Fluorescence in fireflies (Coleoptera: Lampyridae): using sentinel prey to investigate a possible aposematic signal.
Previous studies have shown that certain fireflies also are fluorescent, absorbing short wavelength light and reemitting it at longer wavelengths. Metcalf (1943) first described a firefly pigment with UV-induced red fluorescence, which he named lampyrine. In the firefly Photinus marginellus (LeConte) (Coleoptera: Lampyridae), this same author observed lampyrine beneath the pronotum, below the cuticle in the thorax and abdomen, and in the male testes. Examining preserved museum specimens with a UV light, Metcalf noted red fluorescence in 43 different lampyrid taxa, while it was lacking in related beetles he examined in the clades Phengodidae, Cantharidae, and Lycidae. Fluorescence in specific body regions has subsequently been reported in other firefly species (Sannasi 1970; Cicero 2008; Deheyn & Ballantyne 2009; Yiu & Jeng 2018), yet its function remains unexamined. In contrast to bioluminescence, fluorescence may serve as a passive warning signal that is useful in dim or daylight conditions.
Here we examined the possibility that firefly fluorescence may serve as an aposematic signal that deters predators. Under certain light environments, externally visible fluorescence can contribute substantively to body coloration (Marshall & Johnsen 2017). For example, undertwilight or nocturnal incident illumination, Taboada et al. (2017) showed that fluorescence in South American tree frogs generated 20 to 30% of their total emerging light (fluoresced plus reflected photons). Across firefly taxa, courtship aggregations are found in diverse light environments: certain bioluminescent fireflies court at dusk, whereas others are fully nocturnal, and species with non-luminescent adults are active during the d (Lloyd 2008). In addition, under various light conditions fireflies are likely to be encountered by insectivorous birds and mammals while resting on the ground or in vegetation. Here we experimentally investigate whether externally visible fluorescence altered predation rates using artificial firefly models with or without fluorescent markings as sentinel prey. Additionally, we measured seasonal variation in predation rates on the model prey (Lovei & Ferrante 2016; Roslin et al. 2017; Ferrante et al. 2017). Finally, we provide a detailed description of blue-induced fluorescence in adults and larvae of Ellychnia corrusca (L.) (Coleoptera, Lampyridae), an unusual diurnal non-luminescent firefly that overwinters on tree trunks during its adult stage.
Materials and Methods
FIELD STUDY SITE
We conducted the field portion of this study at Massachusetts Audubon's Habitat Sanctuary in Belmont, Massachusetts, USA (42.402184[degrees]N, 71.187205[degrees]W), a site we have used previously to investigate the behavior and life history of E. corrusca (Rooney & Lewis 2000). Widely distributed across the eastern US, this diurnal firefly has a unique phenology (Rooney & Lewis 2000; Faust 2012; Deyrup et al. 2017). In New England, the non-luminescent E. corrusca adults eclose in early fall, spend the winter exposed on tree trunks, then mate in early spring. Within this site, a suitable study area was chosen based on observed bird and small mammal activity as well as tree diversity.
TESTING FLUORESCENCE AS AN APOSEMATIC SIGNAL
To investigate whether fluorescent markings alter rates of predator attack we used the sentinel prey approach (Kidd & Jervis 2005), placing artificial prey in an area where they are exposed to a natural predator guild for a fixed amount of time. Artificial, firefly-sized prey (3.3 cm length x 1 cm width) were fashioned from black Fimo modelling clay (Staedtler, Nuernberg, Germany), left unbaked such that imprints from predator attacks would be visible. All models were produced with the same mold to ensure size and shape consistency. Models were marked using Gellyroll[R] gel pens(Sakura, Osaka, Japan); this waterproof ink did not wash off in rain or fade from sun exposure. We marked models to resemble the fluorescent coloration we have observed on other closely related Photinus fireflies (Stanger-Hall et al. 2007); these markings consisted of 3 green lines outlining the elytral margins, and 1 central red dot on the pronotum (see Supplementary Fig. 3). Models were marked with the following colors (fluorescent vs. non-fluorescent treatment, respectively): either Fluorescent Green (XPGB#427) or Green (XPGB-M#29), and either Fluorescent Red (XPGB06#418) or Red (XPGB#19).
Predation rate assays were conducted on a bi-weekly basis for 1 wk each from Oct 2017 to May 2018 (total of 11 assays). Each assay incorporated 12 model pairs, each pair containing 1 fluorescent and 1 control (non-fluorescent) artificial prey model. Within the study plot, a pair of models was placed on each of 12 haphazardly selected trees that varied in species, height, and diam; selected trees were at least 2 m apart. Each assay used a different group of 12 trees located within the same area. The 2 models in each pair were placed on opposite sides of the tree at approximately 1.5 to 2 m height, and were affixed to the tree trunk using short pins; the paired design accounted for any variation in predation rates that might be due to tree species and location.
In each assay, models were left out for 1 wk and inspected every 2 to 3 d for evidence of predation. Attacks were recorded, and any model showing evidence of predator attack was removed and replaced. After 7 d, all models were removed. As models were checked 3 times each wk, each assay yielded 36 observations per treatment. We report the number of attacks for each treatment as the sum of all recorded attacks, and calculated the number of "misses" by subtracting the number of attacks from the total number of observations (typically 36). We tested whether predation rates differed between fluorescent and non-fluorescent models using a Fisher's exact test on a 2 x 2 contingency table (R version 3.2.4, package "Hmisc").
We collected and photographed all models that had been attacked to aid in identifying specific predators (Roslin et al. 2017). In addition, during each trial conducted in the winter and early spring we surveyed locally active predators near models that we deployed on a separate tree using a motion-sensing Reconyx Hyperfire trail camera (Reconyx, Holden, Wisconsin, USA).
SEASONAL VARIATION IN PREDATION RATES
Because E. corrusca adults overwinter in exposed locations on tree trunks, we also used our sentinel prey experiment to investigate whether predation rates varied seasonally. Sentinel prey techniques are useful for measuring spatial and temporal variation in predation (Lovei & Ferrante 2016; Ferrante et al. 2017; Roslin et al. 2017). To investigate how seasonal changes in daylength and temperature might influence the total number of predator attacks, we conducted separate linear regressions using average photoperiod (h) and air temperature during each of the 11 assays periods (data obtained from Wunderground.com; analyses conducted in R using packages "Car" and "MASS").
FLUORESCENCE IN ELLYCHNIA FIREFLIES
Ellychnia corrusca fireflies have been shown to contain toxic lucibufagins that deter potential predators (Smedley et al. 2017). This species has shown distinctive coloration on its pronotum (head shield): a central black area is bordered with red, and surrounded on both sides by pale, parentheses-shaped areas. To investigate patterns of fluorescence, we photographed E. corrusca adults that we collected between Apr and Jun in Lincoln (42.424629[degrees]N, 71.307482[degrees]W) and Arlington, Massachusetts, USA (42.411750[degrees]N, 71.168096[degrees]W). Adult Ellychnia were freeze-killed for 5 min, then we immediately photographed their dorsal and ventral aspects. We also photographed a few E. corrusca larvae that we reared from eggs laid in the laboratory. Larvae were kept in darkness in small Petri dishes, and periodically fed with small pieces of earthworms.
Photographs were taken under illumination with a Nightsea Blue-Star light (Nightsea, Lexington, Massachusetts, USA) emitting 440 to 460 nm, with a longpass yellow filter (500 nm cutoff). Photographs were taken with either a Fujifilm Finepix HS10 camera (Fujifilm, Edison, New Jersey, USA), or under a Nikon dissecting microscope fitted with a Spot Insight camera (Nikon, Melville, New Jersey).
Across the entire study, about 50% of our models showed signs of predator attack (Table 1). However, we found no significant difference between the fluorescent and the non-fluorescent treatments in the percentage of model prey that were attacked (Fisher's exact test; 1 df; P = 0.47; odds ratio = 0.846).
We noted marked seasonal variation in the total number of attacks (Fig. 1). Attack rates on model prey increased through the fall until mid- to late-Nov, then declined during winter mo. While attack rates on non-fluorescent models showed an increase during Feb and Mar, no such increase was observed for fluorescent models (Fig. 1). This seasonal variation in attack rates was not associated with changes in either temperature (Fig. 2a; least squares minimization linear regression [F.sub.(19)] = 0.04, P = 0.84) or daylength (Fig. 2b; [F.sub.(19)] = 0.71, P = 0.42).
Approximately 20% of attacked models showed 2 parallel grooves about 3 mm long that could be indicative of small rodents (P. Marek, personal communication). We also observed deeper gashes ranging from 4 to 7 mm long in 30% of attacked models that may have resulted from bird attacks (L. Long, personal communication). Approximately 10% of attacked models showed shallow scrape marks conceivably caused by arthropod mandibles, possibly ants or spiders. Approximately 35% of attacked models showed shallow gashes about 3 mm long that were more difficult to attribute to a particular predator; these could represent marks made by the claws or beak of a bird, or claw marks of a small mammal. Finally, 5% of our models had chunks missing, were dismembered, or were removed from the tree; in these cases, no likely attacker could be determined. The trail camera revealed a white-breasted nuthatch (Sitta carolinensis) (Latham) (Sittidae: Sitta) and a grey squirrel (Sciurus carolinensis) (Gmelin) (Sciurus: Sciurus) foraging on trees near our models.
Under 440 to 460 nm (blue) excitation, E. corrusca adults showed green fluorescence on the dorsal pronotum, which was limited to the curved areas of non-melanized chitin bracketing the central dark spot (Fig. 3a). The area below and just posterior to the tip of the scutellum also fluoresced red (Fig. 3a). No fluorescence was apparent on the elytra. Ventrally (Fig. 3b), the pronotum and eyes showed green fluorescence, while soft tissues of the head and thorax displayed red fluorescence visible through the transparent integument. Patches of red fluorescence also surrounded the base of the legs (not shown). Under identical wavelength excitation, E. corrusca larvae (2 wk old) displayed only weak fluorescence from soft tissues visible through the body wall.
Adults of several firefly species are known to display externally visible, UV-induced fluorescent markings on various body regions, as evidenced by our study and those of Metcalf (1943), Sannasi (1970), Cicero (2008), Deheyn and Ballantyne (2009), as well as Yiu and Jeng (2018). Also fluorescence has been observed in diurnal and nocturnal species that differ remarkably in range, behavior, and life history. In the crepuscular firefly P. marginellus, Metcalf (1943) identified lampyrine, a fluorescent pigment present in fat body and responsible for the bright red coloration on the pronotum and other body regions. Lampyrine is likely to be responsible for the red fluorescence we observed underlying areas of clear cuticle on the ventral meso- and meta-thorax in the diurnally active E. corrusca. Though widely observed in preserved specimens across the Lampyridae, Metcalf (1943) noted that lampryine was absent from 2 species, Tenaspis angularis (Gorham) (Coleoptera: Lampyridae) and Photuris (Coleoptera: Lampyridae) sp., indicating interspecific variation that bears investigating.
The green fluorescence that we observed on the pronotum of E corrusca has not been previously described, and may arise in certain areas of untanned, unpigmented cuticle. Fluorescence has been found in the light producing organs of the firefly Bourgeoisia hypocrita (Olivier) (Coleoptera: Lampyridae), as well as in dorsal and ventral markings (Deheyn & Ballantyne 2009). Yiu and Jeng (2018) recently described whole-body blue-green fluorescence in the neotenic, flightless females of a newly described nocturnal lampyrid from Hong Kong, Oculogryphus chenghoiyanae Yiu & Jeng (Coleoptera: Lampyridae). Wiesenborn (2011) reported representatives of several insect orders that show blue fluorescence (emission maximum at 420 nm) associated with resilin, a structural protein providing elasticity. The green fluorescence we observed in E. corrusca is not likely from resilin, based on its distinct emission characteristics.
When we used sentinel prey to investigate the possible aposematic function for firefly fluorescence, we found no difference in predator attack rates on artificial prey models that had been painted with red and green fluorescent inks. This suggests that fireflies' fluorescent markings do not serve as an aposematic signal, at least for the predator guild active in New England woodlands. However, while our fluorescent models resembled generic firefly patterning to us, it is possible that they did not adequately match their brightness or spectral emission as perceived by natural predators. While measuring spectral properties was beyond the scope of this study, future work should quantify emission and excitation spectra of firefly fluorescence. Without measuring the exact excitation we cannot know how closely our models resembled actual fireflies. Additionally, it is possible that fluorescence may be perceived only as an effective warning in concert with other signals; for instance, Leavell et al. (2018) demonstrated that bioluminescence acts synergistically with some unknown acoustic signal to deter bat predation on fireflies in flight.
Fluorescence has been observed in fireflies that differ remarkably in their range, behavior, and life history, and several alternative explanations for firefly fluorescence are possible (Yiu & Jeng 2018). First, it is possible that firefly fluorescence has no adaptive value and is merely correlated with other features of body pigmentation. Other possible adaptive functions of fluorescence in fireflies that remain to be tested include sexual signaling or species recognition in dim light environments. Although courtship in many lampyrids takes place at night, others court during daytime or at dusk.
In summary, we found little evidence that fireflies gain any advantage in predation deterrence from conspicuous fluorescent markings. Our data show no substantial difference in predator attacks between models with or without fluorescence. These data do not support the hypothesis that firefly fluorescence serves as an aposematic signal. However, because of the prevalence of fluorescence in lampyrids and its variation across different species and genera, future studies should explore other possible functions for such a trait, including intraspecific and sexual communication. UV and blue-induced fluorescence has the potential to contribute substantively to body coloration in crepuscular and other dim light environments, and remains an exciting area for future investigations.
We thank Roger Wrubel for permission to work at Massachusetts Audubon's Habitat Sanctuary, Paul Marek (Virginia Tech), and Lawrence Long (North Carolina State University) for helping to identify characteristic predator marks, and the Starks-Lewis lab group for helpful comments on earlier versions of the manuscript.
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Aidan Wilcox ( (1)), and Sara Lewis ( (1))
(1) Tufts University, Department of Biology, Medford, Massachusetts 02155, USA; Email: firstname.lastname@example.org (A. W.); email@example.com (S. L.)
(*) Corresponding author; Email: firstname.lastname@example.org
Caption: Fig. 1. Seasonal changes in the number of recorded attacks on artificial prey having fluorescent (short-dashed line) and non-fluorescent (long-dashed line) markings between Oct 2017 and Feb 2018. For each trial, 36 observations were made for each treatment; in the fifth and sixth trials there were only 34 observations due to sampling difficulties. Total number of models attacked is also shown.
Caption: Fig. 2. Relationship between climatic variables and the total number of attacks recorded on artificial prey (both treatments combined) during each wk-long assay conducted from Oct 2017 through May 2018 (n = 11 wk): (a) photoperiod (d length in h), (b) average temperature per wk.
Caption: Fig. 3. Dorsal and ventral aspects of the head area of an Ellychnia corrusca adult illuminated with (a, b) Nightsea BlueStar light emitting 440 to 460 nm, and photographed with a longpass yellow filter (500 nm cutoff), and (c, d) the same individual under white light illumination.
Table 1. Total number and percentage of attacks on fluorescent and non-fluorescent artificial prey recorded from Oct 2017 to Feb 2018. Treatment Attacked Not attacked % Attacked Fluorescent 52 340 46.4 Non-Fluorescent 60 332 53.6
Please Note: Illustration(s) are not available due to copyright restrictions.
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|Author:||Wilcox, Aidan; Lewis, Sara|
|Date:||Sep 1, 2019|
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