Species that sequester toxins from prey for their own defense against predators may exhibit population-level variation in their chemical arsenal that reflects the availability of chemically defended prey in their habitat. Rhabdophis tigrinus is an Asian snake that possesses defensive glands in the skin of its neck (‘nuchal glands’), which typically contain toxic bufadienolide steroids that the snakes sequester from consumed toads. In this study, we compared the chemistry of the nuchal gland fluid of R. tigrinus from toad-rich and toad-free islands in Japan and determined the effect of diet on the nuchal gland constituents. Our findings demonstrate that captive-hatched juveniles from toad-rich Ishima Island that had not been fed toads possess defensive bufadienolides in their nuchal glands, presumably due to maternal provisioning of these sequestered compounds. Wild-caught juveniles from Ishima possess large quantities of bufadienolides, which could result from a combination of maternal provisioning and sequestration of these defensive compounds from consumed toads. Interestingly, juvenile females from Ishima possess larger quantities of bufadienolides than do juvenile males, whereas a small sample of field-collected snakes suggests that adult males contain larger quantities of bufadienolides than do adult females. Captive-born hatchlings from Kinkasan Island lack bufadienolides in their nuchal glands, reflecting the absence of toads on that island, but they can sequester bufadienolides by feeding on toads (Bufo japonicus) in captivity. The presence of large quantities of bufadienolides in the nuchal glands of R. tigrinus from Ishima may reduce the risk of predation by providing an effective chemical defense, whereas snakes on Kinkasan may experience increased predation due to the lack of defensive compounds in their nuchal glands.
Animals that rely on chemicals for antipredator defense may synthesize those compounds from nontoxic precursors (Daly, 1995; Eisner, Eisner & Siegler, 2005) or sequester defensive toxins from other organisms (González, Hare & Eisner, 1999; Nishida, 2002; Dumbacher et al., 2004; Williams, Brodie Jr & Brodie III, 2004; Opitz & Müller, 2009; Saporito et al., 2012; Savitzky et al., 2012). Animals capable of synthesizing their own toxins would not be expected to differ geographically in levels of chemical defense unless there was genetic variation among populations in the ability to synthesize toxins or geographic variation in their suite of predators (Thompson, 2005). However, geographic variation in chemical defense would be more likely to exist among animals dependent on prey for sequestered chemical defenses if critical prey species are distributed unevenly or have geographically variable toxicity (Hanifin et al., 1999; Thompson, 2005).
Rhabdophis tigrinus is an oviparous Asian snake (Colubridae: Natricinae) that possesses unusual defensive glands on the neck known as nuchal glands (Fig. 1; Nakamura, 1935; Smith, 1938; Mori et al., 2012). The contents of the nuchal glands have been shown to contain toxic bufadienolides (Akizawa et al., 1985a,b), which irritate mucous membranes and cause corneal injuries (Kawashima, 1959; Suzuki, 1960; Asahi et al., 1985). Bufadienolides are cardiotonic steroids, similar to cardiac glycosides in foxglove plants (Digitalis), that act by inhibiting the sodium–potassium pump, causing arrhythmia and cardiac failure in high doses (Melero, Medarde & San Feliciano, 2000). The bufadienolides in the nuchal glands of R. tigrinus are similar to those found in the skin secretions of toads (Bufonidae; Erspamer, 1994), which are often consumed by R. tigrinus (Mori & Moriguchi, 1988). Although toads are capable of synthesizing their defensive bufadienolides from cholesterol (Siperstein, Murray & Titus, 1957; Porto, Baralle & Gros, 1972), R. tigrinus is dependent on dietary toads from which it can sequester these compounds for storage in the nuchal glands (Hutchinson et al., 2007). Bufadienolides sequestered from toads can be provisioned by female R. tigrinus to offspring in utero by deposition of those compounds in yolk and by transfer to oviducal eggs during gestation (Hutchinson et al., 2008, 2012).
The majority of reported natural predators of R. tigrinus are birds, but fish, giant salamanders, raccoon dogs (Nyctereutes) and other snakes also have been reported to prey on this species (Tanaka & Mori, 2000). Field observations of encounters between R. tigrinus and its predators are lacking, but presumably, contact between the irritating nuchal gland fluid and the eyes or mouth of a bird or mammal serves as an effective deterrent (Asahi et al., 1985; Mori et al., 2012). Rhabdophis tigrinus has been shown in laboratory experiments to exhibit specific defensive behaviors that orient the nuchal glands toward a perceived threat (Mori & Burghardt, 2001), demonstrating the defensive function of the nuchal glands.
Rhabdophis tigrinus primarily consumes anurans (frogs), including the Japanese toad Bufo japonicus (Fukada, 1959; Moriguchi, 1982; Mori & Moriguchi, 1988). Unfed hatchlings of R. tigrinus are at least twice as likely to feed on toads or nonbufonid frogs than fish, demonstrating an innate preference for anurans (Mori et al., 2012). However, toads are not entirely sympatric with R. tigrinus, so some populations of snakes lack access to toads as prey. Within Japan, R. tigrinus occurs on the main islands of Honshu, Shikoku and Kyushu, as well as some of the smaller Japanese islands (Nakamura & Uéno, 1963; Toriba & Sawai, 1990; Takeuchi et al., 2012).
In this study, we analyzed the chemistry of the nuchal gland fluid of R. tigrinus from two small Japanese islands: Ishima (Tokushima Prefecture), where toads are abundant, and Kinkasan (Miyagi Prefecture), where toads are absent (Fig. 2). Ishima supports dense populations of anurans, including B. japonicus (Bufonidae), Hyla japonica (Hylidae), Glandirana rugosa (formerly Rana rugosa; Ranidae) and Pelophylax nigromaculatus (formerly Rana nigromaculata; Ranidae). In contrast, the only frog present on Kinkasan is the nonbufonid Rana tagoi (Ranidae; Nagata & Mori, 2003).
Our primary aim for this study was to compare the bufadienolide content of R. tigrinus from Kinkasan and Ishima. Substantial differences would presumably reflect disparities in defensive efficacy of the nuchal glands between these populations. Furthermore, we aimed to establish experimentally the effects of diet on the defensive chemistry of R. tigrinus from these two islands.
Experimental design and sample collection
For the feeding study, 12 gravid female R. tigrinus were collected on Kinkasan Island (38°17.7′N, 141°34.0′E) and Ishima Island (33°50.9′N, 134°48.8′E), six from each location. They were transported to Kyoto University, where they were fed only fish and nonbufonid frogs that lack bufadienolides (P. nigromaculatus). Following oviposition, the eggs were incubated between 25 and 30°C. The hatchlings were reared on controlled diets of either exclusively nonbufonid prey or a combination of toads and nonbufonid prey. The nonbufonid prey items consisted primarily of fish (Oryzias latipes; Adrianichthyidae) and frogs (H. japonica); salamanders (Hynobius tokyoensis and Hynobius lichenatus; Hynobiidae) were used as supplemental food for individuals that lived longer than 6 months. The toads used as prey were metamorphic (newly metamorphosed) B. japonicus from Niijima Island, Tokyo Prefecture. Most hatchling snakes were sacrificed after 7–9 months and frozen for later collection and analysis of nuchal gland fluid.
For chemical analyses, samples of metamorphic toads and nuchal gland fluid of snakes were prepared. Two frozen metamorphic toads (0.12 g each) were cut into pieces and extracted individually in methanol for chemical analyses. From each previously frozen snake, we expressed all nuchal glands onto a portion of Kimwipe (Kimwipes Wipers S-200; Kimberly-Clark, Dallas, TX, USA) while wearing nitrile, polyethylene or latex gloves; each Kimwipe was then placed into a vial of methanol with forceps and covered with a Teflon-lined cap. The forceps were rinsed in methanol from a glass pipette and were dried with a Kimwipe between each individual; gloves were also changed between individuals. At least one control vial consisting of a Kimwipe in methanol was prepared at the end of each sampling session to test for cross-contamination between samples. At least six hatchlings from each of 12 clutches were sampled for a total of 51 hatchlings from Ishima (age 5–280 days) and 48 hatchlings from Kinkasan (age 9–223 days). All samples were stored at −20°C.
To determine quantities of bufadienolides in wild-caught R. tigrinus, we collected nuchal gland fluid from individuals on toad-free Kinkasan Island and toad-rich Ishima Island. We sampled six wild-caught adults (two females and four males) from Ishima in summer and early fall and six wild-caught adults (three females and three males) from Kinkasan in summer. Additionally, we analyzed nuchal gland fluid from 20 wild-caught juveniles (10 females and 10 males) that were sampled on Ishima in September. The juveniles ranged in snout–vent length (SVL) from 166 to 292 mm, suggesting that they had hatched that year (Fukada, 1992). The majority of these animals were captured, sampled and released; those that were taken into captivity were sampled prior to feeding or were fed only nonbufonid prey. A partial sample of nuchal gland fluid was collected from four of the six adults from Kinkasan (some nuchal glands were left intact) so the animals could be used for subsequent studies; we have preliminary evidence to suggest that nuchal glands do not regenerate after use (A. H. Savitzky & A. Mori, pers. obs.).
To assess the chemical profiles of some of the prey available to R. tigrinus on Ishima and Kinkasan, we sampled parotoid gland secretion from toads (B. japonicus) on Ishima and skin secretion from R. tagoi on Kinkasan. The parotoid glands of toads can be squeezed to collect bufadienolide-rich secretions on Kimwipes, but Rana spp. lack parotoid glands. Therefore, we used a transcutaneous amphibian stimulator (Grant & Land, 2002) to collect skin secretions from R. tagoi. The frogs were stimulated and then sections of Kimwipes were rubbed over their backs and submerged in individual vials of methanol. Our animal use protocols conformed to institutional policies and practices.
Methanolic extracts of prey species and nuchal gland fluid from snakes were evaporated to dryness, reconstituted and analyzed by proton nuclear magnetic resonance (1H-NMR) spectroscopy and/or high-performance liquid chromatography (HPLC). The whole-body extracts of two metamorphic B. japonicus from Niijima Island (the population used in the feeding experiment), as well as parotoid gland secretion from adult toads on Ishima, were prepared and analyzed by nuclear magnetic resonance (NMR) spectroscopy and HPLC. The presence or absence of bufadienolides was determined by analyzing unfractionated samples on Unity INOVA 400-, 500-, or 600-MHz NMR spectrometers (Varian, Palo Alto, CA, USA) equipped with Oxford magnets (Oxford Instruments, Eynsham, Witney, Oxon, UK) and 5-mm inverse-detection hydrogen, carbon and nitrogen (HCN) or dual broadband gradient (DBG) probes.
To obtain quantitative data, we analyzed nuchal gland fluid from 99 hatchlings in the feeding experiment, as well as 20 wild-caught juveniles and 6 wild-caught adult R. tigrinus from Ishima. The samples were reconstituted in known volumes of methanol (typically 0.3 mL for samples with small quantities of bufadienolides or no bufadienolides, and 1.5–4.2 mL for concentrated samples) for analysis with HPLC. Most samples were analyzed with an Agilent (Santa Clara, CA, USA) 1100 series HPLC equipped with a quaternary pump, diode array detector and automated sampler. A reversed-phase 250 × 10 mm Supelco (Bellefonte, PA, USA) Discovery® HS C18 column was used for most samples (3.4 mL min−1 and 25 μL injection volume), but several samples were analyzed with a Varian Pursuit XRs 3 μm 250 × 4.6 mm C18 column at 0.75 mL min−1 (5 or 10 μL injection volume). A solvent gradient using a mixture of methanol and water was used. The methanol was held at 20% (v/v) for 2 min and then increased linearly over 38 min to 100%. After 2 min at 100% methanol, the mixture was returned to 20:80 methanol:water.
Several samples were analyzed using a Waters 2790 HPLC (Waters Corporation, Milford, MA, USA) with an internal microtiter plate autosampler and Waters 2487 dual wavelength detector set to 225 and 300 nm, which approximate the absorbance maxima of bufadienolides. We used a Dionex Acclaim 120 C18 5 μm 4.6 × 150 mm column (Thermo Scientific, Sunnyvale, CA, USA) with a flow rate of 1 mL min−1 with this HPLC.
To calculate the total quantity of bufadienolides present in each sample, we calibrated the HPLC using a series of dilutions of telocinobufagin (T. Spande and J. W. Daly) and cinobufotalin (Sigma C1147-10 mg; Sigma-Aldrich, St. Louis, MO, USA). The equations obtained from the linear trend lines fitted to the dilution curves were used to convert the cumulative area in mAU⋅s (milliabsorbance units⋅seconds) of bufadienolide peaks at 280 nm into milligrams of bufadienolides. Peaks produced by bufadienolides were identified by their characteristic UV-absorbance spectra, and only those peaks with areas greater than 15.0 mAU⋅s were used to calculate the total quantity of bufadienolides in each sample.
To identify individual bufadienolides, we compared chromatograms of the samples to those from standards containing 17 previously identified compounds from a related feeding experiment (electronic supplementary material, Supporting Information Fig. S1b; Hutchinson et al., 2007). The standards were reanalyzed with HPLC to determine any changes in retention time before comparing the two sets of data. Of the 17 bufadienolides we have identified in R. tigrinus, compounds 6 and 7 coelute, so they could not be distinguished from one another using HPLC. The software used to analyze the chromatograms was ChemStation for LC3D Rev. A.09.01 (Agilent).
To determine the effect of the total mass of toads consumed on the quantity of bufadienolides in nuchal gland fluid, we calculated Spearman's rank correlation coefficients for hatchling R. tigrinus from Kinkasan and Ishima. We used SPSS version 11.0 (Chicago, IL, USA) for statistical analyses and plotted data using SigmaPlot version 9.0 (SYSTAT, San Jose, CA, USA).
We conducted an analysis of covariance (ANCOVA) to test for the effect of sex on the quantity of bufadienolides in 20 wild-caught, juvenile R. tigrinus from Ishima. We used sex as the fixed factor and mass and SVL as covariates. To test for the homogeneity of slopes, we ran a preliminary ANCOVA including interaction terms of sex⋅mass and sex⋅SVL. Both interaction terms were nonsignificant (sex⋅mass P = 0.361; sex⋅SVL P = 0.273), so the interaction terms were removed and the ANCOVA was rerun without them (Engqvist, 2005). The assumption of equality of variances was met (Levene's test, P = 0.435), as was the assumption of normality (Shapiro–Wilk test, P = 0.674 for females, P = 0.425 for males).
Adult and metamorphic toads (B. japonicus) possessed bufadienolides (Fig. 3a,b), whereas the skin secretion of R. tagoi lacked those compounds. Whole-body extracts of metamorphic B. japonicus, which were fed to the hatchling R. tigrinus in the experimental group, contained small quantities of bufadienolides, as confirmed by NMR spectroscopy and HPLC (Fig. 3a). In a pooled sample of two whole-body extracts of metamorphic toads, each of which weighed 0.12 g, the approximate total quantity of bufadienolides was 0.02 mg. However, these metamorphs were not homogenized prior to extraction, so this amount of bufadienolides is probably an underestimate. The parotoid gland secretion of adult B. japonicus from Ishima contained large amounts of bufadienolides (Fig. 3b; electronic supplementary material, Supporting Information Fig. S1a).
R. tigrinus from Kinkasan
All six adult R. tigrinus from toad-free Kinkasan Island (three females and three males) lacked bufadienolides in their nuchal gland fluid (Fig. 4b), whereas hatchlings produced variable results depending on the individual's diet in captivity. Unfed and non-toad-fed hatchlings lacked bufadienolides (Fig. 4a), whereas hatchlings that were fed metamorphic toads (B. japonicus) possessed such compounds (Fig. 3c). Toad-fed hatchlings from all six clutches sequestered at least eight bufadienolides from their bufonid prey, with compound 11 being the most abundant bufadienolide in each sample (Table 1). The quantity of bufadienolides in the nuchal gland fluid increased as the mass of toads consumed increased (Fig. 5a; Spearman's rho = 0.947, P < 0.0005).
Table 1. Bufadienolides in juvenile Rhabdophis tigrinus from toad-free Kinkasan Island, fed controlled diets
Clutch 1 (N = 12)
Clutch 2 (N = 17)
Clutch 3 (N = 14)
Clutch 4 (N = 18)
Clutch 5 (N = 13)
Clutch 6 (N = 15)
N represents the number of hatchlings per clutch, whereas n indicates the number of individuals analyzed. Bufadienolides present in the majority of individuals per group are identified by compound numbers (see electronic supplementary material, Supporting Information Fig. S1b, for structures of compounds). The bufadienolide present in the largest quantity per group is underlined.
A strikingly different pattern emerged from the analysis of hatchling R. tigrinus from Ishima Island, which harbors a dense population of toads (B. japonicus). The unfed and non-toad-fed hatchlings typically possessed large quantities of bufadienolides (Fig. 4c). As an example, three unfed hatchlings from one clutch each contained 1.4–2.0 mg of bufadienolides in their nuchal gland fluid. Most hatchlings that were fed toads also contained large quantities of bufadienolides (Fig. 5b). Similar to the pattern seen in toad-fed hatchlings from Kinkasan, R. tigrinus from Ishima increased the quantity of bufadienolides in their nuchal gland fluid as the mass of toads consumed increased (Fig. 5b; Spearman's rho = 0.559, P < 0.0005).
Most unfed and non-toad-fed hatchlings from Ishima possessed seven or more bufadienolide compounds in their nuchal gland fluid (Table 2). Hatchlings that were fed toads from Niijima Island contained additional bufadienolides that were absent in their non-toad-fed counterparts (Table 2). Compound 14 was found only in those hatchlings that had been fed toads in captivity (Table 2).
Table 2. Bufadienolides in juvenile Rhabdophis tigrinus from toad-rich Ishima Island, fed controlled diets
Clutch 7 (N = 21)
Clutch 8 (N = 7)
Clutch 9 (N = 14)
Clutch 10 (N = 14)
Clutch 11 (N = 18)
Clutch 12 (N = 43)
N represents the number of hatchlings per clutch; n indicates the number of individuals analyzed. Bufadienolides present in the majority of individuals per group are identified by compound numbers (see electronic supplementary material, Supporting Information Fig. S1b, for structures of compounds). The bufadienolide present in the largest quantity in the majority of individuals per group is underlined. Two bufadienolides were present in equally large quantities in toad-fed individuals in clutch 10.
The six wild-caught adults from Ishima each possessed considerable quantities of bufadienolides in their nuchal gland fluid (Fig. 4d), and males contained extremely large amounts. Four adult males weighing 53–152 g possessed 27.0–68.9 mg of bufadienolides (mean = 43.7 mg). Nuchal gland fluid of two females weighing 275 and 652 g contained 7.3 and 20.4 mg of bufadienolides, respectively. Males had 0.34–0.69 mg of bufadienolides per gram of body mass (mean = 0.48 mg g−1), whereas both females had 0.03 mg g−1. This difference reflects both the larger body size of females and the smaller absolute quantity of bufadienolides that they possess relative to males.
The analysis of 20 wild-caught juvenile R. tigrinus on Ishima revealed large amounts of bufadienolides in both sexes (Fig. 3d), with females possessing significantly larger quantities than males. Females possessed an average of 6.5 mg of bufadienolides in their nuchal glands (range: 3.7–9.9 mg; n = 10), whereas males harbored an average of 4.1 mg (range: 1.9–7.8 mg; n = 10; Fig. 6). An ANCOVA revealed a significant difference between females and males in their quantities of bufadienolides (F = 6.849; d.f. = 1,16; P = 0.019). The covariates of mass and SVL did not affect bufadienolide quantity (P = 0.325 and P = 0.234, respectively). Compounds 1–13 and 17 were identified in this group of snakes, and all 20 individuals contained compounds 6/7 or 10 (gamabufotalin) in the greatest quantity, as did the hatchlings from Ishima that were used in the feeding experiment (Table 2).
Our results demonstrate clearly that the quantity of bufadienolides present in the nuchal glands of R. tigrinus reflects the availability of toads in the environment and, in captivity, is influenced by the diet of hatchlings. Hatchlings from toad-free Kinkasan Island lack bufadienolides in their nuchal glands at hatching because their dams (mothers) did not have access to toads as prey, from which the females could have sequestered and provisioned defensive bufadienolides to their offspring. These hatchlings lack bufadienolides after being fed nonbufonid frogs, fish and/or salamanders. However, hatchlings from Kinkasan are capable of sequestering bufadienolides in their nuchal glands when fed toads in the laboratory, and the quantity of bufadienolides they possess increases significantly with the mass of toads consumed.
Analysis of six adult R. tigrinus from Kinkasan demonstrated that the adults from this island also lack bufadienolides in their nuchal glands, which provides further evidence that this species is incapable of synthesizing defensive bufadienolides, even as adults. Therefore, the nuchal glands of R. tigrinus from Kinkasan are likely ineffective at deterring predators, which explains why snakes from this island tend to flee rather than use their nuchal glands in defensive displays (Mori & Burghardt, 2000). However, because these snakes have retained the ability to sequester toxins from bufonid prey, as demonstrated by our feeding experiment, they could regain the use of their nuchal glands for defense in the event of an introduction of toads to Kinkasan.
In contrast, all hatchling R. tigrinus from Ishima, where toads are abundant, possessed bufadienolides in their nuchal gland fluid, regardless of diet. Presumably, these compounds in unfed individuals and those fed nonbufonid prey were provisioned to them by their dams in utero, although the dams were not available for chemical sampling in this study. However, in support of this hypothesis, six adults from Ishima collected on subsequent expeditions possessed large quantities of bufadienolides. We have demonstrated previously that female R. tigrinus produce offspring with quantities of bufadienolides reflecting bufadienolide levels in the dams (Hutchinson et al., 2008) and that females can provision bufadienolides through deposition in yolk and by transfer to oviducal eggs during gestation (Hutchinson et al., 2008, 2012). In most cases, toad-fed hatchlings possessed larger quantities of bufadienolides than non-toad-fed hatchlings. The toad-fed hatchlings contained a greater diversity of bufadienolides than their non-toad-fed siblings, and the compounds found only in toad-fed snakes were those sequestered directly from the diet and not maternally provisioned. The difference between the most abundant bufadienolide in hatchlings from Ishima (compound 6/7 or 10) and that in toad-fed hatchlings from Kinkasan (compound 11) may reflect geographic or ontogenetic variation in the chemical profiles of B. japonicus, or physiological differences in sequestration abilities between R. tigrinus from Kinkasan and Ishima.
Most hatchlings from Ishima that were fed nonbufonid diets were sacrificed at 7–9 months of age, and their nuchal gland fluid was sampled after freezing. Thus, in most cases, the quantity of bufadienolides for these experimental hatchlings represents maternally provisioned compounds that were retained by the juveniles for more than 6 months, which is a pattern that we have reported previously for R. tigrinus (Hutchinson et al., 2008). It is not known how long these compounds ultimately persist in the snakes, but it is likely that the offspring must ingest toads at some point during their lives, if only to counter dilution of maternally provisioned toxins as they grow.
The 20 juvenile, wild-caught R. tigrinus from Ishima all possessed large quantities of bufadienolides in their nuchal gland fluid, and females contained significantly larger quantities of these defensive compounds than males. This difference could have arisen due to unequal maternal provisioning between male and female offspring in utero, perhaps due to the ability of female embryos to take up greater quantities of bufadienolides than males. Alternatively, the females may have been more successful at obtaining bufonid prey after hatching. However, R. tigrinus hatchlings emerge from their eggs in August to mid-September (Fukada, 1959), and we sampled these juveniles in September, so they had not had much time to forage.
Regardless of the mechanism that results in juvenile females possessing larger quantities of bufadienolides than juvenile males, the larger quantity of defensive compounds in females could prove important to their fitness. It is possible that females mobilize bufadienolides stored in their nuchal glands during vitellogenesis (yolk production) and/or during gestation to provide bufadienolides to their offspring prior to hatching. The nuchal glands contain a dense network of capillaries (Hutchinson et al., 2007), which likely serves to deliver bufadienolides from the oral mucosa or digestive tract to the nuchal glands. Those vessels may also carry bufadienolides from the nuchal glands to the liver (for deposition in yolk during vitellogenesis) and/or the oviducts for delivery to developing embryos. Thus, females would require larger quantities of bufadienolides than males so they can defend both themselves and their offspring from predators.
Although juvenile females from Ishima possess larger quantities of bufadienolides than juvenile males, our limited sample of adults from that island suggests that adult male R. tigrinus possess larger amounts of bufadienolides than adult females. On the basis of body mass, the bufadienolide content of adult males exceeds that of females by an order of magnitude. This is surprising because females reach a much larger body size than males (Fukada, 1992), so a larger proportion of toads in the population are available to females of this gape-limited predator. It is possible that the two adult females from Ishima possessed a lower quantity of bufadienolides than expected because they had transferred the toxins from their nuchal glands to their eggs, although this hypothesis remains untested. Further research is needed to explain why females possess more bufadienolides than males as juveniles, but the opposite is true for adults.
The presence of bufadienolides in the nuchal gland fluid of R. tigrinus from Ishima and the absence of those compounds in snakes from Kinkasan may strongly affect the fitness of individuals on these two islands. The large quantity of bufadienolides found in the nuchal gland fluid of most individuals from Ishima may result in enlarged nuchal ridges (Fig. 1), more effective defensive displays involving the glands and greater levels of chemical defense. Rhabdophis tigrinus from Kinkasan typically flee from perceived predatory threats (Mori & Burghardt, 2000), which is likely due to the lack of sequestered dietary compounds in that population. Thus, it is possible that R. tigrinus on toad-rich Ishima Island are better defended against their predators than are individuals on the toad-free island of Kinkasan.
We thank the following individuals for their contributions to this study: Seth Barribeau, Masami Hasegawa, Isami Ikeuchi, Noriko Kidera, Taku Mizuta, Eiko Nagata, Ralph Saporito, Tomohiko Shimada, Hirohiko Takeuchi and Ken Yoda for collecting animals; Takashi Haramura, Azusa Hayano, Yoshihisa Mori, Eiko Nagata and Koji Tanaka for husbandry; Noriko Kidera for assistance with the sampling of nuchal gland fluid and data entry; Georg Jander and Minsang Lee for the use of an LC-MS at Cornell; Thomas Spande and John Daly for supplying the telocinobufagin standard; and Xiaogang Wu for assistance with HPLC. This work was supported by the National Science Foundation (IBN-0429223 and IOB-0519458 to A.H.S. and J.M.); Coastal Carolina University (Research Enhancement Grant to D.A.H.); The Society for Integrative and Comparative Biology (Grant-in-Aid of Research to D.A.H.); the Japanese Ministry of Education, Culture, Sports, Science, and Technology (Grant for Biodiversity Research of the 21st Century COE A14 to A.M. and Department of Zoology, Kyoto University); the Kyoto University Museum (Visiting Faculty Award to A.H.S.); the Japan–US Cooperative Science Program (Japan Society for the Promotion of Science, JSPS, to A.M. and NSF INT-9513100 to G.M.B.); the Fujiwara Natural History Foundation (10th Annual Grant for Scientific Research to A.M.); and JSPS (Grant-in-Aid of Scientific Research C: 23570115 to A.M.).