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. 2012;7(4):e35545.
doi: 10.1371/journal.pone.0035545. Epub 2012 Apr 20.

Turning the 'mustard oil bomb' into a 'cyanide bomb': aromatic glucosinolate metabolism in a specialist insect herbivore

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Turning the 'mustard oil bomb' into a 'cyanide bomb': aromatic glucosinolate metabolism in a specialist insect herbivore

Einar J Stauber et al. PLoS One. 2012.

Abstract

Plants have evolved a variety of mechanisms for dealing with insect herbivory among which chemical defense through secondary metabolites plays a prominent role. Physiological, behavioural and sensorical adaptations to these chemicals provide herbivores with selective advantages allowing them to diversify within the newly occupied ecological niche. In turn, this may influence the evolution of plant metabolism giving rise to e.g. new chemical defenses. The association of Pierid butterflies and plants of the Brassicales has been cited as an illustrative example of this adaptive process known as 'coevolutionary armsrace'. All plants of the Brassicales are defended by the glucosinolate-myrosinase system to which larvae of cabbage white butterflies and related species are biochemically adapted through a gut nitrile-specifier protein. Here, we provide evidence by metabolite profiling and enzyme assays that metabolism of benzylglucosinolate in Pieris rapae results in release of equimolar amounts of cyanide, a potent inhibitor of cellular respiration. We further demonstrate that P. rapae larvae develop on transgenic Arabidopsis plants with ectopic production of the cyanogenic glucoside dhurrin without ill effects. Metabolite analyses and fumigation experiments indicate that cyanide is detoxified by β-cyanoalanine synthase and rhodanese in the larvae. Based on these results as well as on the facts that benzylglucosinolate was one of the predominant glucosinolates in ancient Brassicales and that ancient Brassicales lack nitrilases involved in alternative pathways, we propose that the ability of Pierid species to safely handle cyanide contributed to the primary host shift from Fabales to Brassicales that occured about 75 million years ago and was followed by Pierid species diversification.

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Conflict of interest statement

Competing Interests: The authors have declared that no competing interests exist.

Figures

Figure 1
Figure 1. The glucosinolate-myrosinase system and proposed pathways of aromatic nitrile metabolism in P. rapae larvae.
A. Myrosinase-catalyzed hydrolysis of glucosinolates upon plant tissue disruption yields an unstable aglucone which most commonly rearranges to a toxic isothiocyanate. Larvae of P. rapae redirect glucosinolate breakdown to the formation of simple nitriles by the gut nitrile-specifier protein (NSP). R, variable side chain. B. Examples of glucosinolates with aromatic (i.e. benzene ring-containing) side chains. C. Upon ingestion of plant material by P. rapae larvae, 1 and 2 are converted to phenylacetonitrile (3) and 3-phenylpropionitrile (4), respectively. These undergo further metabolism to the glycine conjugates 5–7 which are excreted with the feces. The major metabolite of 1 is hippuric acid (N-benzoylglycine, 5; 23, 24), the major metabolite of 2 is N-(3-phenylpropionyl)glycine (7, this study). N-phenylacetylglycine (6) is formed as a minor metabolite from both glucosinolates. This study establishes the pathways from 3 and 4 to 5–7. While the conversion of 3 to 5 involves a C1-loss through HCN release (route a), the side chain of 4 is maintained throughout its major metabolic pathway (route e). Reactions a, b and c are catalyzed by an NADPH-dependent microsomal enzyme activity. Reaction d, and likely, reaction e involve nitrilase activity from the ingested plant material. Compounds 9, 11b and 12 were detected as intermediates in this study. Bold and thin arrows indicate major and minor metabolic pathways, respectively.
Figure 2
Figure 2. Differential metabolism of aromatic glucosinolates with different side chain lengths in P. rapae larvae.
Feces were collected from P. rapae larvae that had fed on leaves of A. thaliana Col-0, 35S:CYP79A2, Tropaeolum majus, or Nasturtium officinale. Glycine conjugates 5 (white), 6 (light-gray), and 7 (dark-gray) were quantified in feces extracts by HPLC-MS using 13C-labeled 5, 6, and 7 as standards. Means ± SD are given with N (number of biological replicates). Each replicate represents a pair of larvae.
Figure 3
Figure 3. Organic phase metabolites of 2-phenylethylglucosinolate in plant homogenates and P. rapae larvae.
Dichloromethane extracts of N. officinale leaf autolysates (A) and the organic phase of dichloromethane/water extracts of feces from P. rapae larvae that had fed on N. officinale leaves (B) were analyzed by GC-MS. Shown are total ion current traces. IS, internal standard.
Figure 4
Figure 4. NADPH-dependent hydroxylation of aromatic nitriles by P. rapae gut microsomes.
Larval gut microsomes were incubated with 2.5 mM phenylacetonitrile 3 (AD) or 2.5 mM 3-phenylpropionitrile 4 (EH) for 45 min at 31°C in the presence (A, CE, G, H) or absence (B, F) of NADPH. In C and G, microsomes were flushed with CO prior to addition of NADPH. In D and H, microsomes were heated (95°C, 5 min) prior to the assay. Assays were extracted with dichloromethane, and the organic phases analyzed by GC-MS. Shown are total ion current traces. IS, internal standard.
Figure 5
Figure 5. Cyanide is released as a consequence of aromatic nitrile hydroxylation by P. rapae gut microsomes.
Larval gut microsomes were incubated with 2.5 mM phenylacetonitrile 3 (AD) or 2.5 mM 3-phenylpropionitrile 4 (EH) in the presence (A, CE, G, H) or absence (B, F) of NADPH. Cyanide was captured by derivatization. Shown are HPLC-MS/MRM traces of the derivatization product (X). In C and G, microsomes were flushed with CO prior to addition of NADPH. In D and H, microsomes were heated (95°C, 5 min) prior to the assay.
Figure 6
Figure 6. Performance of P. rapae larvae on cyanogenic plants.
P. rapae and S. littoralis larvae were allowed to feed on either A. thaliana Col-0 wildtype (gray) or cyanogenic A. thaliana 3x/dhurrin plants (dark grey). After 10 d, surviving larvae were counted and weighted. Larval mortality is given as means ± SEM of three independent experiments. Larval weights are given as means ± SEM from one out of three independent experiments. Results of all experiments are shown in Table S1. Numbers in the bars indicate N (number of surviving individuals).
Figure 7
Figure 7. Detoxification of cyanide in P. rapae.
A. Scheme of the reaction catalyzed by rhodanese. B. Scheme of the reaction catalyzed by β-cyanoalanine synthase. C. β-Cyanoalanine content in P. rapae larvae after nine days of feeding on wildtype, benzylglucosinolate-rich (35S:CYP79A2) and cyanogenic (3x/dhurrin) A. thaliana plants. Larvae were extracted with dichloromethane and water. The aqueous phase was analyzed by HPLC-MS. Data are means ± SD. N (number of larvae analyzed) is given in the bars, p values (t-test) for the comparison with Col-0 above the bars. D. Quantitative analysis of β-cyanoalanine and SCN with M+1 after 24 h [15N]HCN fumigation of the larvae. Each bar represents the mean ± SD of N = 16 individual larvae. P values (t-test) are given above the bars for the comparison of fumigated (dark-grey bars) to non-fumigated larvae (light-grey bars). Data in C and D are each from one out of at least three independent experiments that all showed significant differences (p<0.05).

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