RAPID COMMUNICATIONS IN MASS SPECTROMETRY Rapid Commun. Mass Spectrom. 2004; 18: 2577–2586 Published online in Wiley InterScience (www.interscience.wiley.com). DOI: 10.1002/rcm.1659 Mass spectrometric studies on the intrinsic stability of destruxin E from Metarhizium anisopliae Ed Dudley 1 *, Chengshu Wang 2 , Anke Skrobek 2 , Russell P. Newton 1,2 and Tariq M. Butt 2 1 Biomolecular Analysis Mass Spectrometry Laboratory, University of Wales Swansea, Swansea SA2 8PP, UK 2 School of Biological Sciences, University of Wales Swansea, Swansea SA2 8PP, UK Received 3 June 2004; Revised 1 September 2004; Accepted 1 September 2004 Destruxins are of current interest as bioactive agents. They are cyclic hexadepsipeptides produced by fungi, the most common destruxins, A, B and E, differing in the structure of a side chain. Before they can be widely used, the potential risk of destruxins and their metabolites entering the human food chain must to be assessed; thus, knowledge of the structures of their degradation products is essential. Here we report a study aimed at identifying, by tandem mass spectrometry and accurate mass analysis, the products resulting from thermally and temporally induced degradation of des- truxin E. The degradation products fell into two groups: those with relatively simple modifications of the side chain and those involving much more complex rearrangements. The structures of most of the degradation products were deduced from the MS data, with the major product being destrux- in E diol: significantly, this compound had previously been reported to have only been produced as a metabolic product of enzyme action rather than as a simple degradation product as demonstrated here. Copyright # 2004 John Wiley & Sons, Ltd. The entomogenous fungus Metarhizium anisopliae shows considerable promise as a biological control agent (BCA) for use in integrated pest management programmes, 1 where it may be applied as an environmental insecticide agent. 2,3 Several strains have been commercialised yet still much infor- mation is required by registration authorities regarding the risks it may pose to human health and the environment. Of particular concern are the bioactive metabolites secreted by Metarhizium. One major group of metabolites produced by this fungus consists of cyclic hexadepsipeptides called des- truxins. 4,5 These compounds are also known to be produced by the insect pathogen Aschersonia sp. 6 and the plant patho- gen Alternaria brassicae. 7 The most commonly produced destruxins are A, B and E with the latter usually predominat- ing. 4,8 The chemical structures of cyclic hexadepsipeptide destruxins A, B and E have the same backbone, with the gen- eral formula: – D -HA 1 - L -Pro 2 - L -Ile 3 - L -MeVal 4 - L -MeAla 5 -b- Ala 6 -, where HA is a D -a-hydroxy acid residue. The difference is found in the R residue (see Fig. 4) bound to HA which is – CH 2 –CH CH 2 , –CH 2 –CH(CH 3 ) 2 , and for dtx A, B and E, respectively. Some of the properties of these compounds have been reviewed by Vey et al. 5 and Pedras et al. 9 Little is known about the stability and fate of these com- pounds in the environment yet such information could help in risk assessment and possibly accelerate the registration process. Mass spectrometry has previously been applied to the analysis of destruxin metabolism, 10 identification from fungus extracts 11 and their gas-phase fragmentation, 12 and was therefore considered to be a useful technique for the study of destruxin E and related compounds. This paper provides the first detailed mass spectrometric analysis of the intrinsic stabi- lity of purified destruxins with attention focused on destruxin E, the most bioactive of the metabolites, 5,13 and its degradation products. This study forms part of a major programme to deter- mine if destruxins enter the food chain and pose a risk to humans and the environment. EXPERIMENTAL Chemicals All chemicals used were purchased from Fisher Scientific (UK) with the exception of leucine enkephalin purchased from Sigma Aldrich (UK). Water for the analytical analysis was prepared in-house using an Elix and Milli-Q system (Millipore, UK). Cultures and metabolites Metarhizium anisopliae strains V275 (isolated from Cydia pome- nella, Austria) and V245 (isolated from hay field soil, Finland) were grown in Czapek Dox liquid media and crude extracts of the metabolites prepared as described by Wang et al. 13 Destruxin E (dtx E) was purified using a Dionex HPLC system, equipped with a C18 reverse-phase column (Acclaim TM , silica, particle size: 5 mm, pore diameter: 120 A ˚ , length: 4.6 250 mm) and a UVD 340U diode-array detector at a flow rate of 1 mL/min. 13 Purified samples from different batch cultures were stored at 208C until required. Storage under different temperature conditions To evaluate the temperature stability of the purified dtx E as well as the comparative stability in crude extracts, the Copyright # 2004 John Wiley & Sons, Ltd. *Correspondence to: E. Dudley, BAMS Laboratory, University of Wales Swansea, Swansea, SA2 8PP, UK. E-mail: [email protected]Contract/grant sponsor: European Commission; contract/ grant number: QLK1-2001-01391.
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RAPID COMMUNICATIONS IN MASS SPECTROMETRY
Rapid Commun. Mass Spectrom. 2004; 18: 2577–2586
Published online in Wiley InterScience (www.interscience.wiley.com). DOI: 10.1002/rcm.1659
Mass spectrometric studies on the intrinsic stability
of destruxin E from Metarhizium anisopliae
Ed Dudley1*, Chengshu Wang2, Anke Skrobek2, Russell P. Newton1,2 and Tariq M. Butt2
1Biomolecular Analysis Mass Spectrometry Laboratory, University of Wales Swansea, Swansea SA2 8PP, UK2School of Biological Sciences, University of Wales Swansea, Swansea SA2 8PP, UK
Received 3 June 2004; Revised 1 September 2004; Accepted 1 September 2004
Destruxins are of current interest as bioactive agents. They are cyclic hexadepsipeptides produced
by fungi, the most common destruxins, A, B and E, differing in the structure of a side chain. Before
they can be widely used, the potential risk of destruxins and their metabolites entering the human
food chain must to be assessed; thus, knowledge of the structures of their degradation products is
essential. Here we report a study aimed at identifying, by tandem mass spectrometry and accurate
mass analysis, the products resulting from thermally and temporally induced degradation of des-
truxin E. The degradation products fell into two groups: those with relatively simple modifications
of the side chain and those involving much more complex rearrangements. The structures of most
of the degradation products were deduced from the MS data, with the major product being destrux-
in E diol: significantly, this compound had previously been reported to have only been produced as
a metabolic product of enzyme action rather than as a simple degradation product as demonstrated
here. Copyright # 2004 John Wiley & Sons, Ltd.
The entomogenous fungus Metarhizium anisopliae shows
considerable promise as a biological control agent (BCA)
for use in integrated pest management programmes,1 where
it may be applied as an environmental insecticide agent.2,3
Several strains have been commercialised yet still much infor-
mation is required by registration authorities regarding the
risks it may pose to human health and the environment. Of
particular concern are the bioactive metabolites secreted by
Metarhizium. One major group of metabolites produced by
this fungus consists of cyclic hexadepsipeptides called des-
truxins.4,5 These compounds are also known to be produced
by the insect pathogen Aschersonia sp.6 and the plant patho-
gen Alternaria brassicae.7 The most commonly produced
destruxins are A, B and E with the latter usually predominat-
ing.4,8 The chemical structures of cyclic hexadepsipeptide
destruxins A, B and E have the same backbone, with the gen-
Table 2. Identifications and verifications of destruxin E and its degradation products
UV peak m/z detected Mass accuracy (ppm) LCQ MS2/3Q-ToF AccMass MS
Q-ToF Acc MassMS/MS Modifications
E 594 0.5 H H H —1 666 0.5 H H H RO2 626 2.8 H H H RGM3 553, 1127 5.6 NC H NC RO4 594 0 H H H RGM5 562 0.3 H H H RO6 684 4 H H H RO7 ND NA ND ND ND NA8 654 1.2 H H H RGM9 ACN NA ND ND ND NA10 610 6.3 (1.0 Na adduct) H H H RGM11 612 1.9 H H H RGM12 ND NA ND ND ND NA13 630 1.3 H H H RGM14 603 NA ND H H NA15 512 37.1 ND H H RO
H, detected; NA, not available; NC, not clear; ND, not detected; ACN, possible gradient acetonitrile; RO, ring opening; RGM, R group modifica-tions (Fig. 4).
2582 E. Dudley et al.
Copyright # 2004 John Wiley & Sons, Ltd. Rapid Commun. Mass Spectrom. 2004; 18: 2577–2586
compound gave product ions at m/z 324, 211 and 183 and the
structure of the proposed compound and its fragmentations
are outlined in Fig. 7(e). It is proposed that the compound
arose from the loss of CH3NHCHCH3CO from the N ter-
minus of the ring-opened dtx E (Fig. 4) with the donation of
protons from this lost group back to the degradation product.
For the described fragmentations, the accuracy of the m/z
values in relation to the expected ions was 37.1 ppm diffe-
rence between the observed m/z and that expected for the ion
atm/z 512 with differences of 2.6, 10 and 11.3 ppm for the ions
at m/z 324, 211 and 183, respectively. The mass accuracy for
the [MþH]þ ion at m/z 512 is low (possible due to an unstable
signal); however, the MS/MS data gave better mass accuracy
and helped support this identification.
The structures of peaks 7, 9, 12 and 14 were not deduced.
Peak 7 was too low in intensity to be detected with any MS
Figure 5. The proposed ring opening and fragmentation of peak 11 (m/z 612) under MS/MS conditions.
Degradation products of destruxin E 2583
Copyright # 2004 John Wiley & Sons, Ltd. Rapid Commun. Mass Spectrom. 2004; 18: 2577–2586
data (Fig. 2(c)). Peak 9 was thought to arise from the acetoni-
trile gradient as the peak occurred around the time when the
HPLC gradient reached 100% organic solvent and mobile
phase related peaks are commonly detected in UV detection
at these time points. Peak 12 co-eluted with peak 11 which
was far in excess and masked the identity of the former (as
shown in Figs. 2(b) and 2(c)). Despite altering the gradient
used for the HPLC run, no improved separation was obtained
between these two peaks. Peak 14 was again of low intensity
but gave a possible [MþH]þ ion atm/z 603; however, its signal
intensity was too low to provide any further useful mass
spectrometric data for structural elucidation.
DISCUSSION
Purified destruxin E has been shown to degrade when stored
at all the temperatures examined, with the degradation
becoming more pronounced at temperatures at or above
258C. The degree of degradation in the purified sample has
also been shown to be mimicked in crude extracts; however,
to date no data concerning the comparative degradation
products from crude extracts has been obtained. The data
allowed the study of the degradation products formed from
purified destruxin E and suggested that two classes of degra-
dation product are formed (Table 2). The first group of degra-
dation products arises purely as a result of the R group of
the destruxin E being modified in some way; these modi-
fications are summarised in Table 3. The second class of
degradation products is formed by the ring opening of the
destruxin E followed by loss of parts of the structure and/
or modifications of the structure. This second class of product
proved more complex and therefore more difficult to obtain
useful structural information for. Highly intriguingly, among
15 detected peaks, mass spectrometric analysis of peaks 11
and 10 identified them as destruxin E diol (dtx Ed) and
destruxin F, respectively.14,15 Dtx Ed has been reported to
be easily formed from dtx E.8,9,16 The less toxic dtx Ed was
previously described as dtx E17,18 and later confirmed as a
new toxin.14,15 Dtx Ed has always been thought to arise
from the enzymatic hydrolysis of dtx E inside the mycelium
with its levels increasing with a comparative decrease in
destruxin E levels;8 however, its observation in this study
suggests that the conversion of dtx Ed from dtx E is a non-
enzymatic process since it could occur under storage condi-
tions and exhibits the change in comparative amounts as
previously reported.8 Dtx F was reported previously as a ‘nat-
ural’ product from the culture filtrate of M. anisopliae;14 the
data in our study suggests that it may instead be a degrada-
tion product formed from destruxin E rather than a newly
synthesised toxin. Peaks 1–4 were pre-existing in the dtx E
sample before the start of storage experiments. Mass analysis
indicated these ions were each related to the structure of dtx
E, eliminating the possibility of contamination during HPLC
purification; however, the dtx E derivates could have arisen
during the sample preparation storage under �208C for
1 month before the start of the experiments. In this respect,
peak 5, with an [MþH]þ ion at m/z 562, could be speculated
to be a derivative arising from peak 1 (m/z 666) rather than
arising directly from dtx E. This argument is based on the
structural similarities between the two compounds as peak
1 appears to lose part of its structure to form peak 5. Also,
as shown in Fig. 3, peak 1 decreases in UV response over
the different temperatures whereas peak 5 shows a compara-
tive increase in signal, adding weight to the idea that peak 1
degrades to form peak 5. Of further interest is peak 13
(m/z 630) which corresponds to destruxin E chlorohydrin
(again previously believed to be a new toxin released by
Metarrhizium anisopliae11 and shown here to arise from sam-
ple degradation). This degradation product contains a chlor-
ine atom which was not added to the sample at any point
during storage. A possible explanation for the formation
of this compound arises from the fact that destruxin E was
extracted in dichloromethane and this might cause contami-
nation of the storage solution with chlorine. Whilst this may
explain the formation of the chlorohydrin product in this pre-
sent study it is unknown whether the degradation reaction of
destruxin E with chloride ions is responsible for the presence
of this compound in fungal extracts. The other degradation
products detected involve ring opening with some loss of
the structure (peak 3 and 15) or possibly extensive modifica-
tion of the structure (peak 6).
The R group modified peaks give reliable structural
information and accurate mass and fragmentation data
allow the investigation of the structure of some of the more
unusual degradation products. This is demonstrated by the
fact that only three of these products have a mass lower than
their parent compound, dtx E, suggesting that complex
rearrangements occurred during degradation and these are
comparatively more complicated to elucidate. We feel that
the structures presented here for such compounds accurately
reflect the empirical formulae suggested by the accurate mass
analysis, and represent the most probable structures based
both on these data and on the fragmentation data obtained,
despite the complications arising from such unusual trans-
formations. In this study, thermal instability and degradation
of dtx E were studied under laboratory conditions; however,
environmentally, the detoxification/modification of de-
struxins by other biotic and abiotic factors is still poorly
Figure 6. R group modifications to destruxin E during
degradation.
2584 E. Dudley et al.
Copyright # 2004 John Wiley & Sons, Ltd. Rapid Commun. Mass Spectrom. 2004; 18: 2577–2586
understood. Further studies are required to elucidate the
persistence of destruxins in soil, their entry into the food
chain, their modifications by other organisms, plus particu-
larly the toxicity study of the degraded products identified in
this study.
AcknowledgementsThis work was supported by the Quality of Life and Manage-
ment of Living Resources Programme of the European
Commission, Key Action 1 on Food, Nutrition and Health,
QLK1-2001-01391 (RAFBCA).
Figure 7. Other degradation products: (a) isomerisation of the R group in peak 4; (b) identity and fragmentation of peaks 1 and
5; (c) identity and fragmentation of peak 6; (d) identity and fragmentation of peak 3; and (e) identity and fragmentation of peak 15.
Degradation products of destruxin E 2585
Copyright # 2004 John Wiley & Sons, Ltd. Rapid Commun. Mass Spectrom. 2004; 18: 2577–2586
REFERENCES
1. Butt TM, Jackson CW, Magan N (eds). Fungi as BiocontrolAgents: Progress, Problems and Potential. CAB International:Wallingford, UK, 2001.
2. Ignoffo CM. In CRC Handbook of Natural Pesticides, vol. V.Microbial insecticides, Part A, Entomogenous protozoa andfungi. CRC Press Inc.: Boca Raton, 1988; 243.
5. Vey A, Hoagland R, Butt TM. In Fungi as Biocontrol Agents:Progress, Problems and Potential, Butt TM, Jackson CW,Magan N (eds). CAB International: Wallingford, UK,2001; 311–345.