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Proceedings of the National Academy of Sciences of the United States of America logoLink to Proceedings of the National Academy of Sciences of the United States of America
. 2021 Apr 13;118(16):e2024463118. doi: 10.1073/pnas.2024463118

Cardenolides, toxicity, and the costs of sequestration in the coevolutionary interaction between monarchs and milkweeds

Anurag A Agrawal a,b,1, Katalin Böröczky a, Meena Haribal c, Amy P Hastings a, Ronald A White a, Ren-Wang Jiang d, Christophe Duplais e
PMCID: PMC8072370  PMID: 33850021

Significance

Interactions between plants and herbivores constitute a major pathway of energy transfer up the food chain. As a consequence, evolution by natural selection has honed the chemically mediated antagonistic interactions between these groups. Monarch butterflies and milkweeds serve as royal representatives in deciphering such coevolution, and our study takes a mechanistic and manipulative approach to understand how the tropical milkweed, Asclepias curassavica, defends itself against monarch butterflies, which would seem to be impervious feeders. By directly observing plant–herbivore interactions and coupling this with experiments on isolated toxins and the monarch’s neural sodium-potassium pump enzymes, we show that tropical milkweed produces a burdensome cardenolide toxin, and monarchs convert it to less toxic compounds, the latter sequestered for their own benefit.

Keywords: chemical ecology, coevolution, monarch butterfly (Danaus plexippus), milkweeds Asclepias, plant–insect interactions

Abstract

For highly specialized insect herbivores, plant chemical defenses are often co-opted as cues for oviposition and sequestration. In such interactions, can plants evolve novel defenses, pushing herbivores to trade off benefits of specialization with costs of coping with toxins? We tested how variation in milkweed toxins (cardenolides) impacted monarch butterfly (Danaus plexippus) growth, sequestration, and oviposition when consuming tropical milkweed (Asclepias curassavica), one of two critical host plants worldwide. The most abundant leaf toxin, highly apolar and thiazolidine ring–containing voruscharin, accounted for 40% of leaf cardenolides, negatively predicted caterpillar growth, and was not sequestered. Using whole plants and purified voruscharin, we show that monarch caterpillars convert voruscharin to calotropin and calactin in vivo, imposing a burden on growth. As shown by in vitro experiments, this conversion is facilitated by temperature and alkaline pH. We next employed toxin-target site experiments with isolated cardenolides and the monarch’s neural Na+/K+-ATPase, revealing that voruscharin is highly inhibitory compared with several standards and sequestered cardenolides. The monarch’s typical >50-fold enhanced resistance to cardenolides compared with sensitive animals was absent for voruscharin, suggesting highly specific plant defense. Finally, oviposition was greatest on intermediate cardenolide plants, supporting the notion of a trade-off between benefits and costs of sequestration for this highly specialized herbivore. There is apparently ample opportunity for continued coevolution between monarchs and milkweeds, although the diffuse nature of the interaction, due to migration and interaction with multiple milkweeds, may limit the ability of monarchs to counteradapt.


Although coevolutionary interactions are often portrayed as simplified arms races of reciprocal defense and offense evolution, the dynamics are decidedly more complex. For example, how do plants respond to highly specialized herbivores, and are such adapted consumers immune to plant defenses? On average, specialists are less impacted by particular plant defense compounds than generalists (1, 2), but does this mean that further coevolution is not possible? Even highly specialized herbivores must contend with plant defenses if coevolutionary interactions are proceeding (3). For any herbivorous insect, larval feeding, protection from enemies, and adult oviposition are each key points in the life cycle where plant chemistry plays a role in the outcome. Thus, the typical cornucopia of chemical compounds in an individual plant presents opportunities for both plant resistance and co-option of this defense by specialist herbivores (46).

Thus, it is unclear how often coevolutionary interactions reach equilibrium or “stalemate,” as it were (7). Nonetheless, several conditions are predicted to slow or suppress the endless arms race. First, the more specialized an interaction, the greater the investments required and potential challenges to innovation. Second, when different life stages of herbivores are subject to distinct selection pressures (810), continued coevolution may be restricted because of conflicting selection. Finally, when aspects of the population biology of the species involved reduce local adaptation, such as gene flow and the presence of alternate hosts, asymmetry may emerge in the coevolutionary match between plants and herbivores (11, 12). In the interaction between milkweed plants and monarch butterflies, cardenolides have played a central role in our understanding of coevolutionary specialization, larval feeding, sequestration, and, to a lesser extent, oviposition (13). Although monarchs are abundant across a broad geographical range, substantial phenotypic and genetic analyses have failed to reveal population differentiation (14, 15). A lack of local adaptation is likely due to the four-generation annual cycle where butterflies feed on diverse milkweed species and yet intermix during migration and overwintering (13).

There is some evidence that cardenolides can be a burden for monarch caterpillars (1620), although costs of sequestration have not been demonstrated. Nonetheless, many assays, even across >10-fold concentrations of cardenolides, fail to show negative effects of cardenolides on monarchs (21). More mechanistic in vitro work with the monarch’s highly resistant sodium-potassium pump (Na+/K+-ATPase), the cellular target of cardenolides, demonstrated that some milkweed cardenolides are strong inhibitors of monarch neural physiology (22). Thus, work with specific compounds that are variable in plants is needed to pinpoint agents of resistance. For sequestration of cardenolides, a model proposed by Nelson (23) and supported in a review of early work (24) and new research (25) suggests that monarchs selectively sequester more polar cardenolides, some compounds are metabolized (modification or detoxification), and others are transported via carriers (20, 2628). Finally, observational work indicated that monarchs tend to oviposit on intermediate cardenolide concentration plants (29, 30), suggesting the hypothesis that adult butterflies minimize toxic exposure to larvae while optimizing sequestration of plant poisons.

Asclepias curassavica is surprisingly understudied in its interactions with monarch butterflies, despite being a critical hostplant worldwide (second only to Asclepias syriaca) (13). Attack of A. curassavica by monarchs can be strong and therefore a likely source of selection for plant defense. The species is weedy throughout the tropics and has a plethora of cardenolides, including relatively uncommon compounds, some of which may be detrimental to monarch performance (20, 28, 3134). In particular, voruscharin is a long-known cardenolide containing a thiazolidine heterocycle (having both nitrogen and sulfur; Fig. 1), yet its previous study was hampered by solubility issues and the inability of thin layer chromatography to separate it from related compounds (20, 28, 31, 35). In terms of sequestration, it was demonstrated decades ago that monarchs preferentially sequester two cardenolides, calotropin and calactin, especially when feeding on A. curassavica (20, 31, 33, 36). For oviposition, two flavonol glycosides were isolated from A. curassavica leaves that stimulate egg laying (37). Nonetheless, the relative importance of quercetin glycosides versus cardenolides in oviposition is unknown, and specific cardenolides that impact larval growth and sequestration have not been well-studied. If A. curassavica defends itself against this specialized herbivore in a coevolutionary interaction mediated by plant chemistry, connecting specific toxins to their target site in the context of sequestration and oviposition is critical. In particular, we hypothesized that specific cardenolides modulate a trade-off between benefits of specialization and costs of coping with toxicity.

Fig. 1.

Fig. 1.

Chemical conversion of milkweed cardenolides by monarch caterpillars. (A) A visualization of metabolomic data showing the differences in the chemical composition across sample groups (n = 4 per group; significance tested by PERMANOVA). After data curation, over 7,000 chemical features (m/z) were generated with MS data collected in positive ionization mode and visualized with a Bray–Curtis distance matrix. Ellipses represent the region of 95% confidence. (B) Voruscharin was converted to calactin and calotropin when fed to monarch caterpillars. Shown are means ± SE concentrations as determined by UV-HPLC (n = 3 to 9). Data bars very close to zero had no detectable cardenolides. Note that the caterpillars fed A. curassavica were reared on this diet from hatching and had an order of magnitude higher cardenolides than other treatments which were dosed only during the fourth instar. (C) The basic skeleton of cardenolides and the chemical structures of calactin, calotropin, and voruscharin.

Here, we identify cardenolides produced by A. curassavica and address which compounds are sequestered by monarchs, followed by asking four questions: 1) Do specific cardenolides reduce monarch larval growth, or does sequestration impose a burden for larvae? 2) Using in vivo and in vitro assays, do monarchs detoxify or convert particular cardenolides to less toxic forms? 3) What is the relative toxicity (measured as in vitro inhibition of the cellular target, the monarch’s Na+/K+-ATPase) of nonsequestered cardenolides, those sequestered intact, and those modified during sequestration? And, finally, 4) do monarch oviposition decisions minimize toxicity and optimize sequestration of cardenolides, or are oviposition stimulants (flavonol glycosides) drivers of oviposition?

Results

Plant Cardenolides, Sequestration, and Conversion.

Among the >200 A. curassavica plants grown in a common environment, the range of total leaf cardenolides varied eightfold (0.96 to 8.16 mg/g dry mass). Of the nine cardenolides quantified, one apolar compound, thiazolidine ring–containing voruscharin, identified by liquid chromatography coupled with high-resolution mass spectrometry (LC-HRMS/MS) was, on average, 40% of the total leaf cardenolides. Three other major peaks represented about 10% each of the total (two unidentified compounds at retention times 14.7 and 17.9 min and uscharin). Of the 36 pairwise phenotypic correlations between the nine cardenolides (n = 212), all but four were highly significant and positive, and the four exceptions all involved voruscharin (SI Appendix, Table S1). A principal component analysis (PCA) yielded two orthogonal PC axes, explaining 85% of the variation in the concentrations of the nine cardenolides, with PC1 having loadings of over 0.5 for all peaks except voruscharin, while voruscharin dominated PC2 (SI Appendix, Table S2). Thus, voruscharin production appears to be regulated somewhat independently from other A. curassavica cardenolides.

Monarch caterpillars were grown individually on these intact plants and were collected in their fourth instar, weighed, freeze-dried, and had their guts removed. Chemical analysis by ultraviolet (UV) and mass spectrometry (MS) detection revealed an absence of voruscharin from caterpillar bodies (Fig. 1A and SI Appendix, Figs. S1 and S2). Three compounds, frugoside, calotropin, and calactin, accounted for 77% of the total sequestered cardenolides (SI Appendix, Table S2). While frugoside occurred in both plant and insect tissues, calactin was very low in leaves, and calotropin, if present, was too low to quantify in leaves. The six other compounds sequestered were minor (each <6.5% of the total) and were not detected in the plant.

To test if monarchs convert voruscharin to calactin and calotropin, we purified voruscharin from A. curassavica, painted it on leaves of Asclepias tuberosa (a milkweed that is eaten by monarchs in nature but lacks cardenolides), and fed it to monarch caterpillars. In particular, we compared monarchs fed painted versus unpainted A. tuberosa, in addition to their frass and positive controls fed A. curassavica. First, an untargeted MS-based metabolomics analysis showed that the chemical compositions of the groups assessed by permutational multivariate analysis of variance (PERMANOVA) were different (P < 0.05), although not all pairwise comparisons were significant (Fig. 1A and SI Appendix, Table S3). Second, in parallel, cardenolide sequestration was assessed by measuring absolute concentrations based on UV detection (Fig. 1B) and the relative concentrations based on LC-HRMS detection (SI Appendix, Fig. S2). Voruscharin was only recovered on painted leaves and in small quantities in caterpillar frass. Monarchs fed control A. tuberosa leaves lacked cardenolides, and those fed painted leaves only contained calactin and calotropin. Finally, as expected, our positive control of monarchs fed A. curassavica foliage sequestered calactin and calotropin, in addition to several polar cardenolides, but lacked voruscharin.

To connect the dots of voruscharin synthesis and degradation, we hypothesized a biochemical model (SI Appendix, Fig. S3) and examined transformation dynamics of voruscharin in vivo and in vitro. In particular, we hypothesized that voruscharin first degrades to uscharidin, which is secondarily converted to calactin and calotropin. We detected low levels of uscharidin in monarchs on A. curassavica, but uscharidin was absent in monarchs fed A. tuberosa painted with voruscharin and was found in traces in their frass (SI Appendix, Fig. S4). To understand the degradation pathway, we conducted an assay in which pure voruscharin was subjected to different basic pH values and temperatures (SI Appendix, Fig. S5). Voruscharin is transformed to uscharidin under various alkaline conditions (pH 7 to 10), and the rate of conversion was enhanced at warmer temperatures (SI Appendix, Fig. S5).

The Burden of Cardenolide Consumption and Sequestration.

Although both plant cardenolide PC axes were associated with total plant cardenolide concentrations (SI Appendix, Table S2), only PC2 (as well as the single compound voruscharin) predicted total cardenolides sequestered by monarchs (PC1 F1,68 = 0.296, P = 0.588; PC2 F1,68 = 5.501, P = 0.022; voruscharin F1,68 = 10.107, P = 0.002; Fig. 2A). To address the relative importance of voruscharin (as a plant toxin) or sequestered cardenolides (as a burden, i.e., the combined effect of converting cardenolides and storing the preferred compounds), we used these two predictors in multiple regression to predict caterpillar growth (the two variables are only modestly correlated; r = 0.36, variance inflation factor = 1.15). Here, monarch growth was strongly negatively predicted by total sequestered cardenolides (R2 = 0.61) but not leaf voruscharin concentration (Fig. 2B; sequestered cardenolide F1,67 = 85.660, P < 0.001; voruscharin F1,67 = 1.254, P = 0.267; SI Appendix, Fig. S6). This analysis was robust to different configurations of using plant and sequestered cardenolides as predictors of monarch growth (i.e., using plant PC2 or total plant cardenolides and insect PC1 in multiple regressions; SI Appendix, Fig. S6).

Fig. 2.

Fig. 2.

Connections between plant cardenolides, monarch sequestration, and monarch growth. (A) Sequestration was predicted by the concentration of the dominant plant cardenolide, voruscharin, although this compound was itself not sequestered (it was converted to calactin and calotropin). (B) In multiple regression, sequestered cardenolides were predictive of monarch growth (whereas plant cardenolides were not), indicating a cost of converting or storing cardenolides. The weak relationships of growth predicted by total leaf cardenolides and leaf voruscharin are shown in SI Appendix, Fig. S6. Monarch image credit: Frances Fawcett.

To address the inhibitory capacity of different cardenolides on their physiological target, the monarch Na+/K+-ATPase, we isolated and purified frugoside (polar, sequestered intact), uscharin (apolar, 3-thiazoline ring–containing, minor leaf component, and not sequestered), voruscharin (apolar, thiazolidine ring–containing, dominant leaf component, and not sequestered), calotropin (intermediate polarity, minimal in the plant but sequestered), and calactin (intermediate polarity, minimal in the plant but sequestered) (SI Appendix, Figs. S7–S9). The inhibitory capacity of these compounds was referenced to two standards (ouabain and digitoxin) and all were compared on the sensitive porcine Na+/K+-ATPase versus the highly resistant enzyme isolated from monarch neural tissues. The two nonsequestered cardenolides were the most potent inhibitors of the monarch Na+/K+-ATPase and yet were among the least inhibitive of the sensitive porcine Na+/K+-ATPase (Fig. 3). In particular, the monarch’s Na+/K+-ATPase is typically 50 to 100 times more resistant to cardenolides than the porcine Na+/K+-ATPase (22, 38), and this was borne out by the average of 86-fold higher IC50 (concentration necessary to cause 50% inhibition) for five compounds tested, including three sequestered cardenolides and the two standards (Fig. 3 and SI Appendix, Table S4). Strikingly, for nonsequestered uscharin and voruscharin, the monarch was less than twofold more resistant than the sensitive Na+/K+-ATPase.

Fig. 3.

Fig. 3.

The difference in inhibitory impacts of isolated cardenolides on the highly sensitive porcine Na+/K+-ATPase versus the milkweed-adapted monarch butterfly Na+/K+-ATPase. Data are presented as the molar concentration of plant toxin necessary to cause 50% inhibition of the animal enzyme, or IC50, on the y-axis. Thus, higher values on the log scale y-axis indicate that the enzyme is more resistant to the cardenolide. The monarch Na+/K+-ATPase is substantially more resistant (it typically takes a higher concentration of the plant compounds to inhibit the enzyme). Sequestered+ indicates that these compounds are sequestered intact from consumed leaves as well as converted products from consumed voruscharin and uscharin. Each bar is a mean of three to nine replicates (each based on a six-concentration inhibition curve) ± SE (where not visible, SEs are too small). The arrow representing the polarity of cardenolides is based on elution through a C18 HPLC column (apolar stationary phase).

Monarch Oviposition.

When we tested free-flying monarchs for their oviposition preferences, egg laying was best predicted by intermediate concentrations of total leaf cardenolides and plant height (Fig. 4; Poisson general linear model: total cardenolides, l-R χ2 = 5.638, P = 0.018; total cardenolides squared l-R χ2 = 4.827, P = 0.028; and height l-R χ2 = 15.395, P < 0.001; alternative models including the significant predictive effect of cardenolide PC1 and individual compounds are given in SI Appendix, Table S5). Neither leaf voruscharin nor plant PC2 predicted oviposition. Because egg laying was also not predicted by foliar concentrations of two quercetin glycosides in leaf tissues (a quercetin-rhamno-di-hexoside and quercetin-rhamno-hexoside; SI Appendix, Table S6 and Fig. S10), we tested their stimulatory effect on oviposition by isolating and purifying the compounds. The latter compound was indeed found to be stimulatory in oviposition trials, but only at unrealistically high concentrations (SI Appendix, Table S6). Thus, overall, oviposition on whole plants was best predicted by plant height and the set of more polar cardenolides, which showed correlated expression, but neither the most potent cardenolides nor the low levels of quercetin glycosides in leaves.

Fig. 4.

Fig. 4.

Monarch oviposition was a quadratic function of total leaf cardenolides, with the highest number of eggs laid on intermediate cardenolide plants. Ten butterflies were released to freely oviposit in a large greenhouse common garden (n = 212 plants). Although raw data are shown, plant height was included and was significant in the statistical model. Zero egg values have been jittered. Monarch image credit: Frances Fawcett.

Discussion

It has long been conventional wisdom that specialist insect herbivores are less impacted by plant defensive chemistry than generalists; reciprocally, specialist pests that have been persistent over millions of years are potent forces of natural selection for specific plant defenses (1, 2). Nonetheless, as Berenbaum et al. (7) pointed out over 30 y ago, there is potential for stalemate in the metaphorical coevolutionary arms race, where herbivores and plants are well adapted to each other, with little room for further escalation. In the case of monarchs on milkweed, despite all the various barriers to feeding that milkweeds possess (trichomes, latex, and cardenolides), monarchs seem to prevail by shaving leaf trichomes and trenching latex canals as caterpillars, and by possessing a highly cardenolide-insensitive sodium-potassium pump (13).

Here, we have reported that the dominant cardenolide in one of the most important milkweed host plants for monarchs, the tropical milkweed A. curassavica, is the unusual thiazolidine ring–containing compound, voruscharin. The fact that most cardenolides lack nitrogen and sulfur and that nitrogen is typically limiting for plant growth, suggests that such compounds may be evolutionarily derived and highly potent (28). Although voruscharin has been known from A. curassavica and two other species in the Apocynaceae (Gomphocarpus fruticosus and Calotropis procera) for decades, and it was known not to be sequestered by monarchs, its potency, conversion, and impact on sequestration and oviposition were largely unknown (20, 28, 31, 33, 35). We have found that voruscharin is among the most potent milkweed cardenolides known to inhibit the monarch Na+/K+-ATPase (22), but it has rather poor inhibition of the highly sensitive porcine Na+/K+-ATPase, suggesting that this compound and its high expression in A. curassavica may function specifically against the monarch butterfly. In related work, we will show that natural populations of A. curassavica harbor substantial genetic variation in voruscharin production.

In perhaps the best-known system of plant–herbivore chemical coevolution, Berenbaum and colleagues (3) revealed how toxic furanocoumarins evolved in plants of the Apiaceae and the means by which lepidopteran herbivores detoxify these compounds. In particular, diverse cytochrome P450 enzymes in insects appear to have specifically evolved to detoxify the compounds. Among swallowtail butterflies, although linear furanocoumarins are metabolized easily, the biochemically novel angular furanocoumarins are much more challenging and have imposed selection to diversify cytochrome P450 enzymes. In the monarch–milkweed system, selective sequestration of more polar compounds is well known, but metabolic detoxification was thought to be far less important, partly because butterflies store cardenolides for their own defense (20, 24, 25). While some cardenolides, like frugoside, are stored intact, others, such as voruscharin, are converted to other forms. We found that the preferentially sequestered calactin and calotropin were less toxic to monarchs than voruscharin, but conversion or storage imposed a significant burden for caterpillars in terms of reduced growth rate that was stronger than direct effects of voruscharin itself. Ultimately, the benefits of sequestering calactin and calotropin may outweigh the costs we have described here. Recent research indicates substantial genetic variation in monarchs for sequestration (15), and our future work will address selection on this ability.

It is interesting to note that the basic conditions which mimic the pH of the monarch gut hydrolyze voruscharin or uscharin to uscharidin. Our data support this as the first step in the hypothesized pathway to derive calactin and calotropin (SI Appendix, Fig. S5). Acid hydrolysis of the 3-thiazoline ring has also been reported for the conversion of uscharin into uscharidin (28), and the enzymatic reduction of uscharidin to calactin and calotropin was demonstrated in vivo using monarch gut homogenates (20, 27). Perhaps it seems odd that a novel and highly potent chemical defense produced by Asclepias is degraded passively in the monarch gut. One possible explanation for this observation is that the degradation is not immediate, and the further enzymatic modification is costly. Depending on the hydrolysis rate and temperature in the gut, all of the voruscharin may not be converted to uscharidin, potentially imposing a cost for monarchs. Spontaneous and environment-dependent degradation of plant defense compounds is not unique to cardenolides and has been shown to have various effects in other systems (3941).

Given the high-chemical diversity of hundreds of distinct cardenolides in Asclepias (42), it is puzzling that very few cardenolides containing a 3-thiazoline or 3-thiazolidine ring have been found (e.g., uscharin, voruscharin, and labriformin) (28, 43). So far, these have been found in some of the major host plants of monarchs, as labriformin occurs in A. syriaca (44), but the evolutionary history of these compounds and why they are not more common is thus far unclear. Although the biosynthesis of cardenolides in Asclepias has been little studied (45), and the pathway leading to voruscharin in particular is unknown, we speculated that formation of the thiazolidine ring likely involves the condensation of cysteine with the carbonyl group in position 3′ of uscharidin (SI Appendix, Fig. S3). Regardless of the specific biosynthetic origin, our analysis of correlations among cardenolides (SI Appendix, Table S1) suggests the biosynthetic steps involved in the thiazolidine ring formation may be regulated independently from the pathways that produce the bulk of other A. curassavica cardenolides.

There has been a lack of clarity on the relative importance of flavonoid oviposition stimulants (quercetin glycosides) and cardenolides (which do not occur on the surface of milkweed leaves) for egg laying. On the one hand, monarchs tend to oviposit on intermediate cardenolide concentration plants (29, 30); yet, on the other hand, there does not appear to be a consistent relationship between cardenolides and quercetin glycosides (46, 47). In the current study, although we were able to show that an isolated quercetin-rhamno-hexoside was indeed stimulatory for oviposition, quantitative variation in quercetin glycosides measured in leaves did not predict egg laying in our trials. We speculate that quercetin glycosides, although stimulatory in isolation, occur in much too low concentrations to be drivers of egg laying. Nonetheless, we did find that monarchs laid the most eggs on intermediate cardenolide plants, as expected based on past observations. Our plants were not flowering during the oviposition trial, so nectar was not a potential cue, although other research indicates that nectar cardenolides impact monarch oviposition (48).

Finally, although we do not know how monarchs sense leaf cardenolides (or what correlated traits they detect), monarchs’ preference for intermediate cardenolide plants supports the notion that specialist herbivores must balance the benefits of plant secondary compounds for sequestration with the burden that these same compounds impose. Thus, perhaps there is room for additional coevolution between these highly adapted herbivores and their toxic host plants. One challenge for monarchs is that there is relatively little evidence of local population differentiation or adaptation to particular host plants (14, 15). This is likely the outcome of their complex annual migratory cycle, where butterflies encounter diverse milkweeds, and yet geographically distinct breeding populations intermix during migration and overwintering. Thus, although monarchs themselves are specialists on a genus of plants, that genus contains chemically diverse cardenolide toxins for which there may not be a single insect counter ploy (28, 49). In fact, recent work has also shown that alternative defenses may result in some plants being ecological traps where monarch oviposition is followed by poor caterpillar performance (9, 50). We conclude by speculating that although monarchs are highly adapted to Asclepias spp., overall, they may not be able to strongly adapt to any one plant species. The ratio of cardenolide sequestration by monarchs to host plant cardenolides is the highest for A. syriaca and A. curassavica (24), suggesting that coevolution may be primarily occurring between monarchs and these two species, and strong selection by monarchs on particularly important host plant species (e.g., A. syriaca and A. curassavica) may stimulate adaptation in these plant species. Thus, coevolution in this system is decidedly diffuse. The geographical availability of multiple milkweed species is a buffet for monarchs, but perhaps also a limitation preventing stronger specialized insect adaptation.

Materials and Methods

Plant Growth.

In April 2016, we germinated a diverse pool of Asclepias curassavica seeds collected from several sites in the southern United States and Mexico, and obtained from commercial seed suppliers. Our goal was to have diversity within the species, and there was substantial phenotypic variation among collections (e.g., in flower color and leaf shape), but all were confirmed to be A. curassavica based on flowers. In total, we grew approximately 10 plants from each of the 22 collections. Plants were grown as described in Rasmann and Agrawal (49), with surface-sterilized seeds that were nicked, stratified at 4 °C for 4 d, germinated in Petri dishes at 28 °C, and grown in potting soil (Metro-Mix, Sun Gro Horticulture) in plastic pots (500 mL) in a high-light growth chamber (at least 350 microeinsteins, 16 h daylight, 26 °C day, and 22 °C night). Plants were given two applications of dilute fertilizer (N:P:K 21:5:20; 150 ppm N [microgram/gram]) over 1 mo of growth, after which they were clipped to just above the cotyledons. Clipped leaf tissue was freeze-dried and analyzed for cardenolides by high-performance liquid chromatography (HPLC, see below in Cardenolide and Flavonol Quantification). Plants were up-potted and moved to a rooftop greenhouse at Cornell University. A total of 212 A. curassavica plants regrew in the greenhouse.

Initial Insect Bioassays.

Two assays were conducted. In the first, adult oviposition was assessed by releasing 10 mated female monarchs (from a laboratory colony) into the 56 m2 greenhouse. After 24 h, over one-third of the plants had at least one egg laid on them and the trial was ended. Plant height was measured, eggs were removed from plants with tweezers, and the second assay was initiated to assess caterpillar growth. Neonate monarch caterpillars were introduced to 70 of the plants, and growth rate was measured as fresh mass 8 d later when the caterpillars had entered the fourth instar (when monarchs typically begin to move between plants). Caterpillars were freeze-dried, their guts were removed by dissection under a microscope, and the rest of the body was used to assess cardenolide sequestration. We then estimated the total cardenolides sequestered by HPLC (see below in Cardenolide and Flavonol Quantification). This design allowed us to connect individual variation in plant chemistry, caterpillar growth, and sequestration.

Cardenolides and Flavonols: Isolation and Identification.

We authenticated chemical structures using a set of authentic standards from Zhang et al. (32) and Petschenka et al. (22) and matched retention times, MS exact masses (HRMS), and MS fragmentation profiles for frugoside, asclepin, calactin, and calotropin in samples, and purified compounds voruscharin, uscharin, quercetin-rhamno-hexoside, and quercetin-rhamno-di-hexoside. HRMS/MS data of voruscharin, uscharidin, calactin, and calotropin are detailed in SI Appendix, Table S7, and their respective MS2 can be found in SI Appendix, Figs. S7–S9. SI Appendix, Figs. S10 and S11 give the HRMS/MS data for the quercetin glycosides.

Frugoside, calactin, and calotropin were purified from the bioassay monarch caterpillars raised on A. curassavica (3.1 g dry tissue). The pooled extract was defatted with 50 mL hexane and taken to dryness. The remaining residue was suspended in 9 mL 16% acetonitrile and water, sonicated for 30 s, vortexed, centrifuged at 20,800 × g for 12 min, and treated by adding 24 uL 40% lead acetate. This step clears the sample of pigments and other interfering compounds. The vial was then lightly vortexed and allowed to sit for a minimum of 10 min to allow unwanted compounds to complex. The vial was then centrifuged at 20,800 × g for 12 min and the supernatant transferred to a new vial. To bind up any remaining lead ions, we added an addition of 1,200 uL 5% sodium sulfate. After a 10 min wait, the vial was again centrifuged at 20,800 × g for 12 min and the supernatants transferred to a new vial. The vial was then taken to dryness and the residue resuspended in 9 mL of methanol by sonication and vortexing. The vial was then centrifuged at 20,800 × g for 12 min and the supernatant transferred to a new vial. The methanolic supernatant was transferred to a new vial and taken to dryness. We then added 16% acetonitrile to water, and the residue was resuspended by sonication and vortexing. The sample was again centrifuged at 20,800 × g for 12 min and the supernatant saved for preparative HPLC fractionation. Uscharin and voruscharin were purified from >40 mL fresh A. curassavica latex collected from greenhouse-grown plants.

All prepared samples were injected into an Agilent 1260 series preparative LC system with an Agilent 21.2 mm × 150 mm, C-18, 5 um column. Each first-pass injection was eluted at a constant flow rate of 14.87 mL/min with a gradient of acetonitrile and water as follows: 0 to 2 min at 16% acetonitrile; 2 to 25 min from 16 to 70%; 25 to 30 min from 70 to 95%; and 30 to 35 min at 95%. Target peaks were detected at 218 nm. In most cases, each first-pass target fraction needed to be dried down, resuspended in 16% acetonitrile, and reinjected for further cleanup. Fractions needing reinjection often required modifications to the Method gradients to increase column retention times to help isolate target peaks. The isolated fractions were pooled, dried, and resuspended in 0.5 mL 100% methanol and then analyzed on a Thermo Scientific QExactiveTM hybrid quadrupole-orbitrap LC-MS system in positive ionization mode. Compounds were identified by their exact parental mass ([M+H]+) as well as the corresponding sodium adduct ([M+Na]+).

Reversed-phase chromatography was performed using a Dionex 3000 LC coupled to an Orbitrap Q-Exactive mass spectrometer controlled by Xcalibur software (ThermoFisher Scientific). Methanolic extracts were separated on an Agilent Zorbax Eclipse XDB-C18 column (150 mm × 2.1 mm; particle size: 1.8 µm), maintained at 40 °C with a flow rate of 0.5 mL/min. Solvent A contained 0.1% formic acid in water; solvent B contained 0.1% formic acid in acetonitrile. A/B gradient started at 5% B for 2 min after injection and increased linearly to 98% B at 11 min, followed by 3 min at 98% B, then back to 5% B over 0.1 min, and finally at 5% B held for an additional 2.9 min to re-equilibrate the column. Mass spectrometer parameters were as follows: spray voltage, −3.0 kV, +3.5 kV; capillary temperature, 380 °C; probe heater temperature, 400 °C; and sheath, auxiliary, and sweep gas, 60, 20, and 2 arbitrary units, respectively. S-Lens radio frequency level was 50, and resolution was 240,000 at m/z 200; the automatic gain control (AGC) target was 3E6. Each sample was analyzed in negative and positive electrospray ionization modes with m/z ranges from 70 to 1,000 for reversed-phase, 120 to 800 for reversed-phase postcolumn ion pairing, and 70 to 700 for normal phase. Parameters for MS/MS (dd-MS2) were as follows: MS1 resolution, 60,000; and AGC target, 1E6. MS2 resolution was 30,000; AGC target was 2E5; maximum injection time was 50 ms; isolation window was 1.0 m/z, stepped normalized collision energy was 10, 30; and dynamic exclusion was 1.5 s, with the top five masses selected for MS/MS per scan. LC-MS data were analyzed using MZmine software and MS2 spectra were obtained via Excalibur software (ThermoFisher Scientific).

Cardenolide and Flavonol Quantification.

We used an Agilent 1100 HPLC with diode array detector and a Gemini C18 reversed-phase, 3 μm, 150 mm × 4.6 mm column. We use 50 mg pulverized tissue for analyses by adding 1.5 mL 100% methanol, a 20 μg digitoxin spike as internal standard, and 20 FastPrep beads. Cardenolides were then extracted by agitating twice on a FastPrep-24 homogenizer for 45 s at 6.5 m/s and then centrifuged at 20,800 × g for 12 min. Supernatants were dried down in a vacuum concentrator at 35 °C, resuspended in 200 μL methanol, and filtered using 0.45 μm hydrophilic membranes, and 15 μL was injected into the HPLC running a constant flow of 0.7 mL/min with a gradient of acetonitrile and water as follows: 0 to 2 min at 16% acetonitrile; 2 to 25 min from 16 to 70%; 25 to 30 min from 70 to 95%; and 30 to 35 min at 95%, followed by 10 min reconditioning at 16% acetonitrile. Peaks were recorded at 218 nm, and absorbance spectra are recorded between 200 and 300 nm. Peaks showing a characteristic single absorption maximum between 214 and 222 nm correspond to the unsaturated lactone indicative of cardenolides. Concentrations were standardized by peak area to the digitoxin internal standard with known concentration. Flavonols were similarly quantified from the same chromatograms based on our digitoxin internal standard.

Voruscharin Painting Experiment.

We modeled our analysis of the fate of purified cardenolides based on Seiber et al. (20). We used monarchs from a laboratory colony (reared for four generations from wild collected individuals) and reared a cohort on A. tuberosa. A. tuberosa is milkweed that lacks detectable cardenolides and has the lowest inhibition of the porcine sodium-potassium pump of any milkweed species assayed to date (51). When caterpillars newly molted to the fourth instar, we kept them cool and without food until use (<5 h). Our main treatments were A. tuberosa leaves (controls treated with methanol, n = 5) and leaves dosed with realistic amounts of voruscharin (n = 4). Briefly, because voruscharin was estimated to be 40% of total cardenolides in A. curassavica and totals an average of 1.7 μg/mg dry mass, we added 7 μg voruscharin (dissolved in methanol) per square centimeter of A. tuberosa foliage. Individual caterpillars were provided two leaves at a time in Petri dishes lined with filter paper. After molting into fifth instar, they were deprived of food for 8 h and freeze-dried for analysis. Two caterpillars were simultaneously reared on A. curassavica from hatching to the fifth instar. In addition to these positive controls, we analyzed samples from methanol-treated A. tuberosa leaves, A. tuberosa leaves spiked with voruscharin, caterpillars fed each of these diets, and the frass from caterpillars fed the voruscharin diet.

Oviposition Experiments.

We modeled oviposition trials with isolated quercetin glycosides on Haribal and Renwick (37). Briefly, cubes of washed green sponges were arranged on a four-arm stand inside of a collapsible field cage (Bioquip, 0.23 m3). Each trial consisted of two control arms (sponge with water) and one sponge each of the two isolated quercetin glycosides (1 g leaf equivalents); at least four female (all mated) and one male butterflies were included in each of the 10 trials. Butterflies were allowed to lay eggs for a maximum of 5 h (daylight hours). All eggs were counted on sponges for analysis.

Data Preprocessing and Metabolomics Analysis.

The acquired LC-MS data files were converted to mzXML files using the ProteoWizard MSconvert tool. LC-MS data were then preprocessed with the open-source MZmine software and consisted of peak detection, removal of isotopes, alignment, filtering, and peak filling. Peak detection was performed in three steps: 1) mass detection with noise value = 15,000; 2) automated data analysis pipeline (ADAP) chromatogram builder with minimum group size in number of scan = 5, group intensity threshold = 25,000, minimum height = 30,000, and m/z tolerance = 10 ppm; and 3) wavelets ADAP deconvolution with S/N = 3, minimum feature height = 1,000, coefficient area threshold = 5, peak duration range = 0.01 to 3 min, and retention time wavelet range = 0.01 to 0.04 min. Isotopes were removed using the isotopic peak grouper with m/z tolerance = 10 ppm, retention time tolerance = 0.5 min, and maximum charge = 3. Chromatograms were aligned using the join aligner with m/z tolerance = 10 ppm, weight for m/z = 75%, retention time tolerance = 0.5 min, and weight for retention time = 25%. The filtering minimum peak in a row = 2, minimum peak in an isotopic pattern = 2, and keep only peaks with MS2 scan. Gap filling was applied using the method peak finder with retention time correction with intensity tolerance = 10%, m/z tolerance = 10 ppm, and retention time tolerance = 0.5 min. Quality control metabolites with a coefficient of variation greater than 30% were removed from the whole data matrix. In positive mode ionization, the data matrices contain 7,252 and 6,795 features in mass range of 152 to 1,185 m/z and 156 to 1,155 m/z, respectively.

Sodium-Potassium Pump Assays.

We quantified the biological activity of isolated cardenolides using Na+/K+-ATPase from the porcine cerebral cortex (Sigma-Aldrich) and monarch butterflies following the methods of Petschenka et al. (22). Briefly, Na+/K+-ATPase activity was measured as the amount of inorganic phosphate (Pi) enzymatically released from ATP in the presence of K+ (Na+/K+-ATPase active) minus the amount of Pi released in the absence of K+ (Na+/K+-ATPase inactive). Each compound was dissolved fully in methanol (frugoside, calactin, and calotropin) or acetonitrile (voruscharin and uscharin, due to solubility), assayed by HPLC to determine concentration, and then dried and resuspended in 20% dimethyl sulfoxide (DMSO) to a concentration of either 0.5 mM (frugoside, calactin, and calotropin) or 0.1 mM (voruscharin and uscharin, due to decreased solubility). We then prepared five serial dilutions to reach the concentrations 5 × 10−5 M, 5 × 10−6 M, 5 × 10−7 M, 5 × 10−8 M, and 5 × 10−9 M to produce a six-point inhibition curve for each compound, incubated with each of the two enzyme preparations. These milkweed cardenolides were run alongside equivalent solutions of ouabain and digitoxin in 20% DMSO. Reactions were performed in 96-well microplates on a BioShake Iq microplate shaker (Quantifoil Instruments) at 200 rpm and 37 °C. Absorbance values of reactions were corrected by their respective backgrounds, and dose–response curves were fitted using a nonlinear mixed effects model with a four-parameter logistic function in the statistical software R (function nlme with SSfpl in package nlme v3.1 to 137) based on ref. 52. We focus analyses on the dilution value IC50, at which the enzyme is inhibited by 50%.

Statistical Approaches.

Linear statistical models (regression and ANOVA) were usable for most analyses, and residuals were checked for normality and heteroscedasticity. Except as noted below, all analyses were conducted in JMP Pro V14. As noted in the text, we quantified nine abundant cardenolides in the leaf tissue of A. curassavica and nine sequestered cardenolides in monarchs (which overlapped but were not identical to those in plants). As shown in the results, the concentrations of many, but not all, of the distinct cardenolides were highly correlated across individual plants. Thus, we first used PCA to reduce the number of variables in each set and used the two PCs (eigenvalues >1) in statistical analyses (mostly regressions to explain response variables like egg number, larval mass, and sequestration). Next, to confirm a role (or lack thereof) for particular cardenolides that were strongly (or weakly) loaded on particular PC axes, we followed up with analyses using the individual compounds.

Metabolomic analyses were performed using the web-based metabolomics data processing tool, MetaboAnalyst 3.0 (https://www.metaboanalyst.ca/). Briefly, data were filtered using a nonparametric relative SD (median absolute deviation/medium), normalized by sum, log transformed, and auto scaled. The metabolomes of each group of samples were analyzed with a Bray–Curtis distance matrix on normalized chemical data and visualized using principal coordinate analyses. Statistical tests were conducted using PERMANOVA.

We used a Poisson regression to predict egg count data, which ranged from zero to six eggs per plant; a squared term was include in the model, both because past work (29, 30) and the current results fit a quadratic model.

Supplementary Material

Supplementary File
Supplementary File
pnas.2024463118.sd01.xlsx (76.5KB, xlsx)

Acknowledgments

We thank Bennett Fox and Frank Schroeder for unfailing assistance with the MS at the Boyce Thompson Institute, as well as Nicolas Baert for MS analyses of quercetin glycosides at the Cornell Chemical Ecology Core Facility. Chelsea Lee and Steven Broyles helped with latex collection. The manuscript was improved by comments from two anonymous reviewers, Nathaniel Carlson, Tyler Coverdale, Arielle Johnson, Xosé López-Goldar, Jennifer Thaler, and Shirley Zhang. This research was supported by a grant from the NSF to A.A.A. (IOS-1907491).

Footnotes

The authors declare no competing interest.

This article is a PNAS Direct Submission.

This article contains supporting information online at https://www.pnas.org/lookup/suppl/doi:10.1073/pnas.2024463118/-/DCSupplemental.

Data Availability

All study data are included in the article and/or SI Appendix.

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Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

Supplementary File
Supplementary File
pnas.2024463118.sd01.xlsx (76.5KB, xlsx)

Data Availability Statement

All study data are included in the article and/or SI Appendix.


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