BioBlog

Smells Like Trouble

Presence of multi-female pheromones increases male aggression in the Mediterranean field cricket, Gryllus bimaculatus

Sebastian Carvello

March 2025

Imperial College London

Abstract

Intraspecific aggression is fundamental to resource competition, often influencing reproductive success across taxa. In this study, we examined how female pheromonal cues modulate male aggression in the Mediterranean field cricket, Gryllus bimaculatus. Building on behavioural game theory predictions, we hypothesised that exposure to multi‐female pheromones would elevate perceived resource value, thereby intensifying aggressive interactions among males. Size‐matched male crickets were paired in custom-designed polypropylene arenas and subjected to one of three treatments: (i) multi-female pheromones (filter paper from a female-only tank), (ii) the presence of a single female confined within an isolation tube, and (iii) a control with no female cues. Aggressive behaviour was quantified using multiple metrics, including the total number of discrete agonistic bouts and the maximum escalation level reached during 10-minute trials. Generalised linear models revealed that males exposed to multi-female pheromonal cues engaged in approximately 2.6 times more fights and reached twice the peak aggression level compared to those in the single-female treatment. In contrast, no significant differences were observed in the latency to or duration of the initial aggressive encounter across treatments. These results support the notion that chemical cues, specifically those indicative of multiple potential mates, enhance the perceived value of a resource and thus drive increased male aggression. Our findings contribute to a growing understanding of the role of olfactory signals in mediating intrasexual competition in crickets.

Smells Like Trouble - Presence of multi-female pheromones increases male aggression in the Mediterranean field cricket, Gryllus bimaculatus | Sebastian Carvello, Imperial College London, 2025.pdf

Full-text

Introduction

Intraspecific aggression is commonplace across the animal kingdom, largely due to competition for limited resources, from food and shelter to territory and sexual partners (Stevenson & Rillich, 2016). Indeed, agonistic social interactions have a key role in reproductive success across many different taxa (Buena & Walker, 2008), including in crickets (Grylloidea) (Savage et al., 2005). However, fighting is metabolically costly (Hack, 1997) and, more seriously, often carries the risk of injury or death (Huntingford & Turner, 1987). As such, to minimise uneconomically favourable conflict that is likely not to be worth the potential resulting costs in fitness, escalation in aggression tends to be mediated, among a range of factors, by perceived resource value (Enquist & Leimar, 1987). Should an agonistic bout between two male crickets commence, escalation in aggression tends to stereotypically follow a relatively predictable probabilistic sequence, ranging from inexpensive, lower risk behaviours, such as antennal fencing, to riskier behaviours, climaxing in full grappling (Hack, 1997); these are illustrated in the ethogram used to categorise levels of aggression in this study, shown in Figure 2 (Stevenson et al., 2005).

Chemical communication is acknowledged to be key in the mediation of social interactions in insects (d’Ettorre & Hughes, 2008). While crickets appear to rely on acoustic and vibrational communication more so that chemical, it has been found that olfactory cues can be used by both field (Gryllus) and house (Acheta) species to determine the sex of another individual, with aggression in male crickets increasing in the presence of the odour of a female (Otte & Cade, 1976). However, the consensus on this is not conclusive, with a more recent study finding that, while the presence of conspecific females elicited increased agonistic behaviour, female olfactory cues alone did not have such an effect (Tachon et al., 1999). A 2008 study (Buena & Walker) noted that, as predicted by behavioural game theory models (Enquist & Leimar, 1987), resident males were increasingly aggressive, defending their territories more vigorously, when it was of a higher perceived value, which importantly was manipulated by varying the number of females’ chemical cues present. To further investigate the impact of female pheromonal cues on modulating male cricket aggression, we paired male Gryllus bimaculatus of similar sizes in a controlled arena under three different treatments (female pheromones, a single female, and a control with neither) and recorded various indicators of aggression. Filter paper that had been left in a female-only G. bimaculatus tank was used for the pheromonal treatment so, should our results align with Buena & Walker’s findings (2008) that aggression was correlated with number of females’ pheromones present (and therefore resource value), we would expect significantly increased aggression between individuals under this condition. However, should olfactory cues alone be insufficient to elicit an aggression response, as stated by Tachon et al. (1999), we would not observe such a trend, and instead the single female treatment, which provided the males with visual and potentially acoustic/vibrational cues (in addition to pheromonal cues of just one female), would result in the most significant increase in aggression.

Methods

Study animals

The G. bimaculatus for this study were sourced from a UK-based live feed supplier and separated into male and female isolation tanks upon arrival at the department. Commercial cricket food and water gel was provided ad libitum, and the crickets were euthanised via freezing at -20°C after completion of the study. As invertebrates, crickets are not under the regulation of the Animals (Scientific Procedures) Act 1986 however, the use of live organisms in this study was conducted in accordance with the ASAB Ethical Committee’s Guidelines for the ethical treatment of nonhuman animals in behavioural research (2023). Experiments were carried out between 4th and 11th March, 2025 and with the assistance of experienced technicians.

Pairing of males, arena design & fight procedure

Males were captured from the main tanks as required, selected for consistent and good body condition. Body size is acknowledged to be a major determiner of resource holding potential (RHP) in crickets (Dixon & Cade, 1986). To control for this, pronotum width was recorded for all individuals, and fighting pairs were approximately size-matched (see Appendix). The sufficiency of our size matching was verified through generalised linear modelling of size difference as a predictor for the aggression indicators that were found to be significant (see Results), and no significance was found for either (p=0.535 for Bouts.T~SizeDiff (negative binomial family with a log link function, used due to overdispersion), p=0.255 for MaxLevel.T~SizeDiff (Poisson family with a log link function)). It was ensured that paired males came from separate main tanks to avoid pre-established dominance, which would otherwise likely affect the dynamics of any future aggression (Stevenson & Rillich, 2012).

A set of custom hinged arenas was constructed from polypropylene containers (Figure 1), with final dimensions of 10W x 15L x 8H cm and a removable divider to facilitate a 2-minute acclimatisation period before each trial. Arenas were wiped with 70% ethanol and allowed to fully dry between uses to remove any persisting olfactory residues.

Trials lasted 10 minutes each (following the 2-minute acclimatisation period), and each was observed by two researchers for increased accuracy. The variables recorded for each trial are listed in Table 1. MaxLevel.1 and MaxLevel.T – the maximum level of aggression observed in the first agonistic interaction and overall, respectively – were determined using an ethogram of the stereotypical escalation sequence for agonistic interactions between male crickets (Stevenson et al., 2005) (Figure 2). Consistency between pairs of observers was verified through seven trial runs that were observed by all researchers, with interobserver reliability metrics calculated for each dependant variable (Table 2). Individual males were identified using distinguishing physical characteristics and non-toxic researcher-applied ink markings, and subsequently tracked using unique identifiers (see Appendix), to ensure that no individuals were re-fought soon after a previous fight and that no two same individuals were re-paired for a subsequent fight (to avoid pre-established dominance).

Table 1: Description of the five aggression response variables recorded for each trial.
Table 2: Interobserver reliability estimates for the aggression measures. Reliability for ordinal data (MaxLevel.T) was evaluated using Kendall’s W, resulting in a high concordance of 0.978, while the intraclass correlation coefficient (ICC) was used for continuous (Duration.1, Latency.1) and count data (Bouts.T), resulting in very high estimates indicating excellent interobserver reliability. All ICC values were computed with a two-way random effects model for agreement on single scores.

Treatments

Ten trials were run for each treatment. The three treatments were as follows: female pheromones (hereafter referred to as ‘Pheromones’) whereby a 10 x 15 cm cutting from a piece of filter paper left in the female main tank for 48 hours was placed on the arena floor; single female (‘Female’) whereby an individual female was placed in the arena, contained within a caged isolation tube (see Figure 1) that allowed the males to view her and detect any olfactory cues, but not physically access her (so that the aggression allocation of their time budgets could not be reduced by attempting copulation); and ‘Control’ with neither the filter paper nor single female present. The same female was used for all trials of the Female treatment so that varying female attractiveness could not interfere with male willingness to fight over the potential mate (male sexual preferences for cuticular hydrocarbons have been identified in T. oceanicus (Thomas & Simmons, 2010)).

Figure 1: Illustration of the custom polypropylene hinged arenas constructed for the study. Limited ceiling-only airholes aimed to maximise the concentration of pheromones inside the arena, while providing sufficient ventilation for the subjects. The particular experimental setup shown is for the Female treatment, with the female cricket present in an isolation tube. Created in BioRender.
Figure 2: Escalating aggression levels between a pair of male crickets. These were used to score the level of agonistic interaction observed from 0 to 6 (MaxLevel.1 and MaxLevel.T in Table 1). Reproduced from Stevenson et al., 2005.

Statistical analysis

Generalised linear models (GLMs) were used to assess the effect of treatment on each response variable. A Poisson family with a log link function was used for Bouts.T, MaxLevel.1, and MaxLevel.T, while a Gaussian family with an identity link function was used for Latency.1 and Duration.1. Model assumptions were verified by examining base R diagnostic plots, and no violations were observed. Overdispersion was assessed for Poisson models and not found. Post-hoc pairwise comparisons were conducted using Tukey’s HSD test. All statistical analyses were performed in RStudio version 2024.12.1+563.

Results & Analysis

Fight count

Fight count ranged from 0 to 9, with median (IQR) Bouts.T values for Female, Control and Pheromones treatments of 2.5 (2.5), 3.5 (3.0) and 6.5 (2.75) respectively. Our Poisson GLM (Table 3) revealed a significant effect of Treatment on the number of fights (x2 = 19.66, df = 2, p = 5.38x10-5), with an overdispersion ratio of 1.02. Posthoc Tukey tests (adjusted) indicated that the Pheromones group exhibited more fights than both the Female group (p < 0.001) and the Control group (p = 0.010), whereas there was no significant difference between Female and Control (p = 0.389), as shown in Figure 3, corresponding to an increase by a factor of approximately 2.63 (e0.9651) in the number of fights in the presence of multiple females’ pheromonal cues versus the presence of a lone female.

Table 3: Poisson GLM summary for fight count (Bouts.T) with Treatment as a predictor. The intercept, which represents the reference level (Female treatment), is highly significant, indicating that this is reliably different from zero. TreatmentN and TreatmentP represent Control and Pheromones treatments respectively, the latter of which is highly significantly different to the reference level (Female treatment).
Figure 3: Boxplots depicting the distribution of the total number of discrete agonistic interactions across three treatments: Female (red, N = 10), Control (green, N = 10), and Pheromones (blue, N = 10). The horizontal line within each box indicates the median, the diamond shows the mean, and the upper and lower edges of each box represent the interquartile range (IQR). Whiskers extend to 1.5×IQR beyond the box. Individual black dots represent raw data points. Significant post-hoc Tukey comparisons are indicated by red brackets: *** = p < 0.001 between Female and Pheromones, and * = p < 0.05 between Control and Pheromones. The results indicate that crickets exposed to multiple females’ pheromones engaged in significantly more fights compared to both lone Female and Control conditions.

Maximum aggression level

Maximum aggression levels ranged from 0 to 6, with median (IQR) MaxLevel.T values for Female, Control and Pheromone treatments of 2.5 (1.75), 4.5 (3.0), and 5.0 (1.0) respectively. Our Poisson GLM (Table 4) revealed a significant effect of Treatment on maximum aggression (x2 = 8.54, df = 2, p = 0.014), with an overdispersion ratio of 0.82. Posthoc Tukey comparisons indicated that the Pheromones group reached significantly higher peak aggression than the Female group (p = 0.013), whereas neither Pheromones vs. Control (p = 0.288) nor Female vs. Control (p = 0.339) differed significantly, as shown in Figure 4. This means that peak aggression doubles (e0.6931 = 1.9999) in the presence of multiple females’ pheromonal cues versus the presence of a lone female.

Table 4: Poisson GLM summary for maximum aggression level (MaxLevel.T) with Treatment as a predictor. The intercept, which represents the reference level (Female treatment), is highly significant, indicating that this is reliably different from zero. TreatmentN and TreatmentP represent Control and Pheromones treatments respectively, the latter of which is significantly different to the reference level (Female treatment).
Figure 4: Boxplots illustrating the maximum level of agonistic escalation (ranging from 0 to 6) observed during each trial under Female (red, N = 10), Control (green, N = 10), and Pheromones (blue, N = 10) treatments. A red bracket highlights the significant difference in peak aggression between the Female and Pheromones treatments (* = p < 0.05). Neither Pheromones vs. Control nor Female vs. Control showed a statistically significant difference (p > 0.05).

Other indicators of aggression

No significant effects emerged for duration of (Duration.1) or time to (Latency.1) first bout in Gaussian GLMs (p>0.05 for all coefficients), and maximum escalation level of first bout (MaxLevel.1) showed no effect of Treatment in a Poisson GLM (p>0.05 for all coefficients) (Table 6). Descriptive statistics for these three variables are shown in Table5.

Table 5: Descriptive statistics for the non-significant response variables.
Table 6: Summary of the GLMs for Duration.1, Latency.1 and MaxLevel.1 with Treatment as a predictor. No coefficients were found to be significant.

Discussion

Our findings that pheromonal cues from multiple females increases male aggression compared to the physical presence of a single female, namely a 2.63 factor increase in the number of agonistic bouts with double the maximum intensity, appears consistent with those of Buena & Walker (2008) in that cues representing a greater number of potential mates is indeed seemingly associated with a higher perceived resource value. This was demonstrated via increased aggression, as predicted by the behavioural game theory models of Enquist & Leimar (1987). It is possible that male crickets interpret multi-female pheromone signatures as a higher-reward environment, leading to greater motivation to establish dominance, manifesting as increased risk tolerance to engage in potentially more costly aggressive behaviours (Hack, 1997).

These results also serve to highlight the great importance of olfactory cues with respect to the mediation of intrasexual competitive behaviour in G. bimaculatus as identified by Otte & Cade (1976) but contrary, however, to the findings of Tachon et al. (1999) that olfactory cues alone were insufficient to increase male aggression. Indeed, in the decades following Tachon et al.’s publication, there has been mounting evidence of the ability of pheromones to elicit a range of different behaviours in crickets (Nagamoto, Aonuma & Hisada, 2005), although much of this seems to revolve around female pheromones eliciting mating behaviour responses in males and male pheromones eliciting agonistic responses in other males (as opposed to female olfactory cues eliciting agonistic competitive behaviour in males) (Iwasaki & Katagiri, 2008). As such, our study and its findings may be of particular significance.

Limitations & potential future research

It was unexpected that the Female treatment yielded no increased aggression (and that it in fact produced the lowest bout count and total intensity of all three treatments, although not significantly below Control). This is also at odds with the findings of Tachon et al. (1999) however, increased male aggression in the presence of conspecific females has been consistently observed across taxa (Smith et al., 1994; Kitchen, Cheney & Seyfarth, 2005; Petrusková et al., 2007), with the exception of sex-role-reversed female-dominated social structures such as that of the spotted hyaena (Curren et al., 2015). Therefore, this instead likely points to two potential flaws in our experimental design.

Firstly, the presence of the isolation tube containing the female will have altered the spatial dynamics of the arena – for example, it was observed on multiple occasions that the apparently less dominant of the two males would hide behind the tube, thus reducing the likelihood of physical encounters with the other male. A future improved study might employ the use of an external audience zone for the female to reside in, where she can be observed by the males without physical intrusion of the arena space.

Secondly, while we used one particular female in an attempt to maintain consistency and limit variability in female attractiveness confounding the aggression responses from one trial to the next (Thomas & Simmons, 2010), this may have in fact biased the results of the Female treatment group due to a failure to control for attractiveness characteristics of this female. For example, it has been f0und that the quality and quantity of female crickets’ cuticular pheromones is highly age dependant, with courtship behaviour more likely in males when exposed to cues of younger females (Nagamoto, Aonuma & Hisada, 2005). This same study, however, observed that older, ‘less attractive’ females can in fact elicit aggressive behaviours in males. This relationship not only meant that the age characteristics of our chosen female will have likely had a significant impact on the observed male behavioural responses, but that this will not have been a simple case of a younger female leading to more competitive fighting and vice versa, since the relationship at play appears to be substantially more complex. Further experimentation with a series of age-controlled trials would be valuable in exploring and disentangling this phenomenon.

Acknowledgements

Many thanks to Dr Magda Charalambous for academic guidance, Dr Josh Hodge for advice on statistical analysis, Vitor Marques for laboratory support, and our crickets for their contribution to science.

References

ASAB Ethical Committee/ABS Animal Care Committee (2023) Guidelines for the ethical treatment of nonhuman animals in behavioural research and teaching. Animal Behaviour. 195, I–XI. doi:10.1016/j.anbehav.2022.09.006.

Buena, L.J. & Walker, S.E. (2008) Information asymmetry and aggressive behaviour in male house crickets, Acheta domesticus. Animal Behaviour. 75 (1), 199–204. doi:10.1016/j.anbehav.2007.04.027.

Curren, L.J., Linden, D.W., Heinen, V.K., McGuire, M.C. & Holekamp, K.E. (2015) The functions of male–male aggression in a female-dominated mammalian society. Animal Behaviour. 100, 208–216. doi:10.1016/j.anbehav.2014.11.024.

Dixon, K.A. & Cade, W.H. (1986) Some factors influencing male-male aggression in the field cricket Gryllus integer (time of day, age, weight and sexual maturity). Animal Behaviour. 34 (2), 340–346. doi:10.1016/S0003-3472(86)80102-6.

Enquist, M. & Leimar, O. (1987) Evolution of fighting behaviour: The effect of variation in resource value. Journal of Theoretical Biology. 127 (2), 187–205. doi:10.1016/S0022-5193(87)80130-3.

d’Ettorre, P. & Hughes, D.P. (2008) DOI: 10.1093/acprof:oso/9780199216840.001.0001. Sociobiology of Communication. Oxford University Press. doi:10.1093/acprof:oso/9780199216840.001.0001.

Hack, M.A. (1997) The energetic costs of fighting in the house cricket, Acheta domesticus L. Behavioral Ecology. 8 (1), 28–36. doi:10.1093/beheco/8.1.28.

Huntingford, F.A. & Turner, A.K. (1987) Animal Conflict. Dordrecht, Springer Netherlands.

Iwasaki, M. & Katagiri, C. (2008) Cuticular lipids and odors induce sex-specific behaviors in the male cricket Gryllus bimaculatus. Comparative Biochemistry and Physiology. Part A, Molecular & Integrative Physiology. 149 (3), 306–313. doi:10.1016/j.cbpa.2008.01.008.

Kitchen, D.M., Cheney, D.L. & Seyfarth, R.M. (2005) Contextual Factors Meditating Contests Between Male Chacma Baboons in Botswana: Effects of Food, Friends and Females. International Journal of Primatology. 26 (1), 105–125. doi:10.1007/s10764-005-0725-y.

Nagamoto, J., Aonuma, H. & Hisada, M. (2005) Discrimination of conspecific individuals via cuticular pheromones by males of the cricket Gryllus bimaculatus. Zoological Science. 22 (10), 1079–1088. doi:10.2108/zsj.22.1079.

Otte, D. & Cade, W. (1976) On the role of olfaction in sexual and interspecies recognition in crickets (Acheta and Gryllus). Animal Behaviour. 24 (1), 1–6. doi:10.1016/S0003-3472(76)80091-7.

Petrusková, T., Petrusek, A., Pavel, V. & Fuchs, R. (2007) Territorial meadow pipit males (Anthus pratensis; Passeriformes) become more aggressive in female presence. Naturwissenschaften. 94 (8), 643–650. doi:10.1007/s00114-007-0237-z.

Savage, K.E., Hunt, J., Jennions, M.D. & Brooks, R. (2005) Male attractiveness covaries with fighting ability but not with prior fight outcome in house crickets. Behavioral Ecology. 16 (1), 196–200. doi:10.1093/beheco/arh143.

Smith, I.P., Huntingford, F.A., Atkinson, R.J.A. & Taylor, A.C. (1994) Mate competition in the velvet swimming crab Necora puber: effects of perceived resource value on male agonistic behaviour. Marine Biology. 120 (4), 579–584. doi:10.1007/BF00350078.

Stevenson, P.A., Dyakonova, V., Rillich, J. & Schildberger, K. (2005) Octopamine and Experience-Dependent Modulation of Aggression in Crickets. The Journal of Neuroscience. 25 (6), 1431–1441. doi:10.1523/JNEUROSCI.4258-04.2005.

Stevenson, P.A. & Rillich, J. (2016) Controlling the decision to fight or flee: the roles of biogenic amines and nitric oxide in the cricket. Current Zoology. 62 (3), 265–275. doi:10.1093/cz/zow028.

Stevenson, P.A. & Rillich, J. (2012) The Decision to Fight or Flee – Insights into Underlying Mechanism in Crickets. Frontiers in Neuroscience. 6, 118. doi:10.3389/fnins.2012.00118.

Tachon, G., Murray, A.-M., Gray, D.A. & Cade, W.H. (1999) Agonistic Displays and the Benefits of Fighting in the Field Cricket, Gryllus bimaculatus. Journal of Insect Behavior. 12 (4), 533–543. doi:10.1023/A:1020970908541.

Thomas, M.L. & Simmons, L.W. (2010) Cuticular hydrocarbons influence female attractiveness to males in the Australian field cricket, Teleogryllus oceanicus. Journal of Evolutionary Biology. 23 (4), 707–714. doi:10.1111/j.1420-9101.2010.01943.x.

Imperial College London logo.