Research Article |
Corresponding author: Gema Trigos Peral ( getriral@gmail.com ) Academic editor: Jack Neff
© 2016 Gema Trigos Peral, Bálint Marko, Hania Babik, Ionut Tăuşan, István Maák, Zsófia Pálfi, Piotr Ślipiński, Zsolt Czekes, Wojciech Czechowski.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Trigos Peral G, Markó B, Babik H, Tăuşan I, Maák I, Pálfi Z, Ślipiński P, Czekes Z, Czechowski W (2016) Differential impact of two dominant Formica ant species (Hymenoptera, Formicidae) on subordinates in temperate Europe. Journal of Hymenoptera Research 50: 97-116. https://doi.org/10.3897/JHR.50.8301
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Competition is one of the basic mechanisms shaping ant assemblages. Dominant territorial species are known to restrictively influence the traits of subordinates in various ways. However, there could be differences in the effects of dominants due to differences in their colony structure, lifestyle and also behaviour. We tested this hypothesis in natural circumstances in an area where a Formica exsecta Nyl. supercolony neighbours a strong population of the European slave-maker F. sanguinea Latr. For the purpose of our study three different sites were selected: one dominated by F. exsecta, a neighbouring site dominated by F. sanguinea, and a third site where both species co-occurred. We analyzed the structure of subordinate ant communities based on nest counts, and by recording the activity of ants at baits. Based on our findings the structure of ant communities differed significantly among the three sites. The F. exsecta site was characterized by the lowest nest density of subordinates, especially in the case of aggressive species as Lasius platythorax Seifert. At baits even the simple presence of the dominant limited the abundance and occurrence of subordinates. In contrast, no such negative effect could be revealed at the F. sanguinea site. The community of the mixed site showed intermediate features in many respects. Generally, the supercolonial F. exsecta had a bigger influence on the ant community than the slave-making F. sanguinea. On the other hand, our findings revealed a slight protective role of the territorial F. exsecta for potential slave species to F. sanguinea. The current study underlines the importance of differences between dominant ant species in shaping differentially ant communities even within the same restricted area.
Formica exsecta , Formica sanguinea , baits, community structure, competition, interspecific hierarchy, nest density, slavery, territoriality
Most of the concepts regarding the assembly rules of animal communities point to competition as a crucial factor in shaping their composition and structure (
Typically, at least in Euro-Asian boreal and temperate zones, the top dominants of ant communities are territorial species (sensu
Within subordinates, two competition levels are distinguished: (a) encounter species, which are fairly aggressive and usually manage to monopolize (defend) single food sources, and (b) submissive species, which defend only their nests (
The differences among dominant species regarding their effect on subordinates may vary depending on their lifestyle (slave-maker vs non-slave-maker), colony structure (mono- vs polydomous), and on their foraging strategies (narrow vs wide food spectrum). The differential effect of dominants on subordinates are best revealed when dominant species occur syntopically (in the same habitat), consequently, the basic species pool that could make up the ant community is the same. Therefore, if the differences between the dominants are negligible, the differences between the ant communities occurring in their territories/areas should also be minor. In order to test this hypothesis, an appropriate natural set-up is needed, with the long-term co-occurrence of territorial allospecific neighbours (see e.g.
The main subjects of the study are two dominant ant species: Formica (Coptoformica) exsecta and Formica (Raptiformica) sanguinea.
Formica exsecta is a fairly common North-Palaearctic mound-building territorial species, a typical forest-ecotone polytope dwelling in forest margins and clearings, thinned young growth, overgrowing meadows and glades, etc. Its colonies number several thousand to tens of thousands of workers and occur in two, mono- and polygynous social forms. Polygynous colonies may grow through nest splitting into polydomous systems, often with more than 100 nests (so-called supercolonies). Additionally, colonies may be established through the temporary social parasitism of members of the subgenus Serviformica. The optimal home range of foraging workers from a single nest does not exceed a few meters. They are aggressive and predacious ants, which also feed on honeydew (
Formica sanguinea is a common South-Palaearctic species, a polytope of warm and dry habitats, both forested and open areas; generally its ecological preferences widely overlap with those of the former species. It nests in decaying tree stumps, partly covered with dry plant material and also in the ground, often under stones. In general, colonies, usually functionally monogynous, number up to several tens of thousands of workers. It is a facultative socially parasitic species which enslaves workers of the subgenus Serviformica; the range of its slave raids may reach 100 m (usually < 50 m). They are very aggressive and predatory ants; during their raiding period they do not respect the boundaries of other species’ territories (
As habitat niches of Formica exsecta and F. sanguinea overlap each other to a considerable degree, colonies of these two species often co-occur.
Our study area was a vast semi-moist meadow of the Molinion caeruleae W. Koch alliance [with, among others, Molinia caerulea (L.) Moench, Deschampsia caespitose (L.) P. B., Festuca pratensis Huds., Nardus stricta L. and Juncus sp.], densely overgrown with small birch saplings, located in the southern part of the Giurgeului depression (46°36'N; 25°36'E; 780 m a.s.l.) in the eastern Carpathians, Transylvania, Romania. The meadow is fairly intensely grazed by cows for most of the year. This is the location of the largest known European polydomous system of Formica exsecta. The supercolony contains 3,347 permanent nests over an area of nearly 22 ha (i.e. the nest density is ca. 153/ha) (
Three sites were selected within the area for the purpose of our study (Fig.
The study area was not part of any nature protection area and no specific permits were required to carry out the field studies.
Nest densities of different subordinate ant species were obtained using the biocoenometric method, by carefully investigating 15 quadrats of 9 m2 at each of the three study sites. The quadrats were randomly selected by a blindfolded person in the field, they did not border each other, and they were at least 2 m from any Formica exsecta nest (Fig.
Baiting is commonly used to study the foraging pattern of ants around their nests and species’ foraging strategies. It is also an appropriate method for determining the hierarchical positions of particular species within an assemblage (e.g.
The differences in the abundance of different ant species among sites were revealed by the use of the Kruskal-Wallis test, followed by Tukey and Kramer post-hoc tests. The diversity of ant communities was calculated with the Shannon-Wiener entropy index (log2), using data for individual quadrats and baits respectively for nest count and bait data, while differences among sites for these parameters were revealed by using the Kruskal-Wallis test, followed by the Tukey and Kramer post-hoc tests separately for nest count and bait data. In order to determine the differences among the ant assemblages of the three sites, permutational multivariate ANOVA (perMANOVA, 10000 permutations) was applied both for nest count and bait data, while Nonmetric Multidimensional Scaling (NMDS) was used to visualize the three assemblages, both in the case of nest and bait data. The SIMPER test was performed to determine the contribution of each species to dissimilarities between ant communities.
The Generalized Linear Mixed Model approach (GLMM, binomial, maximum likelihood) was applied to analyze the effect of dominant species on the presence and absence of subordinate species at baits. The abundance of Formica sanguinea and F. exsecta workers present at baits were introduced as variables, along with their presence vs absence data as factors, next to the type of the site (F. sanguinea, F. exsecta, mixed) as a factor. The period and time of the observation as well as bait ID were introduced as nested random factors. A similar approach (GLMM, Poisson error, maximum likelihood) was applied to separately test the effect of dominants on the abundance of subordinates. The number of all subordinates was pooled together, since they showed a low abundance separately (see the Results). The same model structure was used as above.
All statistical analyses were carried out using the R 3.1.2 statistical package (R Core Team 2015). Multiple pairwise comparisons in the case of the Kruskal-Wallis tests concerning diversity indices were performed using the Tukey and Kramer post-hoc test after Nemenyi with the PMCMR R-package (
During the quadrat survey, 171 nests were found belonging to 11 subordinate ant species in addition to the two dominant species (i.e. Formica sanguinea and F. exsecta) (Table
Nest densities (mean number per 9 m2 ± SD) of subordinate ant species and their proportions (%) in the three study sites.
Species | F. sanguinea site | F. exsecta site | Mixed site |
---|---|---|---|
mean ± SD % |
mean ± SD % |
mean ± SD % |
|
Tetramorium cf. caespitum (L.) | 0.33 ± 0.49 6.4 |
0.2 ± 0.56 7 |
0.67 ± 1.05 20 |
Leptothorax acervorum (F.) | – | 0.07 ± 0.26 2.3 |
– |
Myrmica scabrinodis Nyl. | 1.13 ± 1.13 21.8 |
0.53 ± 0.92 18.6 |
0.73 ± 1.1 22 |
Myrmica vandeli Bondr. | 0.47 ± 0.99 9.0 |
0.47 ± 0.74 16.3 |
0.13 ± 0.35 4.0 |
Myrmica schencki Viereck | 0.27 ± 0.8 5.1 |
0.07 ± 0.26 2.3 |
0.13 ± 0.35 4 |
Myrmica lobicornis Nyl. | – | 0.13 ± 0.35 4.7 |
0.07 ± 0.26 2 |
Myrmica ruginodis Nyl. | 0.07 ± 0.26 1.3 |
– | – |
Lasius flavus (F.) | 2.00 ± 1.81 38.5 |
1.33 ± 1.54 46.5 |
1.40 ± 0.99 42 |
Lasius platythorax Seifert | 0.87 ± 0.74 16.7 |
0.07 ± 0.26 2.3 |
– |
Formica cunicularia Latr. | 0.07 ± 0.26 1.3 |
– | 0.13 ± 0.35 4 |
Formica rufibarbis F. | – | – | 0.07 ± 0.26 2 |
All subordinate species | 5.21 | 2.87 | 3.33 |
All epigean subordinate species | 3.21 | 1.54 | 1.93 |
Only three aggressive encounter species were found: Lasius platythorax, Tetramorium cf. caespitum and Formica rufibarbis, and none of them were present in high densities at the site (territory) of F. exsecta. The three sites differed mainly in the nest density of two encounter species: L. platythorax and T. cf. caespitum (Table
The ant community of the Formica sanguinea site was significantly more diverse than the F. exsecta site, while the mixed site had an intermediate position (Kruskal-Wallis χ2 = 7.83, p = 0.02; Fig.
Results of the SIMPER analysis: the overall dissimilarity between study sites, the average contribution of subordinated ant species to overall dissimilarity (Dissimilarity contribution), their mean abundances in the compared sites (Mean 1 and Mean 2), and the cumulative percentages of contributions.
Sites (dissimilarity) | Species | Dissimilarity contribution (%) | Mean 1 | Mean 2 | Cumulative contribution (%) |
---|---|---|---|---|---|
F. sanguinea vs. F. exsecta (70.13) |
L. flavus | 20.95 | 2 | 1.54 | 29.88 |
M. scabrinodis | 13.49 | 1.13 | 0.62 | 49.13 | |
L. platythorax | 12.27 | 0.87 | 0.08 | 66.63 | |
M. vandeli | 9.44 | 0.47 | 0.54 | 80.11 | |
T. cf. caespitum | 6.13 | 0.33 | 0.23 | 88.85 | |
F. sanguinea vs. Mixed (67.83) |
L. flavus | 18.83 | 2 | 1.5 | 27.76 |
M. scabrinodis | 13.11 | 1.13 | 0.78 | 47.1 | |
L. platythorax | 12.21 | 0.87 | 0 | 65.11 | |
T. cf. caespitum | 9.33 | 0.33 | 0.71 | 78.88 | |
M. vandeli | 6.18 | 0.47 | 0.14 | 88 | |
F. exsecta vs. Mixed (65.81) |
L. flavus | 20.35 | 1.54 | 1.5 | 30.92 |
M. scabrinodis | 14.38 | 0.62 | 0.79 | 52.79 | |
T. cf. caespitum | 11.16 | 0.23 | 0.71 | 69.75 | |
M. vandeli | 8.48 | 0.54 | 0.14 | 82.64 | |
M. schencki | 3.46 | 0.08 | 0.14 | 87.91 |
Besides Formica sanguinea and F. exsecta, foragers of other species were also present at the baits (Table
Mean number of ant individuals per baits (± SD) for each study site and their relative proportions (%) to other ant species at the same site.
Species | F. sanguinea site | F. exsecta site | Mixed site |
---|---|---|---|
mean ± SD % |
mean ± SD % |
mean ± SD % |
|
Tetramorium cf. caespitum | 31.6 ± 96.78 36.5 |
– | 10.6 ± 21.49 32.0 |
Myrmica spp. | 2.1 ± 3.96 2.4 |
0.2 ± 0.42 0.1 |
4.0 ± 3.83 12.1 |
Lasius platythorax | 52.2 ± 83.48 60.3 |
52.2 ± 120.86 29.6 |
– |
Formica cunicularia | 0.6 ± 1.9 0.7 |
3.4 ± 4.03 1.9 |
1.8 ± 3.16 5.4 |
Formica sanguinea | 0.1 ± 0.32 0.1 |
– | 1.9 ± 2.56 5.7 |
Formica exsecta | – | 120.4 ± 100.65 68.3 |
14.8 ± 35.67 44.7 |
All subordinate species | 86.5 ± 111.43 | 55.8 ± 121.5 | 16.5 ± 22.75 |
99.9 | 31.6 | 49.7 | |
All species | 86.6 ± 111.35 | 176.6 ± 102.94 | 33.2 ± 36.19 |
100 | 100 | 100 |
Different trends were detected in the abundance of two aggressive (encounter) species: Lasius platythorax and Tetramorium cf. caespitum. The former occurred in similar numbers at baits in the Formica exsecta and F. sanguinea sites, whereas it was absent from the mixed site (Table
The highest diversity was found at baits in the mixed site (Kruskal-Wallis χ2 = 9.11, p = 0.011) followed by the significantly lower diversities of Formica sanguinea and F. exsecta sites, which did not differ significantly from each other based on the post-hoc test result (Fig.
According to the results of the GLMM analysis, Formica exsecta’s abundance (z = –3.09, p = 0.002) and presence (z = –2.32, p = 0.02) had a significant negative effect on the occurrence of subordinates at baits, while the abundance of F. sanguinea did not play a major role (z = –1.72, p = 0.08), but its presence did have a positive influence on the occurrence of subordinates (z = 2.13, p = 0.033). There were no differences between the F. sanguinea and the F. exsecta sites with regards to the frequency of the occurrence of subordinates (z = 1.99, p = 0.11). Also, no difference was found between the F. sanguinea and the mixed site in this respect (z = –1.8, p = 0.16), but subordinates were significantly less frequent at baits in the mixed site compared to the F. exsecta site (z = –3.18, p = 0.004).
Generally, a similar pattern with smaller adjustments was found when analyzing the effect of dominants on the abundance of subordinates at baits. In addition to the abundance of Formica exsecta (z = –8.33, p < 0.0001), even its simple presence (z = –2.01, p = 0.044) had a significant negative effect on the abundance of subordinates. On the other hand, F. sanguinea’s abundance (z = 0.04, p = 0.96) and presence (z = 0.96, p = 0.33) had no significant effect. The abundance of subordinates also showed significant differences among the three study sites (z ≥ 9.92, p < 0.0001).
The main factors which shape biodiversity and structure of animal communities are, besides habitat heterogeneity (see e.g.
The species composition of the studied ant communities was quite similar among all three sites, but differences were found in the abundance of different ant species, and also in the diversity of ant communities. In almost all respects the Formica sanguinea site was superior housing the most diverse ant community. Thus, despite the low chance of interaction with Lasius flavus due to its subterranean lifestyle, the lowest density of L. flavus nests was recorded in the Formica exsecta territory, which could be the result of the establishment of F. exsecta colonies on the top of their soil mounds, with the gradual extermination of L. flavus colonies (
Usually, the exploitation patterns of food resources at the Formica exsecta site was in agreement with the general rules concerning hierarchy patterns, where the dominant species, especially a territorial one, monopolizes the area and its resources (
The low number of Formica sanguinea foragers at baits, especially in relation to the numbers of workers of other ant species, requires additional explanations. Recent studies on the foraging strategy of F. sanguinea have already shown, that this species seems to be less competitive towards subordinates to the south (e.g. Romania) than in the northern parts of the species range in Europe (e.g. Finland) (P. Ślipiński et al., in prep). One of the major signs of its weaker competitiveness is its reduced presence at artificial baits, as also confirmed by our present observations. However, it is possible that at least some of the F. cunicularia workers present at baits were individuals enslaved by F. sanguinea, and these de facto acted as foragers of the latter. Since, generally, slaves fulfill intranest tasks in colonies (Kharkiv 1979a, b, see also
Territorial ants can hold off raiding columns of Formica sanguinea to some extent, and in this way directly protect possible slave species against their enslaver. This protective effect would manifest itself when there was a significantly greater abundance of slave species within, rather than outside of wood ant territories of the F. rufa group (
While the decisive effect of Formica exsecta as a typically territorial species on the structure of ant communities is quite evident, this question still remains open regarding F. sanguinea. In the literature, the latter is commonly handled in a similar manner as the territorial Formica s. str. and Coptoformica species (
The results of this study underscore the importance of differences between dominant ant species in differentially shaping ant communities, even within the same limited area.
We are indebted for the Apáthy István Society for the housing during the field works. The study was carried out with the support of scientific cooperation between the Polish Academy of Sciences and the Romanian Academy. This work was supported by a grant of the Romanian National Authority for Scientific Research and Innovation, CNCS – UEFISCDI, project number PN-II-RU-TE-2014-4-1930.