time, while no dtx E was detected from bothcultures up to 30 dpi (Table 1). Interestingly, strain V275
produced approx. 9mg per 100 g rice dtx A at 10 and
20 dpi but after 30 days, only approx. 2mg of this
compound could be detected. Dtx B production was
very low at 10 dpi but increased to 34mg at 30 dpi(Table 1).
3.2. Toxin production in liquid medium
In large-scale fermenter cultures, no dtxs could be
detected for either strain after incubation for five days.
However, in lab-scale flask cultures, three cyclic peptide
toxins, dtxs A, B, and E were detected in the culturefiltrates from day 3 on (Fig. 1). For strain V245 the
production of dtxs A and B reached its maximum at day
C. Wang et al. / Journal of Invertebrate Pathology 85 (2004) 168–174 171
six and then decreased slightly (Fig. 1A), while for V275,18 days of incubation gave the highest amount of both
dtxs A and B (Fig. 1B). The highest amounts of dtx E
were produced in liquid cultures after incubation for
Fig. 2. pH and biomass dynamics of strains V245 (A) and V275 (B) in
Czapek Dox liquid medium.
Fig. 3. HPLC chromatograph of crude extract from strain V275 after nine day
and their molecular weight (MW in g/mol) determined by mass spectrometr
nine days for both V245 and V275 and the productiondecreased sharply afterwards (Fig. 1). With longer in-
cubation time, the pH value of the culture medium de-
creased (Fig. 2). At the same time, the fungal biomass
kept increasing up to day 9 and then decreased for V245
(Fig. 2a), while no significant differences could be de-
tected in biomass production of V275 after nine days of
incubation (P > 0:05) (Fig. 2B).Mass spectrometry analysis confirmed that the peaks
at 14.46� 0.25min, 18.85� 0.17min, and 21.09� 0.32
min in the HPLC analysis were dtxs E, A, and B, respec-
tively. The compound eluted at 13.93� 0.28min had a
molecular weight of 611 g/mol and was confirmed to be E
diol (Fig. 3). Secretion of E diol could be detected in liquid
medium from day 3 on and increased gradually for both
strains V245 and V275 (Fig. 4).
Correlations between the production of the majordtxs A, B, and E, biomass and culture pH were esti-
mated for both M. anisopliae strains (Table 2). The re-
sults showed that secretions of dtxs A and B were
significantly associated (a ¼ 0:01) and both were sig-
nificantly negatively correlated with the pH value of the
culture medium (a ¼ 0:05). The production of dtx A was
also found to be significantly associated with biomass
production (a ¼ 0:05), while no significant associationswere observed between the production of dtxs B, E, and
biomass (Table 2).
3.3. Effect of different media components on toxin
production
Media studies revealed that toxin secretion in liquid
medium was highly influenced by different carbon/
s of incubation showing the signals of the main cyclic peptide products
y analysis.
Table 2
Pearson relationships between different parameters of strain V245
(below diagonal) and V275 (above diagonal)
Dtx A Dtx B Dtx E pH Biomass
Dtx A 0.992�� 0.226 )0.844� 0.661�
Dtx B 0.926�� 0.200 )0.808� 0.637
Dtx E 0.434 0.508 )0.318 0.378
pH )0.741� )0.748� )0.221 )0.510Biomass 0.764� 0.540 0.497 )0.363* Significance at 0.05 level.** Significance at 0.01 level.
Table 3
Biomass, pH, and toxin profiles of the strain V245 detected in different nutr
Media Ingredients Conc. (g/L) Biomass (g/100ml)
CN1 Glucose 30 0.73� 0.10
Peptone 0
CN2 Glucose 0 0.58� 0.11
Peptone 30
CN3 Glucose 25 0.64� 0.05
Peptone 5
CN4 Glucose 20 0.52� 0.05
Peptone 10
CN5 Glucose 15 0.46� 0.01
Peptone 15
CN6 Glucose 10 0.51� 0.03
Peptone 20
CN7 Glucose 5 0.39� 0.01
Peptone 25
M1 Mealworm 1 0.44� 0.00
homogenate
M2 Mealworm 3 0.71� 0.02
homogenate
CN3+M1 Mealworm — 0.78� 0.00
homogenate
C1 Cockroach 1 0.34� 0.01
homogenate
C2 Cockroach 3 0.79� 0.05
homogenate
CN3+C1 Cockroach — 0.75� 0.03
homogenate
Fig. 4. E diol production dynamics of strains V245 and V275 in
Czapek Dox liquid media.
172 C. Wang et al. / Journal of Invertebrate Pathology 85 (2004) 168–174
nitrogen ratios as well as by the addition of insect ho-mogenates (Table 3). The amount of dtxs A, B, and E
produced by strain V245 increased with increasing
peptone content in the medium. Comparatively, the
highest amount of toxins was produced in medium with
peptone as single nutrient source (CN2), the second
highest amount in medium CN7 (peptone:glucose¼ 5:1)
and then in medium CN6 (peptone:glucose¼ 2:1) (Table
3). Medium with the same C:N ratio like Czapek Dox(CN3) resulted in a lower amount of toxins, similar to
medium CN5 (C:N¼ 50:50) (Table 3).
Interestingly, no toxins were detected by HPLC when
using insect homogenates in different percentages of
both Tenebrio molitor (M1, 1%; M2, 3%) and Blaberus
discoidalis (C1, 1%; C2, 3%) as single nutrient source.
Media CN3+M1 and CN3+C1 resulted in very low
amounts or not detectable amount of dtxs. The pHvalue and biomass production in cultures with both in-
sect homogenates were usually higher than in the media
with artificial nutrient sources (Table 3). The studies on
strain V275 displayed a similar trend of toxin produc-
tion in different media (data not shown).
4. Discussion
Investigations on dtx production by M. anisopliae in
this study showed that three major dtxs A, B, and E
could be detected in liquid CD medium in a lab-scale
ient media
pH Dtx A (mg/l) Dtx B (mg/l) Dtx E (mg/l)
4.93� 0.01 2.93� 0.54 1.59� 0.40 2.45� 0.42
6.63� 0.08 18.53� 0.70 4.95� 0.79 13.13� 0.99
3.75� 0.02 6.91� 0.44 2.78� 0.17 3.53� 0.72
3.71� 0.11 14.48� 0.95 4.55� 0.59 3.82� 0.53
4.07� 0.05 6.96� 0.82 2.60� 0.15 0.46� 0.18
3.98� 0.04 15.19� 0.98 4.43� 0.25 2.39� 0.28
5.61� 0.01 15.20� 0.84 5.33� 0.48 10.18� 1.06
7.83� 0.04 0 0 0
7.60� 0.01 0 0 0
4.97� 0.01 0.80� 0.17 1.81� 0.67 0
8.18� 0.03 0 0 0
7.79� 0.15 0 0 0
5.77� 0.21 0.77� 0.06 0 0
C. Wang et al. / Journal of Invertebrate Pathology 85 (2004) 168–174 173
flask but not in solid CD agar for both strains V245 andV275. Strain V275 produced more toxic metabolites in
liquid cultures. Interestingly, dtx E was not detected in
rice grains from both strains, the same was reported by
Liu and Tzeng (1999), however, the potential mecha-
nism remains to be elucidated in future studies. No
toxins could be detected in large-scale fermentation,
where the aeration was higher than in the conical flasks
(Patrick et al., 1993). It has been shown that high aer-ation reduces the metabolite production of swainsonine
by M. anisopliae (Patrick et al., 1993). Our data suggest
that the aeration regime also has a significant impact on
dtx production. From a safety point of view, the ob-
servations indicate that the risk assessment of toxic
metabolites produced by fungal biological agents should
be evaluated in association with the methods and media
as well as the strain used in mass production.The results of toxin secretion dynamics of both
strains showed that the concentrations of dtxs increased
up to the 7–9th day of incubation and then this trend
was followed by either a noticeable decrease (dtx E) or
more or less pronounced (dtxs A and B). In contrast, dtx
E diol was detected to increase outstandingly from the
9th day on. The less toxic dtx E diol was previously
described as dtx E (Cherton et al., 1991; Lange et al.,1992) and later confirmed as a new toxin (Jegorov et al.,
1998; Wahlman and Davidson, 1993), a product resulted
from enzymatic hydrolysis of the epoxide function of
dtx E inside the mycelium (Loutelier et al., 1996). The
responsible degradation enzyme(s) has (have) not been
identified, however, interestingly, the injection of dtx E
into the locust haemolymph also resulted in the detec-
tion of E diol, suggesting that the transformation pro-cess had occurred within the insect haemocoel (Cherton
et al., 1991). Nevertheless, it is still unknown whether
the dtx E is detoxified by insect or hydrolysed by M.
anisopliae itself. Additionally, the conjugated glutathi-
one dtx E, cysteinyl dtx E, sulphated, and phosphory-
lated dtx E have been detected in locusts and G.
mellonella (Hubert et al., 1999; Lange et al., 1992).
In this study, we found for the first time that theproduction of dtxs A and B is significantly correlated
(a ¼ 0:01). The overall relationships between dtx A, B,
and dtx E were less positive, but up to the 9th day, these
three toxins had a similar increasing trend and then the
association was not clear due to the degradation of dtx
E into E diol. The observations suggest that the encoded
genes for dtxs A, B, and E are located as a gene cluster
in the genome and up-regulated at the same level. Sup-portively, our recent study showed that a mutant from
strain V275 had completely lost the ability to produce
dtxs after missing a conditionally dispensable chromo-
some (Wang et al., 2003). In addition, toxin gene clus-
tering has been extensively reported in plant pathogenic
fungi, e.g., fumonisin encoding genes in Fusarium verti-
cillioides (Seo et al., 2001); aflatoxin encoding genes in
Aspergillus parasiticus (Cary et al., 2002); AK-toxinencoding genes in Alternaria alternata (Hatta et al.,
2002).
In vitro toxin secretion of M. anisopliae could be
significantly influenced by culture conditions. In this
study, the result of different carbon/nitrogen combina-
tions revealed that higher concentrations of peptone
(>60%) in liquid media favours toxin production. Liu
et al. (2000) reported that maltose and peptone were thebest carbon and nitrogen sources with the addition of
amino acid b-alanine for the production of dtxs by M.
anisopliae. The optimal compositions for the production
of dtxs A and B were different but in contrast to the
observation in this study, usually higher with increased
concentrations of maltose (ca. 70%). It is possibly due to
genetic and physiological differences between different
strains of M. anisopliae. A previous study showed thatthe addition of a low concentration (<10mg/L) of cy-
clopeptolide 90–215, a natural pipecolic acid-containing
cyclopeptolide composed of nine a-amino acid residues,
in the medium could increase the production of dtxs by
1.3- to 12.5-fold associated with different strains of M.
anisopliae (Espada and Dreyfuss, 1997), suggesting that
cyclopeptolide either serves as nitrogen source or an
intermediate product during the synthesis of dtxs.Destruxins have been often implicated as one of the
causes of insect death infected with M. anisopliae (Butt
et al., 1994; Vestergaard et al., 1995; Vey et al., 2001),
and they could be detected in variable amounts in in-
fected larvae of Galleria associated with mycoses by
different M. anisopliae strains (Amiri-Besheli et al.,
2000). However, in this study, it is surprising that no
toxins were detected when using insect homogenates assingle nutrients or included in CN3 liquid medium. The
potential regulation machinery remains to be elucidated
in further studies.
Acknowledgments
This work was supported by the Quality of Life and
Management of Living Resources Programme of the
European Commission, Key Action 1 on Food, Nutri-
tion and Health, QLK1-2001-01391 (RAFBCA). The
authors thank Dr. Alain Vey (INRA, France) for pro-
viding samples of pure dtxs A and E as well as Dr. John
Davies for his help of the analysis with the mass spec-trometry.
References
Amiri-Besheli, B., Khambay, B., Cameron, S., Deadman, M.L., Butt,
T.M., 2000. Inter- and intra-specific variation in destruxin
production by insect pathogenic Metarhizium spp., and its signif-
icance to pathogenesis. Mycol. Res. 104, 447–452.
174 C. Wang et al. / Journal of Invertebrate Pathology 85 (2004) 168–174
Bailey, A.M., Kershaw, M.J., Hunt, B.A., Paterson, I.C., Charnley,
A.K., Reynolds, S.E., Clarkson, J.M., 1996. Cloning and sequence
analysis of an intron-containing domain from a peptide synthetase-
encoding gene of the entomopathogenic fungus Metarhizium
anisopliae. Gene 173, 195–197.
Brousseau, C., Charpentier, G., Belloncik, S., 1996. Susceptibility of
spruce budworm, Choristoneura fumiferana Clemens, to destruxins,
cyclodepsipeptidic mycotoxins of Metarhizium anisopliae. J. Inver-
tebr. Pathol. 68, 180–182.
Butt, T.M., Ibrahim, L., Ball, B.V., Clark, S.J., 1994. Pathogenicity of
the entomogenous fungi Metarhizium anisopliae and Beauveria
bassiana against crucifer pests and the honey bee. Biocontrol Sci.
Technol. 4, 207–214.
Butt, T.M., Jackson, C.W., Magan, N., 2001. Introduction—Fungal
biological control agents: Progress, problems and potential. In:
Butt, T.M., Jackson, C.W., Magan, N. (Eds.), Fungal Biological
Control Agents: Progress, Problems and Potential. CABI Publish-
ing, Wallingford, UK, pp. 1–8.
Cary, J.W., Dyer, J.M., Ehrlich, K.C., Wright, M.S., Liang, S.H.,
Linz, J.E., 2002. Molecular and functional characterization of a
second copy of the aflatoxin regulatory gene, aflR-2, from
Aspergillus parasiticus. Biochim. Biophys. Acta 1576, 316–323.
Cherton, J.-C., Lange, C., Mulheim, C., Pais, M., Cassier, P., Vey, A.,
1991. Direct in vitro and in vivo monitoring of destruxins
metabolism in insects using internal surface reversed-phase high-
performance liquid chromatography; I. Behaviour of E destruxin in
locusts. J. Chromatogr. B 566, 511–524.
Dumas, C., Robert, P.H., Pais, M., Vey, A., Quiot, J.M., 1994.
Insecticidal and cytotoxic effects of natural and hemisynthetic
destruxins. Comp. Biochem. Physiol. C 108, 195–203.
Espada, A., Dreyfuss, M.M., 1997. Effect of the cyclopeptolide 90–215
on the production of destruxins and helvolic acid by Metarhizium
anisopliae. J. Ind. Microbiol. Biotechnol. 19, 7–11.
Hatta, R., Ito, K., Hosaki, Y., Tanaka, T., Tanaka, A., Yamamoto,
M., Akimitsu, K., Tsuge, T., 2002. A conditionally dispensable
chromosome controls host-specific pathogenicity in the fungal
plant pathogen Alternaria alternata. Genetics 161, 59–70.
Hsiao, Y.M., Ko, J.L., 2001. Determination of destruxins, cyclic
peptide toxins, produced by different strains of Metarhizium
anisopliae and their mutants induced by ethyl methane sulfonate
and ultraviolet using HPLC method. Toxicon 39, 837–841.
Hubert, M., Cherton, J.C., Vey, A., Lange, C., 1999. Metabolites of A
and E destruxins in Galleria mellonella larvae using negative-ion
fast-atom bombardment mass spectrometry. Rapid Commun.
Mass Spectrom. 13, 179–184.
Jegorov, A., Sedmera, P., Matha, V., 1993. Biosynthesis of destruxins.
Phytochemistry 33, 1403–1405.
Jegorov, A., Sedmera, P., Havlicek, V., Matha, V., 1998. Destruxin
Ed1 a cyclopeptide from the fungus Metarhizium anisopliae.
Phytochemistry 49 (6), 1815–1817.
Kershaw, M.J., Moorhouse, E.R., Bateman, R.P., Reynolds, S.E.,
Charnley, A.K., 1999. The role of destruxins in the pathogenicity of
Metarhizium anisopliae for three species of insect. J. Invertebr.
Pathol. 74, 213–223.
Kodaira, Y., 1961. Biochemical studies on the muscardine fungi in the
silkworms, Bombyx mori. J. Fac. Text. Sci. Technol. 5, 1–68.
Lange, C., Loutelier, C., Cherton, J.C., Cassier, P., Vey, A., Pais, M.,
1992. Desorption of ions from locust tissues. 2. Metabolites of E-
destruxin using negative-ion fast-atom-bombardment mass-spec-
trometry. Rapid Comm. Mass Spectrom. 6, 28–31.
Liu, B.L., Tzeng, Y.M., 1999. Water content and water activity for the
production of cyclodepsipeptides in solid-state fermentation by
Metarhizium anisopliae. Biotechnol. Lett. 21, 657–661.
Liu, B.L., Chen, J.W., Tzeng, Y.M., 2000. Production of cyclodepsi-
peptides destruxin A and B from Metarhizium anisopliae. Biotech-
nol. Prog. 16, 993–999.
Loutelier, C., Cherton, J.-C., Lange, C., Traris, M., Vey, A., 1996.
Studies on the dynamics of the production of destruxins by
Metarhizium anisopliae: Direct high-performance liquid chromato-
graphic and fast atom bombardment mass spectrometric analysis
correlated with biological activity tests. J. Chromatogr. A 738, 181–
189.
Marahiel, M.A., 1992. Multidomain enzymes involved in peptide
synthesis. FEBS Lett. 307, 40–43.
Patrick, M., Adlard, M.W., Keshavarz, T., 1993. Production of an
indolizidine alkaloid, swainsonine, by the filamentous fungus
Metarhizium anisopliae. Biotechnol. Lett. 15, 997–1000.
Pedras, M.S.C., Irina, Z.L., Ward, D.E., 2002. The destruxins:
synthesis, biosynthesis, biotransformation, and biological activity.
Phytochemistry 59, 579–596.
Seo, J.A., Proctor, R.H., Plattner, R.D., 2001. Characterization of
four clustered and coregulated genes associated with fumonisin
biosynthesis in Fusarium verticillioides. Fungal Genet. Biol. 34,
155–165.
Strasser, H., Vey, A., Butt, T.M., 2000. Are there any risks in using
entomopathogenic fungi for pest control, with particular reference
to the bioactive metabolites of Metarhizium, Tolypocladium and
Beauveria species? Biocontrol Sci. Technol. 10, 717–735.
Vestergaard, S., Gillespie, A.T., Butt, T.M., Schreiter, G., Eilenberg,
J., 1995. Pathogenicity of the hyphomycete fungi Verticillium
lecanii and Metarhizium anisopliae to the western flower thrips,
Frankliniella occidentalis. Biocontrol Sci. Technol. 5, 185–192.
Vey, A., Hoagland, R., Butt, T.M., 2001. Toxic metabolites of fungal
biocontrol agents. In: Butt, T.M., Jackson, C.W., Magan, N.
(Eds.), Fungi as Biocontrol Agents. CAB International, Walling-
ford, UK, pp. 311–345.
Wahlman, M., Davidson, B.S., 1993. New destruxins from the
entomopathogenic fungus Metarhizium anisopliae. J. Nat. Prod.
(Lloydia) 56, 643–647.
Wang, C.-S., Skrobek, A., Butt, T.M., 2003. Concurrence of losing a
chromosome and the ability to produce destruxins in a mutant of
Metarhizium anisopliae. FEMS Microbiol. Lett. 226, 373–378.
Zuber, P., 1991. Non-ribosomal peptide synthesis. Curr. Opin. Cell
Biol. 3, 1046–1050.