Behavioral Ecology The official journal of the ISBE International Society for Behavioral Ecology Behavioral Ecology (2014), 25(2), 409–414. doi:10.1093/beheco/art128 Original Article Sexual signaling under predation: attractive moths take the greater risks Nils Cordes, Leif Engqvist, Tim Schmoll, and Klaus Reinhold Department of Evolutionary Biology, Bielefeld University, Morgenbreede 45, 33615 Bielefeld, Germany Received 12 August 2013; revised 9 December 2013; accepted 19 December 2013; Advance Access publication 29 January 2014. Individuals often have to balance the costs of risky behavior against the potential benefits they may gain from it. This trade-off is especially obvious in the interplay between natural and sexual selection because traits for mate attraction may attract predators as well. In the lesser wax moth Achroia grisella, ultrasonic sexual signaling comes with such a risk because calling for mates also attracts predatory bats. Attractive males should behave more cautiously than unattractive males under such circumstances, as they can expect more future mating opportunities and therefore have more to lose (the so-called asset protection principle). Contrary to these predictions, we found that pulse pair rate and peak amplitude, 2 song components attractive to females, correlated negatively with the duration of a silence response which is displayed when courtship song is experimentally overlayed with the search signal of a predator, the greater horseshoe bat. More attractive males thus recommence singing sooner than less attractive males. Although this is not in line with the asset protection principle, we discuss 3 different ways in which these distinct behavioral differences might be explained: 1) attractive males are in better condition and thus can more easily evade predators, 2) attractive signals are costly in terms of reduced life expectancy, and 3) risk-taking may in itself be a sexually selected trait and as such act as an honest signal of male quality. Key words: Achroia grisella, asset protection, attractiveness, consistent behavioral differences, risk-taking. Introduction In most species exhibiting elaborate courtship and sexual signaling, males that are conspicuous enough to attract females often are conspicuous enough to attract predators as well (Zuk and Kolluru 1998). Be it extravagant behavioral displays, bright colors, conspicuous odors, or attractive songs, sexual signaling often increases the risk of being eaten (Ryan et al. 1982; Magnhagen 1991; Acharya and McNeil 1998; Hedrick 2000; Kotiaho 2001), forcing individuals to trade current against future reproduction. Such is the case in males of the lesser wax moth Achroia grisella (Lepidoptera; Pyralidae) (Spangler 1984). Males gather in small leks on foliage or grass at night and attract females with ultrasonic songs. Females choose the individual with the most attractive song from the courting males for mating (Spangler et al. 1984; Jang and Greenfield 1996). Song attractiveness is determined by females based on 3 song traits: pulse pair rate, peak song amplitude, and the asynchrony of wing beat (Jang and Greenfield 1996, 1998). These courtship songs are, however, conspicuous also to echolocating predatory bats, informing them of the presence and position of the prey (Schnitzler and Ostwald 1983). The bat Rhinolophus ferrumequinum, for example, has been shown to attack live wax moths as well as loudspeakers broadcasting A. grisella courtship song (Alem et al. 2011). Male wax Address correspondence to N. Cordes. E-mail: [email protected]. © The Author 2014. Published by Oxford University Press on behalf of the International Society for Behavioral Ecology. All rights reserved. For permissions, please e-mail: [email protected] moths should therefore be selected to adjust their song in the presence of predators, for example, by ceasing acoustic signaling when they are aware of adjacent bats. Indeed, when signaling wax moths detect the search call of a predatory bat, they respond with a pause from singing (henceforth silence response) (Spangler 1984). Individuals differ repeatably in the length of this silence response, which may last from a few hundred milliseconds to over a minute (Greenfield and Baker 2003; Brunel-Pons et al. 2011; Cordes et al. 2013). There is evidence that males recommence singing sooner if under competition for females than if they sing alone (Brunel-Pons et al. 2011), suggesting that individual males can adjust their silence response to different social environments. The length of the silence response, however, can be considered a measure of risk-taking: Moths which start singing soon after the disturbance face greater risks of being detected by the bat than moths which remain silent for longer (Greenfield and Baker 2003). Taking a risk means jeopardizing one’s assets (Clark 1994). Often these assets can be an individual’s life or the chance for future reproduction. The amount of risks taken should therefore be higher for individuals with low compared with individuals with high residual reproductive value, a concept termed the “asset protection principle” (Clark 1994), which has found support in a number of species (Candolin 1998; Kemp 2002), including A. grisella (Lafaille et al. 2010). Wolf et al. (2007) showed that in theory such differences in asset protection could lead to the evolution of distinct Behavioral Ecology 410 behavioral phenotypes, i.e., animal personalities (Gosling and John 1999; Dall et al. 2004; Dingemanse and Wolf 2010). When courtship is performed by males in close vicinity, these males are in continuous competition with each other, so introducing a predator into a system like a lek is a valuable opportunity to detect and investigate individual behavioral differences. When other males cease courtship under the presence of a predator, opportunity arises for those individuals which might otherwise not be noticeable or which appear less attractive in direct comparison (Candolin 1997). Surprisingly, there has been little research regarding attractiveness as a manifestation of asset value (Billing et al. 2007; see also Schuett et al. 2010), but if attractive individuals can expect more opportunities for future reproduction, less attractive individuals should take higher risks as they have less to lose, in line with the asset protection principle. To explore the interplay between sexual signaling and predator avoidance, we tested for correlations between risk-taking behavior and the expression of 2 song traits attractive to females (pulse pair rate and peak amplitude). The analyzed data were obtained from an experiment for which larvae were reared under different densities to explore the effects of the larval environment on risk-taking behavior (cf. Cordes et al. 2013). We use this to our advantage by probing how robust the correlations between risk-taking and courtship display are across 3 different rearing environments. According to the asset protection principle, we expected that males whose song trait values suggest high sexual attractiveness would behave more cautiously than less attractive males when confronted with a predator search call. In pronounced contrast to this prediction, we here show that more attractive males behave more, not less risk-prone than their less attractive conspecifics. Methods We used a laboratory population of A. grisella, a short-lived, social parasite of honey bees (Kunike 1930) and reared larvae from different families (i.e., full-sib offspring from 1 pair) at 3 different densities (1, 2, or 6 larvae per 30-ml plastic cup) with ad libitum food to examine the effect of larval density on song quality and correlated behaviors (see Cordes et al. 2013 for detailed information on study populations, rearing methods, and diet). On eclosion, adult moths were weighed, and body mass was measured to the nearest 0.01 mg with a Kern 770 scale (Kern & Sohn GmbH, Balingen, Germany). Experimental setup Adult moths were 24–48 h old when measurements started. Before acoustic measurements, we transferred all males individually into gauze cages (3 cm diameter, 5 cm height) and kept them in shelves covered with insulation foam. To prevent males from hearing the ultrasonic songs of other males during the experiment, we placed the gauze cages into insulated enclosures which opened only to the front. Achroia grisella males sing continuously throughout the night (scotophase). We therefore played back a recording of the search signal of the greater horseshoe bat R. ferrumequinum, a potential predator of A. grisella whose call specifically causes lesser wax moths to intermit their behavior (Greenfield and Weber 2000; Alem et al. 2011; Cordes et al. 2013), for 3 trials: at the onset of scotophase, again 1 h later and at the onset of the subsequent scotophase. For this, we used the software Avisoft RECORDER USGH (Avisoft Bioacoustics, Berlin, Germany). The search call was transferred through an analogue/digital converter UltraSoundGate Player 116 (Avisoft Bioacoustics) and broadcasted by an ultrasonic speaker ScanSpeak from Avisoft Bioacoustics (frequency range [±12 dB]: 60–110 kHz). Before and during each playback, we recorded the courtship song of A. grisella using a condenser microphone (Brüel & Kjær, Nærum, Denmark; Type 4939, frequency response [±2 dB]: 0.004–100 kHz) in a distance of 10 cm from the cage, and a Nexus Conditioning Amplifier (Brüel & Kjær, Type 2690), which transferred the sound through an analogue/digital converter UltraSoundGate 116 (Avisoft Bioacoustics) to a computer. The song was then recorded using the software Avisoft RECORDER USG (Avisoft Bioacoustics). Recordings started 20 s before the bat call playback and were terminated 1 min after the bat signal was presented, even if moths had not recommenced signaling. In total, 6 males did not resume signaling in at least one of the playback trials (one did not recommence its song in all 3 trials); those measurements were considered as reflecting a 60-s duration of the silence response. For each of the 3 recordings, we measured pulse pair rate (the number of pulse pairs per second), peak amplitude (in V), and the duration of the silence response to the bat call (with a precision of 10 ms). Visualization of the song and measurements were performed with the sound analysis application Avisoft SASLab Pro (Version 5.1.14, Avisoft Bioacoustics). We also calculated a compound attractiveness score, which was defined as the sum of normalized and standardized pulse pair rate and peak amplitude, based on linear selection gradients for A. grisella, as determined by Jang and Greenfield (1998) and following the procedure proposed by Brandt and Greenfield (2004). Statistical analysis All statistical analyses were performed with the software package R, version 2.13.0 (R Development Core Team 2011). Prior to the analyses, we log transformed duration of the silence response (plus 1 ms) to approximate normality. In total, 171 individuals were used for all analyses. First, we separately tested for correlations between mean silence response (per individual) and mean pulse pair rate, mean peak amplitude, or mean attractiveness. We calculated Pearson’s product-moment correlation coefficients for all correlations for the full sample and, separately, also for each of the 3 larval density treatments. We then fitted bivariate linear mixed effects models for each correlation using Markov Chain Monte Carlo (MCMC) techniques (implemented in the R package MCMCglmm, Hadfield 2010), which allowed us to separate within- from between-individual effects for each of the correlations (Dingemanse and Dochtermann 2013). The MCMC chain was run for 1 300 000 iterations with a 300 000 iteration burn-in period and the remaining iterations sampled at 1000 iteration intervals. We estimated an unstructured two-by-two variance–covariance matrix for 2 random effects (individual identity and family identity) and the respective error variances. The priors for the variances were set to half of the phenotypic variance, the priors for the covariances were set to zero, and the degree of belief parameter was set to nu = 1.002. We checked all models for convergence using the Gelman–Rubin diagnostic (Gelman and Rubin 1992). Potential scale reduction factors for all variables were below 1.05. Time series plots revealed no autocorrelation issues within chains (Hadfield 2010). Repeatabilities for all 3 traits and correlation coefficients were calculated from the MCMC chains yielding posterior distributions of parameter estimates and the 95% highest posterior density (HPD) interval. We considered correlations significant when estimates’ 95% HPD intervals did not overlap with 0. To determine whether larval density affected the strength of the correlations, we fitted 3 separate models for each variable using the Cordes et al. • Attractiveness and risk-taking in wax moths same MCMC methods outlined above and compared betweenand within-individual correlation coefficients and 95% HPD intervals for all 3 treatment levels. To estimate the effect of larval density on pulse pair rate, peak amplitude, attractiveness, and body mass, we calculated separate linear mixed effects models (R function lmer from the R package lme4, Bates 2007) with individual identity and family identity as nested random effects and density treatment as a fixed effect factor with 3 levels. We refrained from using adult body mass as a covariate in addition to the treatment effect in the linear mixed effects models for pulse pair rate, peak amplitude, and attractiveness as body mass represents an intermediate outcome variable which must not be used because it is impossible to separate treatment effects from effects of the intermediate outcome variable in this case (Gelman and Hill 2007, pp. 188–194). For post hoc analysis of treatment level contrasts, we performed Tukey’s HSD tests (R function glht from the multcomp package, Hothorn et al. 2008). Finally, to analyze the relationship between body mass and song characteristics as well as risk-taking behavior, we calculated Pearson’s correlations between these variables. Results Individual repeatability and treatment effects The song traits pulse pair rate, peak amplitude, and attractiveness were significantly repeatable (Table 1), as was silence response (R = 0.35, 95% HPD interval: 0.26, 0.44, n = 171). Larval rearing density had no effect on pulse pair rate (χ2 = 1.38, df = 2, P = 0.5) but on peak amplitude (χ2 = 8.25, df = 2, P = 0.016) and, as a consequence, on attractiveness (χ2 = 8.31, df = 2, P = 0.016). Males raised under medium larval density performed louder songs (Z = −2.96, P = 0.009) and had a higher attractiveness score (Z = −2.97, P = 0.008) than males raised under high density. Solitarily reared males did not differ from males reared at medium 411 (peak amplitude: Z = 1.37, P = 0.35, attractiveness: Z = 1.46, P = 0.31) or high density (peak amplitude: Z = −1.09, P = 0.51, attractiveness: Z = −1.03, P = 0.56). The larval density treatment had no significant effect on male body mass (χ2 = 2.39, df = 2, P = 0.3). Overall, body mass was significantly positively correlated with peak amplitude (r = 0.40, P < 0.001) and attractiveness (r = 0.39, P < 0.001), but not with pulse pair rate (r = 0.09, P = 0.22) or silence response (r = −0.09, P = 0.26). Correlations between song characteristics and silence response We found a significant negative overall correlation between silence response and pulse pair rate (Table 1). Individuals with high pulse pair rates in courtship song showed shorter silence responses than individuals with lower pulse pair rates (Fig. 1a). The bivariate mixed model confirmed the significant negative between-individual correlation between silence response and pulse pair rate (Table 1). This correlation was consistent across treatment levels as reflected by the same sign and similar strength of the correlations. A withinindividual correlation was only significant for males from the lowdensity treatment (Table 1). We found a significant negative overall correlation between silence response and peak amplitude (Table 1). Males with songs of high amplitude had shorter silence responses than males singing at lower amplitudes (Fig. 1b). The bivariate mixed model, however, showed no significant between- or within-individual correlations (Table 1). Although correlations were all consistently negative, 95% HPD intervals for between- and within-correlation coefficients overlapped with 0 for the full sample as well as for the treatmentlevel-specific subsamples (Table 1). Across experimental treatment levels, pulse pair rate and peak amplitude were significantly positively correlated (Pearson’s Table 1 Correlations between the duration of the silence response in A. grisella courtship induced by playback of bat searching calls and 3 courtship song characteristics (pulse pair rate, peak amplitude, and a compound attractiveness score calculated from these 2 traits) Pulse pair rate Peak amplitude Attractiveness Pearson’s correlation n Estimate P Estimate P Estimate P rmeans Low density Medium density High density 171 31 45 95 −0.47 −0.46 −0.65 −0.46 <0.001 0.009 <0.001 <0.002 −0.15 −0.15 −0.05 −0.15 0.048 0.43 0.76 0.15 −0.24 −0.32 −0.18 −0.23 0.002 0.08 0.23 0.03 Bivariate mixed model n Estimate 95% HPD interval Estimate 95% HPD interval Estimate 95% HPD interval rbetween Low density Medium density High density rwithin Low density Medium density High density Repeatability 171 31 45 95 171 31 45 95 171 −0.49 −0.31 −0.65 −0.49 −0.12 −0.30 −0.04 −0.08 0.61 −0.66, −0.31 −0.69, 0.18 −0.88, −0.29 −0.71, −0.22 −0.22, −0.02 −0.52, −0.05 −0.25, 0.17 −0.22, 0.06 0.53, 0.68 −0.11 −0.12 −0.03 −0.16 −0.05 −0.23 0.02 0.05 0.61 −0.32, 0.09 −0.54, 0.36 −0.49, 0.51 −0.43, 0.14 −0.16, 0.05 −0.46, 0.01 −0.18, 0.22 −0.19, 0.09 0.53, 0.68 −0.21 −0.18 −0.10 −0.25 −0.08 −0.31 0.02 −0.07 0.63 −0.42, −0.003 −0.58, 0.30 −0.58, 0.39 −0.52, 0.03 −0.18, 0.02 −0.52, −0.08 −0.19, 0.23 −0.21, 0.07 0.56, 0.70 Correlations are presented separately for (sub) samples across and within 3 larval density treatment levels. rmeans is the Pearson correlation of means per individual (from 3 subsequent measurements); rbetween represents between-individual correlations and rwithin represents within-individual correlations as determined by a bivariate mixed model with individual identity and family identity as random effects and the overall mean as only fixed effect (see text for details). Repeatabilities were estimated from the bivariate model. Bold face indicates significant effects (P < 0.05); estimates from the bivariate mixed model were considered significant if an estimate’s 95% HPD interval did not overlap with zero. Behavioral Ecology 412 Mean duration of silence response (log10 (ms)) a 5 4 3 2 1 0 50 Mean duration of silence response (log10 (ms)) b 60 70 80 90 100 Mean pulse pair rate (pulse pairs s-1) 5 4 3 2 1 0 0 Mean duration of silence response (log10 (ms)) c 0.2 0.4 0.6 0.8 Mean peak amplitude (V) 1.0 5 4 3 2 1 0 -1.0 -0.5 0 0.5 1.0 Attractiveness score 1.5 2.0 Figure 1 Correlations between the duration of the silence response and (a) pulse pair rate, (b) peak amplitude, and (c) compound attractiveness of Achroia grisella courtship songs (n = 171). Symbols indicate means of 3 subsequent measurements per individual for males from low (circle), medium (square), and high (triangle) larval density treatment levels. correlation: r = 0.28, P < 0.001, n = 171). Furthermore, the compound attractiveness score was overall significantly negatively correlated with silence response (Table 1). Individuals with high attractiveness scores showed shorter silence responses than individuals with lower attractiveness scores (Fig. 1c). The bivariate mixed model confirmed a significant negative between-individual correlation for silence response and attractiveness (Table 1). This correlation was also consistent across treatment levels as reflected by the same sign and similar strength of the correlations. However, 95% HPD intervals overlapped with 0 for the treatment-level-specific subsamples, and within-individual correlation was only significant for males from the low-density treatment (Table 1). Discussion We hypothesized that individual attractiveness would covary negatively with risk-taking behavior in the lesser wax moth. Specifically, we predicted a positive correlation between 2 sexually selected traits and the duration of a silence response in the presence of bats as this would suggest that more attractive males take fewer risks. Hence, individuals with low pulse pair rate and low peak amplitude should have shorter silence responses than moths with high pulse pair rates and peak amplitudes because they should expect fewer future matings due to their lower attractiveness to females (Jang and Greenfield 1996) and should benefit more from recommencing courtship sooner under the perceived threat of predation. However, contrary to our expectations, we found consistently negative correlations between the variables. Individuals with higher pulse pair rate and peak amplitude were more likely to recommence their courtship signaling soon after a confrontation with a bat signal. This correlation appears robust as effect sizes for between-individual correlations were similar across all larval densities. Furthermore, the signs of the correlations were the same for pulse pair rate, peak amplitude, and the compound attractiveness score in both Pearson’s correlations of means per individual and the bivariate mixed model analysis. This means that males with short silence responses always had higher values for the attractiveness traits. The observation that more attractive individuals seem to take greater risks than less attractive ones is quite surprising and rare (Schuett et al. 2010; Wilson et al. 2010). In fact, according to the asset protection principle, there are good reasons for attractive individuals to take fewer risks. Considering that risky behavior means jeopardizing one’s assets, individuals with much to lose, i.e., attractive virgin males with an expectation of multiple future mating opportunities, should behave more cautiously than individuals for whom future copulations are unlikely (Clark 1994). Expanded into a theory for the evolution of distinct behavioral correlations, Wolf et al. (2007) used the residual reproductive value as a crucial component in modeling the evolution of separate strategies within 1 population, resulting in risk-prone and risk-averse individuals. Although this explanation may apply to behavioral differences in lesser wax moths of different age, younger wax moths take fewer risks than old ones (Lafaille et al. 2010), it does not seem to fit with the observed between-male differences in relation to acoustic attractiveness. However, considering that costs are involved in producing high pulse pair rate (Reinhold et al. 1998), attractive individuals may exhaust their resources sooner and have shorter life expectancies than less attractive individuals (cf. Höglund and Sheldon 1998; Hunt et al. 2004). If this was indeed the case, attractive individuals rather employ something akin to a “live fast, die young” strategy (Bonduriansky et al. 2008) and therefore may actually benefit more from taking greater risks than unattractive males. Thus, what we perceive as a moth with high residual reproductive value (and therefore assume should be a more cautious one) may in fact be the one which—in concordance with the asset protection principle—should behave less cautiously. It is also possible that mechanical constraints may contribute to the explanation of the observed correlations. For instance, both pulse pair rate and silence response might be affected by the dynamics of muscular tension in the thorax, as pulse pair rate is simply the wing beat frequency during singing (Spangler et al. 1984), and an interaction between muscular tension and proprioceptors might influence the recommencement of acoustic signaling after a pause. In principle, body mass and wing size may also have an influence on pulse pair rate and peak amplitude (Brandt and Greenfield 2004), but little is known about their effect on the silence response (Cordes et al. 2013). In any case, as we did not find a correlation between silence response and body mass, it is unlikely that body mass or size should be able to explain our results. The argument that attractive males take higher risks by reducing the duration of their silence responses implicitly assumes that Cordes et al. • Attractiveness and risk-taking in wax moths the extent to which sexual advertisement increases predation risk is uncorrelated with male attractiveness. However, actual predation risk for attractive and unattractive A. grisella males has not been studied and remains to be tested. Thus, attractive males could, for example, be more viable and better at actively avoiding predation. In this case, attractiveness would signify a reduction in the degree of risk for an individual male (Lindström et al. 2006; Sih and Bell 2008)—a type of positive feedback between asset and behavior contrary to the negative feedback suggested by Wolf et al. (2007). Risk-taking behavior could then be perceived as an honest signal of male quality. Honest sexual signals must be costly and condition dependent (Kotiaho 2000, 2001). There is as yet no evidence that attractive wax moths should be generally better at avoiding predation, but because individuals need more energy to produce a high pulse pair rate (Reinhold et al. 1998) and high peak amplitude reflects a larger body size, attractive—and, based on this study, the more risky—individuals may actually have and broadcast an overall higher phenotypic and possibly genotypic quality. Finally, the bivariate mixed model analyses allowed us to determine the contribution of within-individual effects on these correlations. The presence of within-individual correlations here means that individuals show correlated changes in song characteristics and risk-taking behavior over subsequent observations. Curiously, withinindividual correlations between silence response and pulse pair rate as well as attractiveness were largest and significantly different from 0 for solitarily reared males. This suggests that within-individual behavioral changes are stronger in solitarily reared males than those reared in groups. Such individual behavioral adjustments may be expected for pulse pair rate, which males are known to adjust slightly, albeit only under high-competition conditions (Jia et al. 2001). In general, the within-individual correlation between silence response and the song traits could be explained by an age effect. The experiment was performed over the course of 25 h, and although this is a relatively short period, age is known to affect both song (Jang et al. 1997) and risk-taking behavior (Lafaille et al. 2010) in A. grisella. Age may therefore have contributed similarly to a change in pulse pair rate and the attractiveness score within individuals, leading to the detected within-individual correlation between the traits. We do not know whether the among-individual correlations we found on the phenotypic level reflect genetically correlated traits. Interestingly, there is some indication that silence response has a heritable component (Cordes et al. 2013), and both pulse pair rate and peak amplitude have actually been shown to be heritable (Collins et al. 1999). This implies that investigating genetic correlations along these lines may provide a valuable direction for future research. We are currently working on a theoretical framework in order to understand under which circumstances it would be expected that more attractive individuals should take greater risks. Irrespective of whether the observed correlation is the result of differential risktaking in response to expected future reproductive output, or risk-taking behavior in A. grisella actually represents an honest signal of male quality, our results illustrate the importance to understand in detail the causes of repeatable behavioral differences among individuals. Funding German Research Foundation (DFG) (project number FOR 1232). We thank M. Greenfield for providing us with recordings of R. ferrumequinum, R. Feist, M. Hausmann, P. Erkeling, D. Kluge, and J. Gumpert for the support in rearing of wax moth populations, and H. Schielzeth for help 413 with the analysis and comments on an earlier version of this manuscript. Special thanks to G. 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