Browse Subject Areas

Click through the PLOS taxonomy to find articles in your field.

For more information about PLOS Subject Areas, click here.

  • Loading metrics

Overwintering aggregations are part of Hippodamia undecimnotata’s (Coleoptera: Coccinellidae) mating system

  • Eline Catherine Susset ,

    Roles Conceptualization, Data curation, Investigation, Methodology, Project administration, Resources, Writing – original draft, Writing – review & editing

    Affiliations Université Toulouse 3 Paul Sabatier, CNRS, ENSFEA, UMR5174 EDB (Laboratoire Évolution et Diversité Biologique), Toulouse, France, CNRS, Université Paul Sabatier,UMR5174 EDB, Toulouse, France

  • Jean-Louis Hemptinne,

    Roles Conceptualization, Writing – review & editing

    Affiliations Université Toulouse 3 Paul Sabatier, CNRS, ENSFEA, UMR5174 EDB (Laboratoire Évolution et Diversité Biologique), Toulouse, France, CNRS, Université Paul Sabatier,UMR5174 EDB, Toulouse, France

  • Etienne Danchin,

    Roles Conceptualization, Funding acquisition, Methodology, Writing – review & editing

    Affiliations CNRS, Université Paul Sabatier,UMR5174 EDB, Toulouse, France, ENSFEA, Université Toulouse 3 Paul Sabatier, CNRS, UMR5174 EDB (Laboratoire Évolution et Diversité Biologique), Castanet-Tolosan, France

  • Alexandra Magro

    Roles Conceptualization, Writing – review & editing

    Affiliations Université Toulouse 3 Paul Sabatier, CNRS, ENSFEA, UMR5174 EDB (Laboratoire Évolution et Diversité Biologique), Toulouse, France, ENSFEA, Université Toulouse 3 Paul Sabatier, CNRS, UMR5174 EDB (Laboratoire Évolution et Diversité Biologique), Castanet-Tolosan, France

Overwintering aggregations are part of Hippodamia undecimnotata’s (Coleoptera: Coccinellidae) mating system

  • Eline Catherine Susset, 
  • Jean-Louis Hemptinne, 
  • Etienne Danchin, 
  • Alexandra Magro


Aggregation during diapause is a common phenomenon in arthropods that nevertheless remains poorly understood. The most commonly claimed benefit is that survival is higher in aggregations but animal aggregations could also be driven by sexual selection. In this perspective, we investigated whether aggregations in insects could be part of their mating system. We studied the overwintering aggregations of the ladybird Hippodamia undecimnotata (Schneider), an aphidophagous species from Southern and Eastern Europe as well as Asia. We collected ladybirds at three aggregation sites in Southwest France, during two overwintering periods (2013–2014 and 2014–2015). We checked their reproductive status by counting the viable sperm cells in the sperm storage organs of both males and females, and by assessing the ovarian status of females. We also investigated if mating behaviour occurred in these aggregations. We found that males have a high quantity of viable sperm cells (70–95%) in their reproductive organs throughout the overwintering periods. In contrast, although most females (85–95%) had empty spermatheca at the onset of the aggregations in autumn, the majority (65–91%) had numerous viable sperm in their spermatheca at the time of dispersal from the aggregation in early spring. Furthermore, frequent copulations were observed towards the end of the overwintering period, few weeks before dispersal. These results suggest that finding sexual mates may have been involved in overwintering aggregations in H. undecimnotata.


Group living is a common feature in the animal kingdom [13] and animal aggregations are often temporary and seasonal. In arthropods, seasonal aggregations generally consist of monospecific clusters, sometimes of high numbers of individuals for several months, and are located in the same places year after year [e.g. 49]. One of the most famous cases is the spectacular meetings of the monarch butterfly Danaus plexippus (L.) (Lepidoptera: Nymphalidae) in the forests of Mexico and Florida [5]. Nevertheless, although seasonal aggregations are a fascinating phenomenon, ultimate mechanisms for their formation are still poorly understood [1012].

Seasonal aggregations are often concomitant with diapause (a hormonally-mediated arrest of development at a species-specific ontogenic state [13]), which is considered an insect’s main strategy to escape unfavourable seasons [14,15]. A first general assumption is that gathering in the course of diapause increases the protection of the relatively immobile individuals against predators [4,16] owing, for instance, to increased intensity of aposematic signals [17,18] or dilution effects [19]. Aggregations during diapause may also generate favourable microclimates [20,21]: they were shown to promote water conservation [2224] or increase temperature inside the group [23]. However, although the most common evolutionary approach underlying the formation of aggregations in insects has focused on survival, there are other major determinants of fitness that have been overlooked [4,25,26].

The hidden lek hypothesis states that animal aggregations can be driven by sexual selection and result from the settlement of promiscuous males on sites where they are most likely to encounter female mates [2729]. According to that hypothesis, by joining one particular site males and females are not looking for aggregation per se but for high quality individuals of the opposite sex [4]. This was shown to be the case for some animals [3032]. This view does not exclude that aggregations then convey other benefits but it posits that these benefits are not at the very origin of aggregations [33]. Although this hypothesis was developed for vertebrates, it is also valid in insects as female mating preferences are sometimes responsible of the formation of clusters in flies and other insects [34].

Worldwide, many ladybird (Coleoptera: Coccinellidae) species aggregate in response to seasonality (see reviews in [9, 35]), either hibernating and/or aestivating. Conventional wisdom has it that ladybirds aggregate either to regulate their microclimate, or to accentuate the aposematic signal sent to the predators, thus increasing survival (e.g. [33]). Nevertheless, no study has tested whether aggregated ladybirds survive better. Interestingly, Taylor (1984) [36] and Majerus (1994) [33] also mentioned that ladybirds could mate during overwintering aggregations. With Hagen (1962) [35] and Hodek and Landa (1971) [37], they noted that copulations often occur in overwintering aggregations in several species. Moreover, some authors found that females in aggregations had no sperm in the spermatheca at the beginning of diapause and that the proportion of females with sperm gradually increased over the course of the overwintering period [3740]. In addition, Hodek and Landa (1971) [37] showed that males had no or few spermatocytes in testicular follicles but had their seminal vesicle full of sperm cells from the beginning to mid-overwintering period. Then, males had fully mature spermatocytes in both their testicular follicles and their seminal vesicle at the end of the aggregation period. Their results are supported by Hemptinne and Naisse’ observations (1987) and Ceryngier et al. (2004) [39,40] who found that most males had inactive or intermediately active testes during the course of overwintering period; Hemptinne and Naisse (1987) [39] also noted that seminal vesicles were always full. That is, although there are observations that point out to the existence of mating during overwintering aggregations, there is no throughout study of its importance.

Our hypothesis is that ladybird overwintering aggregations can be part of their mating system, in the perspective of the hidden lek hypothesis. Indeed, being in the aggregation before dispersing in spring towards breeding sites should greatly increase odds of finding and choosing a compatible sexual partner. Here, as a first step to test that hypothesis, we investigated the extent to which and when mating occurs at the aggregation sites. To do so, we chose the ladybird Hippodamia (Semiadalia) undecimnotata (Schneider) as a model. This species has several synonyms (Ceratomegilla undecimnotata, Semiadalia undecimnotata) currently being used by different authors. Ślipiński (2007) [41] mentions there is indeed some lack of consensus about the generic limits in the Hippodamia-generic complex. Here we follow Fürsch (2007) and Iablokoff-Khnzorian (1982) [42,43] taxonomies as we did in previous papers on the same topic [44,45].

H. undecimnotata is an aphidophagous ladybird species from Southern and Eastern Europe, and Asia [43]. It exhibits large overwintering aggregations at the base of prominent objects located at the top of promontories [9,36,45,46]. Individuals gather at specific and long-used locations year after year eventually undertaking long migrations from breeding and feeding sites in lowlands to aggregation sites [9,36]. Depending on the climate and/or geographical range, overwintering of H. undecimnotata in its whole range takes place between September and May and lasts 5 to 9 months [9,36]. Shortening of day length, reduction of food availability and quality, and a general drop in temperatures induce diapause [4749].

We performed the first comprehensive, systematic study of both the proportion and viability (a precise measure of reproductive status not used before) of sperm cells in males and females, ovarian status of females and mating behaviour of H. undecimnotata, in several clusters, at different aggregation sites during two overwintering periods.

Material and methods

Study sites

The study took place over two consecutive overwintering periods at three sites in Southwest France: Labastide-Gabausse (LG, latitude: 44°2’N, longitude: 2°6’E, altitude: 260 m a.s.l.), Saint-Michel-de-Lanès (SML, latitude: 43°19’N, longitude: 1°45’E, altitude: 315 m a.s.l.), and Mont Seigne (MS, latitude: 44°12’N, longitude: 2°55’E, altitude: 1128 m a.s.l.). The study was carried out on private lands with the permission of the owners.

LG is an organic vineyard and ladybirds aggregate in cracks on the vine stocks present at the highest points. SML is situated on a conventional crop area dominated by wheat and maize and ladybirds aggregate at the base of a phone pole next to a road. MS is a heathland dominated by Calluna vulgaris Hull (Ericaceae), with low human disturbance during the winter and ladybirds aggregate in the crevices of two orientation tables.

In the study sites and in both overwintering periods, H. undecimnotata arrived at the aggregation sites from late October to early-November depending of the sites, and left from mid-April to late April. So, the study took place from November 2013 to April 2014 (Year 1), and from November 2014 to April 2015 (Year 2).

Field sampling of ladybird

We sampled ladybirds in the 3 aggregation sites, from the beginning to the end of the overwintering periods. Samples were taken in November, January, March, and April in both Years 1 and 2. For each aggregation site, samples were collected in two clusters at least 10 m apart from each other, except at SML where only 1 cluster was available.

We carefully collected the ladybirds with fine tweezers to avoid disturbing the remaining ladybirds. After sampling, we brought them to the laboratory in a portable fridge at 10°C and they were individually stored in vials in a climate-controlled room (10°C, Light:Darkness ratio 0:24 for 24h) until dissections.

Two hundred and ninety-seven males and 340 females and 408 males and 438 females were analysed in Year 1 and in Year 2, respectively.

Dissection of ladybirds and sperm collection

We sexed ladybirds under a stereo-microscope according to the shape of the distal abdominal sternites. We carried out dissections in a cavity slide the day following the sampling. The ventral tegument was teased apart with fine tweezers, and 100 μl of a phosphate-buffered saline (PBS) were added to avoid cytolysis and organ retraction. In males, we removed the reproductive organs (i.e. the testes and the seminal vesicle); in females, we removed the spermatheca and the bursa copulatrix. The remains of the ladybird body were removed from the cavity slide. We ruptured the whole reproductive organs to allow sperm release. As the spermatheca is a chitinous structure, we pressed it with forceps to eject the sperm. Then, we pipetted 100 μl of PBS containing the sperm from the cavity slide into a microcentrifuge tube. We washed the cavity slide with PBS (400 μl for males; 100 μl for females) that was added into the microcentrifuge tube. The tube was then vortexed at 600 RPM for 30 min. This allowed remaining sperm cells to leave the reproductive organs without increasing sperm mortality [50].

Sperm cell number

We counted sperm cells under a dark field phase contrast microscope at 400x magnification. We counted the number of sperm cells in two samples for each individual; count repeatability was high (Pearson’s correlation test: r = 0.82; P < 0.0001). The number of sperm cells detected in both samples was thus summed and multiplied by the dilution factor to estimate the total number of sperm cells. Twenty to 25 males and females were analyzed per sampling period for each site.

Sperm cell viability

Sperm cell viability assays were carried out following Damiens et al. (2002) [51] and García-González and Simmons (2005) [52]. We used the LIVE/DEAD® Sperm viability reagents (Molecular Probes). Ten μl of sperm were pipetted and mixed with an equal volume of 1:50 diluted 1 mM SYBR-14 (a permanent nucleic stain), and were left in the dark for 10 min before 2 μl of 2.4 mM propidium iodide was added. The sample was then incubated in the dark for 10 min and observed under a fluorescence microscope (blue excitation filter at λ = 490 nm). Live sperm cells were green stained with SYBR-14, a membrane permanent nucleic acid stain, while dead ones (i.e. with damaged membranes) were stained red with propidium iodide [5152] (Fig 1). To assess the repeatability of the measurement, sperm cells viability (the proportion of viable to non-viable sperm cells) was assessed in two samples for each of 21 ladybirds, and was found to be high (Pearson’s correlation test: r = 0.79; P < 0.0001).

Fig 1. Assay of sperm cell viability.

Live sperm cells are stained in green (indicated by grey arrows), dead sperm cells are stained in red (indicated by white arrows).

Ovarian status

We investigated the ovarian status for each female for which we had sperm cell numbers and viability. Ovarian development was scored on a 1 to 5 scale according to Okuda and Hodek (1989) [53]: stage 1: inactive ovary with ovarioles containing no oocytes; stage 2: ovarioles with the transparent oocytes; stage 3: ovarioles with small, vitellogenic oocytes; stage 4: ovarioles with vitellogenic oocytes; stage 5: ovarioles with mature oocytes.

Exhaustive sampling of females at the time of dispersal at LG site

We investigated the proportion of females leaving the aggregation site in a mated condition in a cluster that had not been used for the other parts of the study, at the LG site. We caught all dispersing ladybirds by means of an interception entomological trap. This trap, inspired by Sarthou (2009) [54], is an asymmetric tent with no ground sheet. The trap was set up to enclose a vine and was fitted tightly to the ground. It was set up in March 2014 and 2015 when the ladybirds were still immobile and densely packed, and removed in May once all the ladybirds had dispersed. The emerging insects were collected in a bottle at the top of the trap. The collecting bottle was checked 3 times a week and emptied when at least one ladybird was trapped. Ladybirds were brought back to the laboratory and their spermatheca and bursa copulatrix content analysed the following day, as described above. The results of this sampling correspond to the data given for LG in April in the “Number and viability of sperm cells in females” part of the Results section.

Ladybird behaviour at the LG aggregation site

We observed ladybird behaviour at each sampling period and once a week on a sunny day, from March to the beginning of May 2014 and 2015, at Labastide-Gabausse between 9:00 am and 6:00 pm. We performed control visits once a month during raining days to check whether mating occurred only during sunny days. In 2014, we followed two clusters of about 200 and 70 ladybirds each and recorded movements across the aggregation and mating events. In 2015, we followed one cluster of about 155 ladybirds. Mating ladybirds were marked with white paint (Edding®) on the elytra; paint dots lasted at least 2 months on elytra.

Statistical analyses

We analysed the differences in the proportion of males and females having viable sperm cells in their reproductive organs, as well as the differences in sperm cell number and viability, and the ovary maturation according to the Site, Period, Year, and Cluster variables with Generalized Linear Mixed Models (GLMMs). We assumed a binomial error distribution for the proportion of individuals with sperm cells and for sperm viability [55]. We used a penalized quasi-likelihood GLMM (glmmPQL) with quasi-Poisson error distribution for the sperm cell number; we investigated the differences in female ovary maturation with a GLMM assuming a Poisson error distribution. In all models, Period was entered as fixed effect while Site, Year, and Cluster were considered as random factors. Period was a 4-level ordered variable: November, January, March and April. Due to heavy rainfalls in March 2014, the aggregation site at SML was destroyed. So, the Site variable had only 2 levels in Year 1: LG and MS and 3 levels in Year 2: LG, MS, and SML.

In addition, we investigated the differences in the sperm cell number and viability in the females sampled in the last sampling period (i.e. April) according to Site, Year, and their interaction using a Generalized Linear Model (GLM) with a quasi-Poisson and a binomial error distribution, respectively to compare the number and viability of sperm cells across sites and years, respectively.

All analyses were conducted in the R (version [2.14]) environment [56], using the lme4 [57] and MASS [58] packages.


Numbers and viability of sperm cells in males

The proportion of males with sperm cells in their reproductive organs was high: between 78% and 100% of males had sperm cells in their reproductive organs (Table 1). Most of the time, all males had sperm cells in their reproductive organs (Table 1). The proportion of males with sperm cells in their reproductive organs did not vary in relation to the period of sampling (GLMM: χ23 = 4.50, P > 0.05).

Table 1. Sperm cells in male reproductive organs (sperm cell number/male).

Proportion of males with sperm cells, sperm cell number and viability during the two successive overwintering periods at the 3 study sites.

For Year 1, sperm cell number was the highest during the second half of the overwintering period. In Year 2, it was high in November 2014 and declined progressively until March and April 2015. However, the number of sperm cells increased in March 2015 before declining again in April at SML (Table 1). Nevertheless, when analysing only the correlation between the Period and the number of sperm cells in males, we found that the number of sperm cells did not vary according to the Period (quasi-Poisson GLMM: χ22 = 2.04, P > 0.05).

Finally, the viability of sperm cells in males ranged between 72.48 ± 3.78% and 92.5 ± 1.09% (Table 1). The viability of sperm cells in males did not vary between the periods of sampling (GLMM: χ23 = 0.33, P > 0.05).

Number and viability of sperm cells in females

The proportion of females with sperm in the spermatheca and the bursa copulatrix varied between the sampling periods (GLMM: χ23 = 12.02, P < 0.01). The proportion of females having sperm cells in their spermatheca and bursa copulatrix increased over the winter. The general trend was clear: few females were mated at their arrival at the aggregation sites. This persisted until March, and then most females were mated in April (Table 2). The exhaustive collection of departing females at LG showed that 91% and 83% out of 124 and 47 females in April 2014 and April 2015 respectively had sperm in their spermatheca and the bursa copulatrix.

Table 2. Sperm cells in female spermatheca and bursa copulatrix (sperm cell number/female).

Sperm cell number and viability during the two successive overwintering periods at the 3 study sites.

Regarding the total sperm cell numbers in the spermatheca and the bursa copulatrix in April we found a significant Site × Year interaction (quasi-Poisson GLM: F1,142 = 8.56; P < 0.01). In Year 1, LG females had a higher sperm load than MS females whereas in Year 2, LG females had the lowest sperm load compared to MS and SML females. The viability of sperm cells in April was also related to the Site × Year interaction (GLM: F1,139 = 26.08; P < 0.001). Nevertheless, sperm cell viability in the spermatheca and bursa copulatrix was high (> 80%) at the time of dispersal in both years (Table 2).

Ovarian status

The ovarian status varied between the sampling periods (GLMM: χ23 = 28.46; P < 0.001). In Year 1, females had immature ovaries (below stage 3) from their arrival at the aggregation site until January 2014 in all 3 locations. A higher proportion of females had ovaries containing vitellogenic oocytes in March. All dissected females in April 2014 had ovaries with vitellogenic oocytes (stage 3 and beyond) (Fig 2). In Year 2, although some females had ovaries with vitellogenic oocytes (i.e. at stage 3) in November, the majority of them had immature ovaries all over winter and spring even when leaving the aggregation (Fig 3).

Fig 2.

Stages of maturation of the ovaries of Hippodamia undecimnotata in relation to the sampling locations and periods 2013–2014 at a) SML, b) LG, and c) MS. In March 2014, only 5 females were sampled at SML due to site destruction.

Fig 3.

Stages of maturation of the ovaries of Hippodamia undecimnotata in relation to the sampling locations and periods 2014–2015 at a) SML, b) LG, and c) MS.

Ladybird behaviour at the LG aggregation site

In both 2014 and 2015, the first walking ladybirds were observed at the beginning of February. Before that, ladybirds remained immobile and densely packed inside the crevices. The first copulations took place in March.

In 2014, over 16 non-consecutive days (representing a total of 144 hours of observation), a total of 46 and 21 different couples out of more than 219 and 208 individuals were recorded in cluster 1 and cluster 2, respectively. No mating was observed during raining days (over 40 hours of observation).

In 2015, over 14 non-consecutive days (representing 126 hours of observations), a total of 25 couples out of about 155 individuals were recorded.


The evolutionary significance of the overwintering aggregations of arthropods is far from clear. We tested the hypothesis that arthropods usually scattered in breeding and feeding habitats aggregate during the harsh season to mate before dispersing towards breeding sites. In this perspective, we thoroughly studied the sexual activity of H. undecimnotata during the overwintering aggregation.

Most males at the aggregation sites had sperm cells

We found that 78 to 100% of the males had several hundreds of thousands of viable sperm cells in their reproductive organs for the whole of the two consecutive overwintering periods. Interestingly, we found that males from all the clusters arrived at the aggregation sites with viable sperm cells, indicating they had mature reproductive organs and were thus physiologically able to inseminate females. These results are in accordance with observations from Hodek and Landa (1971) [37] and Ceryngier et al. (2004) [40] for the same species: they found testis resorption but seminal vesicle filling during the first part of the aggregation period. The H. undecimnotata populations studied by those authors come from Central Europe and these differences might be due to ecological plasticity in terms of dormancy as it happens for C. septempunctata [59].

Finally, we noticed that in most cases sperm cell numbers decreased just before dispersal in year 2 which may suggest that many mating events occurred at the aggregation. Sperm production is energetically costly [60], and therefore we hypothesize that if males mated they might have had no opportunity to renew their sperm stock at the aggregation site.

Females arrived with empty tracts but left loaded with sperm cells

At the onset of the overwintering period in November, most females had an empty spermatheca and bursa copulatrix indicating they were not mated. For the less than 15% having sperm cells in these organs, we suggest two explanations. First, those females had been inseminated during the rare early copulations observed in the beginning of the aggregation. Alternatively, one cannot exclude that some of those females might have been mated during the previous breeding season or even during the previous overwintering period, several months before, ladybirds being able to store sperm for up to 8 months [61]. Indeed, some H. undecimnotata might survive long enough to join the aggregation sites more than once as it was reported for other ladybird species such as Harmonia axyridis (Pallas) or Henosepilachna pustulosa (Kôno) (see [6264] and review in [9]).

We also found that the proportion of females with sperm cells increased over the winter, reaching 65 to 91%, upon leaving the aggregations. These results confirm previous observations made in one population by Hodek and Landa (1971) [37] and Ceryngier et al. (2004) [40]. Moreover, our original study of sperm quantity and viability in females’ reproductive tracts showed an increase in the number of sperm cells throughout the overwintering period. Therefore, our results strongly suggest that mating takes place before leaving the aggregation.

Mating was common at the aggregation sites toward the end of the overwintering period

We observed that mating occurred at the aggregation sites, in agreement with the observations of Hodek and Landa (1971) [37], Tanaka et al. (1987) [65], and Ceryngier et al. (2004) [40] incidental observations. It happened despite the fact that most females had immature ovaries. El Hariri (1966), Hodek and Landa (1971), Hemptinne and Naisse (1987) and Ceryngier et al. (2004) [37,39,40,66] had previously observed that ovaries stay immature during the overwintering period. These results are in accordance with the fact that ovarian maturation is not a prerequisite for the onset of mating in coleopterans [65,67].

More importantly, the frequency of mating in March-April just before aggregation breaks was particularly high. It happened when both sperm cell number and viability in male gonads and female organs were the highest. These results further suggest that mating is a significant activity at the aggregation sites before dispersal to breeding sites.

Altogether, our results strongly support the hypothesis that overwintering aggregations are part of the mating strategy of H. undecimnotata.

Aggregation site features and mating system characteristics

By aggregating and mating during the overwintering period on the top of promontories [9,36,45], H. undecimnotata behaves like hilltopping insects [67]. Hilltopping is a mate-locating strategy akin to a lek [67,68] in which insects head for topographical summits or prominent features to meet with their potential mates [67]. The constancy of the aggregation sites and their prominent features, comparable to landmarks, probably ease mate finding [69]. This mating strategy should be more thoroughly investigated for H. undecimnotata and should be more thoroughly investigated. For instance, it remains to be studied if the sex-ratio in ladybirds is biased at the beginning of the overwintering period, which is a key feature of the hilltopping system [70].

Conclusion: are overwintering aggregations sexually driven?

It is frequently explained that arthropods aggregate in winter or the dry season because they would survive better. The adaptive nature of this behaviour was the paradigm for the evolution of animal aggregations, and remained accepted uncritically. However, the observation that mate choice occurs in and has the potential to drive bird colonies and lizard groups opens other perspectives [71,72]. More generally, Danchin and Wagner (1997) [25] suggested that the origin of animal aggregations may be a by-product of selection acting on the many choice processes necessary to survive and breed rather than on the direct advantages of aggregation. That ladybird’s sexual activity takes place so intensely at the aggregation sites in winter lends some support to Danchin and Wagner’s views, and is a strong incentive to further explore the mating system of these insects in relation with aggregation behaviour.


The authors thank Alain Jauneau and his collaborators of the Imagery Platform of the Fédération de Recherche “Agrobiosciences, Interactions et Biodiversité” for their kind help during the microscopic observations. They also thank Christophe Bressac and Francisco García-González for their scientific advices, Jean-François Garrigues, and Nathalie Dardenne for technical assistance, and Célia Nave for her help in protocol design. We thank the three anonymous reviewers for their helpful comments on the manuscript.


  1. 1. Krause J, Ruxton GD (2002) Living in Groups. Oxford University Press.
  2. 2. Parrish JK, Edelstein-Keshet L (1999) Complexity, pattern, and evolutionary trade-offs in animal aggregation. Science 284: 99–101. pmid:10102827
  3. 3. Parrish JK, Hamner WM (1997) Animal groups in three dimensions: how species aggregate. Cambridge, Cambridge Press University.
  4. 4. Holmberg RG, Angerilli NPD, LaCasse LJ (1984) Overwintering aggregations of Leiobunum paessleri in caves and mines (Arachnida, Opiliones). J Arachnol 12: 195–204.
  5. 5. Malcolm SB, Zalucki PM (1993) Biology and conservation of the monarch butterfly Natural History Museum of Los Angeles County, Los Angeles.
  6. 6. Roubik DW, Skelley PE (2001) Stenotarsus subtilis Arrow, the aggregating fungus beetle of Barro Colorado island nature monument, Panama (Coleoptera: Endomychidae). Coleopt Bull 55: 249–263.
  7. 7. Toyama M, Ihara F, Yaginuma K (2006) Formation of aggregations in adults of the brown marmorated stink bug, Halyomorpha halys (Stål) (Heteroptera: Pentatomidae): the role of antennae in short-range locations. Appl Entomol Zool 41: 309–315.
  8. 8. Dzerefos CM, Witkowski ETF, Toms R (2009) Life-history traits of the edible stinkbug, Encosternum delegorguei (Hemiptera, Tessaratomidae), a traditional food in southern Africa. J Appl Entomol 133: 749–759.
  9. 9. Hodek I (2012) Diapause/Dormancy. In: Hodek I, Van Emden HF, Honěk A. 2012. Ecology and behaviour of the ladybird beetles (Coccinellidae). Wiley-Blackwell, Chichester, West Sussex.
  10. 10. Kitching RL, Zalucki MP (1981) Observations on the ecology of Euploea core corinna (Nymphalidae) with special reference to an overwintering population. J Lepidopt Soc 35: 106–119.
  11. 11. Wells H, Wells PH, Cook P (1990). The importance of overwintering aggregation for reproductive success of monarch butterflies (Danaus plexippus L.). J Theor Biol 147: 115–131.
  12. 12. Sabu TK, Vinod KV, Jobi MC (2008) Life history, aggregation and dormancy of the rubber plantation litter beetle, Luprops tristis, from the rubber plantations of moist south Western Ghats. J Insect Sci 8: 1–17.
  13. 13. Koštál V (2006) Eco-physiological phases of insect diapause. J Insect Physiol 52: 113–127. pmid:16332347
  14. 14. Danks HV (1987) Insect dormancy: an ecological perspective. Biological Survey of Canada monograph, series n°1.
  15. 15. Bradshaw WE (1990) Evolution of life-cycle traits. In: Francis G. (ed) Insect life cycles. Genetics, evolution and co-ordination. Springer-Verlag, London, UK: 43–67.
  16. 16. Monteith GB (1982) Dry season aggregations of insects in Australian monsoon forests. Memoirs Queensland Museum. 20: 533–543
  17. 17. Pasteels JM, Grégoire JC, Rowell-Rahier M (1983) The chemical ecology of defence in arthropods. Annu Rev Entomol 28: 263–289.
  18. 18. Beatty CD, Bain RS, Sherratt TN. 2005. The evolution of aggregation in profitable and unprofitable prey. Anim Behav 70: 199–208.
  19. 19. Vulinec K (1990) Collective security: aggregation by insects as a defence. In: Evans DL, Schmidt JO. (eds) Insect defences: adaptive mechanisms and strategies of prey and predators. State University of New York Press, Albany.
  20. 20. Brower LP, Williams EH, Fink LS, Zubieta RR, Ramírez MI (2008) Monarch butterfly clusters provide microclimatic advantages during the overwintering season in Mexico. J Lepidopt Soc 62: 177–188.
  21. 21. Tanaka S, Wolda H, Denlinger DL (1988) Group size affects the metabolic rate of a tropical beetle. Physiol Entomol 13: 239–241.
  22. 22. Klok CJ, Chown SL (1999) Assessing the benefits of aggregation: thermal biology and water relations of anomalous Emperor Moth caterpillars. Funct Ecol 13: 417–427.
  23. 23. Yoder JA, Denlinger DL, Wolda H (1992) Aggregation promotes water conservation during in the tropical fungus beetle, Stenotarsus rotundus. Ent Exp Appl 63: 203–205.
  24. 24. Pullin AS (1996) Physiological relationships between insect diapause and cold tolerance: coevolution or coincidence. Eur J Entomol 93: 121–129.
  25. 25. Danchin E, Wagner RH (1997) The evolution of coloniality: the emergence of new perspectives. Trends Ecol Evol 12: 342–347. pmid:21238100
  26. 26. Doligez B, Cadet C, Danchin E, Boulinier T (2003) When to use public information for breeding habitat selection? The role of environmental predictability and density dependence. Anim Behav 66: 973–988.
  27. 27. Bradbury J, Gibson R, Tsai IM (1986) Hotspots and the dispersion of leks. Anim Behav 34: 1694–1709.
  28. 28. Wagner RH (1993) The pursuit of extra-pair matings by female birds: a new hypothesis of colony formation. J Theor Biol 163: 333–346.
  29. 29. Wagner RH (1998) Hidden leks: sexual selection and the clustering of avian territories. Ornithol Monogr 49: 123–145.
  30. 30. Tarof SA, Ratcliffe LM, Kasumovic MM, Boag PT (2005) Are least flycatchers (Empidonax minimus) clusters hidden leks? Behav Ecol 16: 207–217.
  31. 31. Cockburn A, Dalziell AH, Blackmore CJ, Double MC, Kokko H, Osmond HL, et al. (2009) Superb fairy-wren males aggregate into hidden leks to solicit extragroup fertilizations before dawn. Behav Ecol 20: 501–510.
  32. 32. Schütz D, Wirtz Ocana S, Maan ME, Taborsky M (2016) Sexual selection promotes colonial breeding in shell-brooding cichlid fish. Anim Behav 112: 153–161.
  33. 33. Majerus MEN (1994) Ladybirds. HarperCollins, London.
  34. 34. Isvaran K, Ponkshe A (2013) How general is a female mating preference for clustered males in lekking species? A meta-analysis. Anim Behav 86: 417–425.
  35. 35. Hagen KS (1962) Biology and ecology of predaceous Coccinellidae. Ann Rev Entomol 7: 289–326.
  36. 36. Taylor F (1984) Mexican bean beetles mate successfully in diapause. Int J Inver Rep Dev 7: 297–302.
  37. 37. Hodek I, Landa V (1971) Anatomical and histological changes during dormancy in two coccinellidae. Entomophaga 16: 239–251.
  38. 38. Kreiter S, Iperti G, Giuge L (1984) Rôle des sommets dans la protection d'un prédateur aphidiphage: Semiadalia undecimnotata SCH., (Coleoptera, Coccinellidae). Tr Mus Hist Nat Grigore Antipa 25: 151–165 (in French).
  39. 39. Hemptinne JL, Naisse J (1987) Ecology of the reproductive activity of Adalia bipunctata L. (Coleoptera, Coccinellidae). Med Fac Landbouww Rijksuniv Gent 52: 225–233.
  40. 40. Ceryngier P, Havelka J, Hodek I (2004) Mating and activity of gonads in pre-dormant and dormant ladybirds (Coleoptera: Coccinellidae). Invert Reprod Dev 45: 127–135.
  41. 41. Ślipiński A (2007) Australian ladybird beetles (Coleoptera: Coccinellidae): their biology and classification. Australian Biological Resources Study, Canberra.
  42. 42. Fürsch H (2007) Taxonomy of Coccinellids. Corrected version of Coccinella 6 (1996).
  43. 43. Iablokoff-Khnzorian SM(1982) Les Coccinelles, Coléoptères-Coccinellidae: tribu Coccinelli des régions Paléarctique et orientale. Boubée, Paris.
  44. 44. Susset EC, Magro A, Hemptinne J-L (2017) Using species distribution models to locate animal aggregations: a case study with Hippodamia undecimnotata (Schneider) overwintering aggregation sites. Ecol entomol 42: 345–354.
  45. 45. Susset EC, Hemptinne J-L, Magro A (2017) Overwintering sites might not be safe haven for Hippodamia undecimnotata (Schneider) (Coleoptera: Coccinellidae). The Coleopterists’ Bulletin 71: 556–564.
  46. 46. Hodek I (1960) Hibernation-bionomics in Coccinellidae. Čas Čsl Spol Entomol 57: 1–20.
  47. 47. Rolley F, Hodek I, Iperti G (1974) Influence de la nourriture aphidienne (selon l’âge de la plante-hôte à partir de laquelle les pucerons se multiplient) sur l’induction de la dormance chez Semiadalia undecimnotata Schn. (Coleoptera, Coccinellidae). Ann Zool Ecol Anim 6: 53–60. (In French).
  48. 48. Iperti G, Hodek I (1976) Développement de la diapause chez les femelles de Semiadalia undecimnotata (Schneider). Ann Zool Ecol Anim 8: 17–24. (In French).
  49. 49. Hodek I, Iperti G (1983) Sensitivity to photoperiod in relation to diapause in Semiadalia undecimnotata females. Ent Exp Appl 34: 9–12.
  50. 50. Gress BE, Kelly CD (2011) Is sperm viability independent of ejaculate size in the house cricket (Acheta domesticus)? Can. J. Zool 89(12): 1231–1236.
  51. 51. Damiens D, Bressac C, Brillard JP, Chevrier C (2002) Qualitative aspects of sperm stock in males and females from Eupelmus orientalis and Dinarmus basalis (Hymenoptera: Chalcidoidea) as revealed by dual fluorescence. Physiol Entomol 27: 97–102.
  52. 52. García-González P, Simmons LW (2005) Sperm viability matters in insect sperm competition. Current Biol 15: 271–275.
  53. 53. Okuda T, Hodek I (1989) Flight tendency of 2 coccinellids, Semiadalia undecimnotata, and Coccinella septempunctata, in relation to diapause. In: Tonner M., Soldán T., Bennettová B. (eds): Regulation of Insect Reproduction IV. Academia, Prague, pp. 385–400.
  54. 54. Sarthou JP (2009) Le piège cornet unidirectionnel, nouveau piège entomologique d’interception. L’Entomologiste 2: 107–108. (In French).
  55. 55. Zuur AF, Ieno EN, Walker NJ, Saveliev AA, Smith GM (2009) Mixed effects models and extensions in ecology with R. Springer, Stanford, USA.
  56. 56. R Development Core Team (2012) R: a language and environment for statistical computing. Version 2.14. R Foundation for Statistical Computing, Vienna, Austria.
  57. 57. Bates D, Maechler M, Dai B (2008) The lme4 Package. <>
  58. 58. Ripley B, Bates D, Hornik K, Gebhardt A, Firth D (2015) Package ‘MASS’ Available at:
  59. 59. Güven O, Göllüoğlu H, Ceryngier P (2015) Aestivo-hibernation of Coccinella septempunctata (Coleoptera: Coccinellidae) in a mountainous area in southern Turkey: is dormancy at high altitudes adaptive? Eur J Entomol 112(1): 41–48.
  60. 60. Perry JC, Tse CT (2013) Extreme costs of mating for male two-spot ladybird beetles. PloS One 8: 1–5.
  61. 61. Awad M, Kalushkov P, Nedvědová T, Nedvěd O (2013). Fecundity and fertility of ladybird beetle Harmonia axyridis. BioControl 58: 657–666.
  62. 62. Savoiskaya GI (1970) Coccinellids in the Alma-Ata reserve. Trudy Alma-Atinskogo Gosudarstvenogo Zapovednika 9: 163–187. (In Russian).
  63. 63. Awad M, Laugier GJM, Loiseau A, Nedvěd O (2015) Unbalanced polyandry in wild-caught ladybirds Harmonia axyridis (Coleoptera: Coccinellidae). Appl Entomol Zool 50: 427–434.
  64. 64. Nakamura K, Ohgushi T (1979) Studies on the population dynamics of a thistle-feeding lady beetle, Henosepilachna pustulosa (Kôno) in a cool temperature climax forest. Res Popul Ecol 20: 297–314.
  65. 65. Tanaka S, Wolda H, Denlinger DL (1987) Abstinence from mating by sexually mature males of the fungus beetle, Stenotarsus rotundus, during a tropical dry season. Biotropica 19: 252–254.
  66. 66. El Hariri G (1966) Studies of the physiology of hibernating Coccinellidae (Coleoptera): changes in the metabolic reserves and gonads. Physiol Entomol 41: 10–12.
  67. 67. Alcock J (1987) Leks and hilltopping in insects. J Nat Hist 21: 319–328.
  68. 68. Bradbury JW (1981) The evolution of leks. In: Alexander RD, Tinkle DW (eds). Natural Selection and Social Behavior, Recent Research and New Theory, pp. 138–173. New York, Chiron Press.
  69. 69. Cuddington K, Hull ZT, Currie WJS, Koops MA (2015) Landmarking and strong Allee thresholds. Theor Ecol 8: 333–347.
  70. 70. Capinera JL, Skevington JH (2008) Hilltopping. In: Capinera JL (editor). Encyclopedia of Entomology, Second edition. Kluwer Academic Publisher.
  71. 71. Stamps JA (1988) Conspecific attraction and aggregation in territorial species. Am Nat 131: 329–347.
  72. 72. Wagner RH, Danchin E, Boulinier T, Helfenstein F (2000) Colonies as byproducts of commodity selection. Behav Ecol 11: 572–573.