# Nesting Associations without Interdependence: A Preliminary Review on Plesiobiosis in Ants

Authors: Orsolya Kanizsai; Gábor Lőrinczi; László Gallé
Journal: Psyche
 (2013)

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## Abstract

Plesiobiosis, the most basic form of interspecific associations in ants, denotes occasional or regular nesting of heterospecific colonies of certain species pairs in close proximity to each other without biological interdependence. Plesiobionts differ from each other both in morphology and in behaviour (e.g., in their foraging strategies), and at least one of the plesiobiotic pair is a submissive species. Recent studies on plesiobiosis have revealed thatFormica fusca and Lasius flavus are two of the most frequent plesiobionts. To date, at least 48 different plesiobiotic species pairs have been recorded from various habitat types of the Holarctic region. Two main habitat properties may play a role in the forming of plesiobiosis: the scarcity of suitable nesting sites as a forcing factor and the sufficient amount of food sources available, influencing the abundance of colonies. Thus, high colony density may contribute to the formation of such associations, resulting in (1) frequent nesting in each other's neighbourhood and (2) stronger intraspecific competition, which forces colonies into the vicinity of heterospecific nests. Plesiobiotic associations formed this way may promote persistent coexistence, leading to the formation of other types of interspecific associations (e.g., clepto- or lestobiosis).


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## Body

## 1. Introduction

Various types of interspecific associations exist among ant species. These can be categorised on the basis of the degree of interactions between heterospecific colonies, ranging from simple cooccurrence with loose interaction to highly specialised social parasitism [1–3]. Following the suggestion by Wasmann [4] and Wheeler [5], Hölldobler and Wilson [6] distinguished two main types of associations between ant colonies, namely, “compound nests” and “mixed nests.” Associations belonging to “mixed nests” mostly result from social parasitism, where one of the species (as a social parasite) depends on its partner, which represents the host. On the other hand, the association types of “compound nests” differ from each other in the degree of interspecific relations ranging from neutral associations through mutualism and commensalism to typical parasitism.The vast majority of studies on interspecific associations in ants have focused on the forms of typical social parasitism (i.e., temporary parasitism, slavery, and inquilinism) [1, 3, 7–9] or on associations that belong to “compound nests” representing a higher degree of biological interdependence between heterospecific colonies (i.e., cleptobiosis, lestobiosis, xenobiosis, or parabiosis) ([10–20] etc.). However, few studies have dealt with plesiobiotic associations so far, and most of these reported only observations that might indicate the existence of such associations [5, 21–36].Although numerous classifications exist for associations related to “compound nests” [2, 4–6, 22, 37], most of them are based on relatively few reports [2]. According to each of the classification systems, plesiobiosis is the most rudimentary form of heterospecific associations. This type of association occurs between species pairs that differ from each other in morphology, in behaviour, and in taxonomy, and it denotes nesting close to each other without biological interdependence. Owing to this close proximity, plesiobiotic partners share not only the nesting shelter, but the same microhabitat, and possibly the foraging area as well.In this review our aim was to summarise the existing information on plesiobiosis, by listing and discussing (1) the recorded plesiobionts and plesiobiotic partner species and (2) the assumed background factors that may promote the formation and persistence of plesiobiotic associations. Furthermore, we pose open questions to call attention to the importance of collecting data considering the mentioned ecological approaches.


## 2. General Categorization of Interspecific Associations in Ants

The general classification system of “compound nests” includes five different association types with increasing degree of interactions and biological interdependence between the associated heterospecific colonies. As mentioned above, the most basic form of these associations is plesiobiosis [5, 6, 22]. According to the classical definition, plesiobiotic partner colonies share the same microhabitat without further interactions [1, 5]. In the case of cleptobiosis and lestobiosis, one of the associated colonies gains benefit from being in the vicinity of the other colony. This can be through robbing the stored resources of the other colony, stealing food from returning foragers (cleptobiosis), or preying on the brood of the alien colony (lestobiosis), thereby reducing the costs of searching and handling of food [1, 6, 9, 10]. Parabiosis differs from the other types of “compound nests” since it is a mutualistic relationship between the associated colonies [1, 6]. In these cases, each species gains benefit from its partner (e.g., by protection from enemies or competitors, interspecific trail following, etc.), and these benefits overweigh the costs of the maintenance of the coexistence [11]. Although xenobiosis is considered as a type of “compound nests,” it has more social parasitic features than the previous ones. Xenobiotic species (i.e., “guest ants”) spend their life inside the nest of their host colony stealing food or inducing trophallaxis with host workers [9]; therefore, xenobiosis is a truly parasitic form of interspecific associations [1, 6, 9].In typical social parasitic associations, individuals of different colonies mix inside the nest, and heterospecific brood is mostly cared for by host workers. These associations imply biological interdependence; that is, the parasite always depends on its host(s) [9]. The queens of temporary social parasitic species use their host colonies during colony foundation, and the mixed colony gradually develops to a pure, monospecific colony of the parasitic species [1]. In this case, the parasitic species depends on its host only during colony foundation [1, 6, 9, 12]. Unlike temporary social parasitism, slave-maker species depend on their hosts throughout their lives; that is, they are constrained to renew their labour force through robbing brood from host colonies in the course of slave-making raids [1, 6, 9]. The final and most extreme stage of social parasitism is inquilinism. Inquilinous species are the “ultimate social parasites,” as they spend their entire life cycle inside the nest of their host colony. Most of these species lack the worker caste, and their queens invest their energy to produce only reproductive offspring [1, 6, 9].


## 3. Plesiobiotic Association

Regarding the lack of biotic interdependence between the associated colonies [1, 5, 6, 12, 30], plesiobiosis is considered the most rudimentary form of interspecific associations in ants. This relationship denotes the nesting of mostly two colonies of different species in the direct proximity of each other, which means that the plesiobiotic colonies occupy the same nesting shelter (e.g., in or under logs, stumps, rocks, etc.). On the basis of the currently available data on plesiobiotic associations, this close nesting can occur occasionally or regularly, depending on the species and/or habitat type (as discussed below). Although plesiobiotic nests are adjacent to one another in several cases, they always remain separate as individual units, and the members of heterospecific colonies do not mix [6]. Plesiobionts are potentially hostile to each other, and if the nest galleries accidentally break in, fighting and brood theft may occur [6, 28, 37]. As a rule, plesiobiotic partner species differ from each other morphologically (e.g., different body size) and/or behaviourally (e.g., different foraging strategies or competitive ability), and they belong to at least different genera [6]. These differences may promote the coexistence of associated colonies according to the “limiting similarity” hypothesis suggested by MacArthur and Levins [38]. Basically, the less similar the species are the more likely they occur together in a plesiobiotic relationship in order to avoid intraspecific competition.


## 4. A Synthesis of the Recorded Cases of Plesiobiosis

### 4.1. Plesiobionts and Plesiobiotic Partners

In Table1, we list 49 species that have been observed so far in plesiobiotic associations. 29 of these belong to the subfamily Formicinae, 17 to Myrmicinae, and only 3 to Ponerinae. The four most frequent genera whose members established plesiobiotic relationships were Formica(11 species), Camponotus(9 species), Lasius(8 species), andMyrmica (4 species), well representing the general number of genera and species in the Holarctic [6].Table 1
Observed cases of plesiobiotic associations in ants.
No. of species pairs
Species pairs recorded in plesiobiotic associations
Country
Habitats
Location of nests/type of nesting shelter
No. of cases of plesiobiotic nests
Source
1
Formica fusca, Myrmica rubra
Finland;UK
Different successional series of rocky habitats;foreshore
In/under moss; under decaying wood;under stone
2; ?
Czechowski 2003, 2004 [32, 34] Morley 1945 [25]
2
Formica fusca, Myrmica ruginodis
Poland
Clearcut of managed forest
In tree stumps
1
Włodarczyk et al. 2009 [36]
3
Formica fusca-Tetramorium caespitum
Poland
Clearcut of managed forest
In tree stumps
3
Włodarczyk et al. 2009 [36]
4
Formica fusca-Leptothorax acervorum
Finland
Different successional series of rocky habitats
Mound ofF. lugubris
1
Czechowski 2004 [34]
5
Formica fusca-Lasius flavus
Finland
Different successional series of rocky habitats
Under wood; in rock crevice; under stone
4
Czechowski 2004 [34]
6
Formica fusca-Lasius platythorax
Finland; Poland
Forest on rocks; clearcut of managed forest
In decaying wood; in tree stump
3
Włodarczyk et al. 2009 [36]
7
Formica fusca-Lasius niger
UK
Foreshore
Under stone
?
Morley 1945 [25]
8
Formica fusca-Camponotus herculeanus
Poland
Forest edge
Under wood
1
Czechowski 2005 [35]
9
Formica fusca-Camponotus vagus
Hungary
Pine and poplar forest patches
In/under wood
10
Kanizsai (unpubl.)
10
Formica fusca-Formica lugubris
Finland
Different successional series of rocky habitats
Mound ofF. lugubris
1
Czechowski 2004 [34]
11
Formica fusca-Formica aquilonia
Finland
Forest on rocks
Mound ofF. lugubris
1
Czechowski and Vepsäläinen 1999 [29]
12
Formica fusca-Formica truncorum
Finland
Different successional series of rocky habitats
In rock crevice
1
Czechowski 2004 [34]
13
Lasius flavus-Formica cunicularia
UK
Foreshore
Under stone
?
Morley 1945 [25]
14
Lasius flavus-Formica aquilonia
Finland
Different successional series of rocky habitats
Mound ofF. aquilonia
1
Czechowski 2004 [34]
15
Lasius flavus-Formica fuscocinerea
Poland
Grassy mountain slope
Under stone
1
Czechowski & Czechowska 2000 [30]
16
Lasius flavus-Tetramorium caespitum
Finland
Different successional series of rocky habitats
Under stone
1
Czechowski 2004 [34]
17
Lasius flavus-Myrmica scabrinodis
UK
Foreshore
Under stone
?
Morley 1945 [25]
18
Lasius flavus-Lasius niger
Finland; UK
Rocky outcrop;shore meadow, foreshore
In rock crevice/under stone
12; ?
Czechowski 2004 [34], Morley 1945 [25]
19
Lasius flavus-Lasius platythorax
Finland
Different successional series of rocky habitats
In rock crevice/under stone/overgrown soil
3
Czechowski 2004 [34]
20
Monomorium minimum-Pachycondyla harpax
USA
?
?
?
Wheeler 1901 [5]
21
Monomorium minimum-Pogonomyrmex barbatus
USA
?
?
?
Wheeler 1901 [5]
22
Monomorium minimum-Camponotus festinatus
USA
?
?
?
Wheeler 1901 [5]
23
Monomorium minimum-Camponotus sansabeanus
USA
?
?
?
Wheeler 1901 [5]
24
Monomorium minimum- Formica gnava
USA
?
?
?
Wheeler 1901 [5]
25
Myrmecina americana-Myrmica pinetorum
USA
?
In the sand
1
Wheeler 1905 [21]
26
Myrmecina americana-Pheidole picea
USA
?
?
?
Wheeler 1901 [5]
27
Myrmecina americana-Ponera pennsylvanica
USA
?
?
?
Wheeler 1901 [5]
28
Myrmecina americana-Formica gnava
USA
?
Under stone
1
Wheeler 1901 [5]
29
Myrmica rubra-Lasius niger
Finland
Shore meadow; at road
Under stone; between asphalt edge and grass
2
Czechowski 2004 [34]
30
Myrmica rubra-Lasius platythorax
Finland
Forest
In decaying wood
1
Czechowski 2004 [34]
31
Myrmica rubra-Leptothorax muscorum
Finland
Shore meadow
Under stone
1
Czechowski 2004 [34]
32
Lasius umbratus-Formica sanguinea
Poland
Clearings in a pine forest
In the sandy soil
1
Czechowski & Rotkiewicz 1997 [27]
33
Lasius umbratus-Polyergus rufescens
Poland
Clearings in a pine forest
In the sandy soil
1
Czechowski & Rotkiewicz 1997 [27]
34
Lasius umbratus-Lasius sabularum
Poland
Stand of oak trees
Under stone
1
Borowiec 2011 [40]
35
Pheidole picea-Lasius minutus
USA
Hardwood forest
In a stump
1
Gaige 1914 [23]
36
Pheidole picea-Lasius nearcticus
USA
Hardwood forest
Under rock
1
Gaige 1914 [23]
37
Camponotus fallax-Lasius brunneus
Poland
Urban park
In decaying wood
1
Czechowski 2004 [33]
38
Camponotus herculeanus-Lasius platythorax
Finland
?
In decaying wood
1
Czechowski 2004 [33]
39
Camponotus yogi-Temnothorax andrei
USA
Chaparral
In living stems ofHaplopappus pinifolius
1
Creighton & Snelling 1966 [26]
40
Camponotus modoc-Leptothorax calderoni
USA
Pine forest
In log/in stump
?
Wheeler 1917 [24]
41
Camponotus pennsylvanicus-Formica subaenescens
USA
Hardwood forest
Under log
1
Gaige 1914 [23]
42
Camponotus festinatus-Pachycondyla harpax
USA
At road
Under stone
2
Wheeler 1901 [5]
43
Camponotus sansabeanus-Pachycondyla harpax
USA
?
?
?
Wheeler 1901 [5]
44
Camponotus ligniperdus-Aphaenogaster subterranea
Hungary
Pine forest
Under stone
3
Lőrinczi (unpubl.)
45
Formica japonica-Tetramorium tsushimae
Japan
Urban area
In the soil
1
Czechowski & Yamauchi 1998 [28]
46
Formica rufa-Leptothorax muscorum
Sweden
?
?
?
Wheeler 1901 [5]
47
Myrmecina graminicola-Ponera coarctata
Hungary
Pine forest
Under stone
2
Lőrinczi (unpubl.)
48
Strumigenys pergandei-Formicaspp., and so forth
USA
?
In the soil
?
Wheeler 1905 [21]Recent studies on plesiobiosis revealed that two species,Formica fusca(Linnaeus, 1758) and Lasius flavus (Fabricius, 1782), can be considered as two of the most frequent plesiobionts, on the basis of the total number of their so far known plesiobiotic partner species (Table 1).Up to the present, at least 48 different plesiobiotic species pairs have been recorded from different habitats of the Holarctic region. Among these,F. fuscawas involved in 12 cases (25%), L. flavusin 8 cases (16.3%), Monomorium minimum in 5 cases (10.2%), M. rubraand Myrmecina americana in 4 cases (8.16%), respectively, and Pheidole picea andLasius umbratus in 3 cases (6.12%) each (Table 1). The total number of plesiobiotic associations—where the exact number of the observed cases was given—was 69, from which the two most frequent plesiobionts participated in 46 associations, F. fuscain 28 cases (60.9%) and L. flavus in 18 cases (39.1%) (Table 1). F. fusca established plesiobiotic associations with species belonging to 6 different genera of two subfamilies (Myrmicinae and Formicinae). Its typical plesiobiotic partners were Myrmica spp. (M. rubra andM. ruginodis), Tetramoriumspp. (T.cf.caespitum), Leptothorax spp. (L. acervorum), Lasius spp. (L. platythorax, L. niger, and L. flavus), and Camponotus spp. (C. vagus andC. herculeanus). Plesiobiotic partners of L. flavus belonged to 3 different genera, Formica spp. (F. fusca, F. cunicularia, F. fuscocinerea, andF. aquilonia), Tetramorium spp. (T.cf. caespitum), and interestingly other members of the genusLasius (L. nigerandL. platythorax).Although plesiobiotic partners usually belong to at least different genera, bothF. fusca and L. flavus occurred in plesiobiosis with species of the same genera. These untypical associations were, however, mostly formed between species of different subgenera with different behavioural features. There was only one exception to this rule in which two species from the subgenus Chthonolasius, namely, Lasius umbratusand Lasius sabularum occurred in each other’s close proximity, although the exact nature of this association is unknown [40]. Among the untypical plesiobiotic associations, the ones between F. fusca and wood ants (Formica lugubris, F. aquilonia, and F. truncorum) were the most peculiar cases considering the well known temporary social parasitic character of wood ants, whose young queens often use F. fusca as host for colony foundation [6]. Nevertheless, in one case F. fuscawas observed to move into an uninhabited part of the nest mound of a F. aquiloniacolony, which was possibly queenless, though this F. fusca colony still remained there after the reviving of the wood ants [29].


### 4.2. Background Factors and Driving Forces of Plesiobiosis

#### 4.2.1. Role of Habitat Type and Food Supply

Plesiobiotic nests have been recorded from various habitat types, representing different stages of both primary succession and secondary succession. It is important to note, however, that a number of records on plesiobiosis were mere observations without any significant ecological information, for example, on habitat type, nesting site, and/or the number of observed cases of plesiobiotic pairs.Many of the recorded plesiobiotic species pairs have been described in rocky habitats in Finland. The spectrum of study sites ranged from earlier stages of primary succession, such as open rocky outcrops and shore meadows, to mature pine forests, which represented the last successional stage of rocky habitats. According to this study, most of the plesiobiotic associations involvingLasius s. str. were observed in earlier stages of primary succession. This observation confirmed the hypothesis by Czechowski [31], stating that plesiobiosis is especially frequent in habitats lacking suitable nesting sites, and the scarcity of these is one of the main factors promoting the formation of plesiobiotic associations between ant colonies [34].Another investigation was conducted in a sand dune complex in Finland, where only one plesiobiotic association was observed, which was betweenF. fusca and M. rubra [32]. The reason for this may be that each successional stage of the sand dunes represents more homogenous habitats and larger areas optimal for nesting than rocky habitats [32].Species that prefer to inhabit stumps can be suitable objects for studying the effect of the amount of potential nesting sites on the frequency of plesiobiotic associations. Włodarczyk et al. [36], for instance, studied clearcuts in a managed forest in western Poland, where stumps that were left on clearcuts served as suitable nesting sites for several species. Although clearcuts represented the initial stage of secondary succession, the amount of potential nesting sites for ants preferring stumps was relatively high, and almost half of the available stumps were occupied by colonies of 9 different ant species [36]. Of the 512 stumps that were checked, five were inhabited by more than one ant species, representing plesiobiotic associations, with F. fusca as one of the partners in all cases (F. fusca, Tetramorium caespitum in three cases; F. fusca, Myrmica ruginodis in one case and F. fusca, L. platythorax in one case) [36]. Although clearcuts offered a high number of stumps suitable for nesting, the sparse vegetation cover provided poor trophic conditions for aphid-related ant species compared with forest patches [36], resulting in the presence of fewer species competing for the available nesting sites.Investigations on plesiobiosis betweenF. fusca and C. vagus were conducted in patches of pine and poplar forests in central Hungary (Kanizsai, unpubl.). It was shown that both the density of nests and the number of plesiobiotic associations were influenced by the age of forest patches, and there were more plesiobiotic relationships in older patches than in younger ones. A possible explanation can be that the higher nest density of either species may have facilitated the formation of plesiobiotic associations in older patches.


#### 4.2.2. Role of Nest Density and Intraspecific Competition

Two main habitat properties may contribute to the formation of plesiobiotic associations: the scarcity of suitable nesting sites as a forcing factor [34] and the sufficient amount of food sources available, which significantly influence the abundance and reproductivity of ant colonies [41]. When colony density is high, the depletion of food resources by neighbouring colonies may be more intensive, resulting in an increased mortality, especially in the case of incipient colonies [42]. According to former studies ([43] and references therein), the spacing pattern of the nests of F. fusca and L. flavus (the two most frequent plesiobionts) was, or tended to be regular, when the density of their colonies were high in a suitable habitat. Although competition can produce any type of spacing pattern [44], the regular spatial arrangement of conspecific nests may indicate an intensive intraspecific competition for the same resources [42, 45–49]. Owing to similar food requirements, intraspecific competition supposed to be stronger than interspecific competition [43, 48–50]. The regular dispersion of conspecific nests can reduce the overlapping of foraging areas, thereby minimising intraspecific competition [43, 46, 49]. To effectively utilise foraging areas, it can be advantageous in these cases to maximise the distance between conspecific colonies with similar food requirements and foraging ranges [48]. Thus, it is more favourable for colonies if their nearest neighbours are rather heterospecifics with less overlapping requirements, resulting in a kind of “dear enemy” effect. Therefore, strong intraspecific competition can also contribute to the formation of plesiobiotic associations.


#### 4.2.3. Significance of Differences between Plesiobiotic Partners

Potential Role of Competition: Position of the Plesiobionts in the Interspecific Competitive Hierarchy.Recent studies have revealed that F. fusca is one of the most frequent plesiobionts among the studied ants. Similarly to other common plesiobionts, F. fuscais also a submissive species in the three-level classification of the competitive hierarchy in ants [51, 52]. The submissive behaviour and the opportunistic character of this species can be considered as one of the main features that contribute to its frequent cooccurrence with other species in plesiobiotic associations. Although most of the plesiobiotic partners of F. fuscaoccupied a higher level in the interspecific competition hierarchy, it established plesiobiotic relationships with species that are also submissive (e.g., with M. rubra, L. flavus, and Leptothorax acervorum).Being also submissive,Myrmica spp. are also able to coexist with aggressive ant species. For example, M. ruginodis and M. scabrinodis were observed to shift their foraging to periods with lower temperature. Accordingly, in areas where territorial competitors were also present, they visited baits at night instead [53].In the case of the subterranean, cryptic speciesL. flavus, competitive ability may play a less significant role regarding the coexistence with other species. While the two above-mentioned plesiobionts are surface foragers, that is, they mostly search for food on or above the ground, the colonies of L. flavus, however, were found to be associated with various species of root aphids [54]. Thus, for subterranean Cautolasius species, the importance of vertical separation in foraging seems more significant than other mechanisms for reducing competition.Contrary to the afore-mentioned species, severalCamponotus species are typically regarded as encounter species that is, they defend not only their nests but the discovered resources as well [51, 52]; therefore only submissive species can be expected to be their plesiobiotic partners.Conflict Avoidance: Differences in the Foraging Strategy of Plesiobiotic Partners and Resource Partitioning.As plesiobiotic partner colonies share the same microhabitat [1], they have overlapping foraging area and home ranges owing to the small distances between their associated nests. Accordingly, the probability of an encounter between the members of the two colonies increases as the distance between their nests decreases [55]. Due to the close neighbourhood of the associated colonies, they are expected to interact most intensely with each other. A common outcome of interspecific competition is the minimising of spatial and/or temporal overlapping during foraging, that is, differing from each other in their daily and/or seasonal activity, foraging area, or diet [56–59]. Beside partitioning spatially and/or temporally, different foraging strategies (e.g., individual searching, tandem running and other types of recruitment systems) may also contribute to the coexistence of different species [39, 60, 61]. Although body size can also influence the foraging range, the existence of food recruitment systems makes ants less constrained by their morphology than what can be seen in the case of other animals [60, 62, 63]; thereby, the effects of behavioural features seem more important than those of morphological ones. On the other hand, differences in body size can promote resource partitioning by reducing the overlap in resource use [64]. Although differences in body size cannot explain food-resource partitioning alone, these can still contribute to the formation of a number of plesiobiotic relationships.


## 4.1. Plesiobionts and Plesiobiotic Partners

In Table1, we list 49 species that have been observed so far in plesiobiotic associations. 29 of these belong to the subfamily Formicinae, 17 to Myrmicinae, and only 3 to Ponerinae. The four most frequent genera whose members established plesiobiotic relationships were Formica(11 species), Camponotus(9 species), Lasius(8 species), andMyrmica (4 species), well representing the general number of genera and species in the Holarctic [6].Table 1
Observed cases of plesiobiotic associations in ants.
No. of species pairs
Species pairs recorded in plesiobiotic associations
Country
Habitats
Location of nests/type of nesting shelter
No. of cases of plesiobiotic nests
Source
1
Formica fusca, Myrmica rubra
Finland;UK
Different successional series of rocky habitats;foreshore
In/under moss; under decaying wood;under stone
2; ?
Czechowski 2003, 2004 [32, 34] Morley 1945 [25]
2
Formica fusca, Myrmica ruginodis
Poland
Clearcut of managed forest
In tree stumps
1
Włodarczyk et al. 2009 [36]
3
Formica fusca-Tetramorium caespitum
Poland
Clearcut of managed forest
In tree stumps
3
Włodarczyk et al. 2009 [36]
4
Formica fusca-Leptothorax acervorum
Finland
Different successional series of rocky habitats
Mound ofF. lugubris
1
Czechowski 2004 [34]
5
Formica fusca-Lasius flavus
Finland
Different successional series of rocky habitats
Under wood; in rock crevice; under stone
4
Czechowski 2004 [34]
6
Formica fusca-Lasius platythorax
Finland; Poland
Forest on rocks; clearcut of managed forest
In decaying wood; in tree stump
3
Włodarczyk et al. 2009 [36]
7
Formica fusca-Lasius niger
UK
Foreshore
Under stone
?
Morley 1945 [25]
8
Formica fusca-Camponotus herculeanus
Poland
Forest edge
Under wood
1
Czechowski 2005 [35]
9
Formica fusca-Camponotus vagus
Hungary
Pine and poplar forest patches
In/under wood
10
Kanizsai (unpubl.)
10
Formica fusca-Formica lugubris
Finland
Different successional series of rocky habitats
Mound ofF. lugubris
1
Czechowski 2004 [34]
11
Formica fusca-Formica aquilonia
Finland
Forest on rocks
Mound ofF. lugubris
1
Czechowski and Vepsäläinen 1999 [29]
12
Formica fusca-Formica truncorum
Finland
Different successional series of rocky habitats
In rock crevice
1
Czechowski 2004 [34]
13
Lasius flavus-Formica cunicularia
UK
Foreshore
Under stone
?
Morley 1945 [25]
14
Lasius flavus-Formica aquilonia
Finland
Different successional series of rocky habitats
Mound ofF. aquilonia
1
Czechowski 2004 [34]
15
Lasius flavus-Formica fuscocinerea
Poland
Grassy mountain slope
Under stone
1
Czechowski & Czechowska 2000 [30]
16
Lasius flavus-Tetramorium caespitum
Finland
Different successional series of rocky habitats
Under stone
1
Czechowski 2004 [34]
17
Lasius flavus-Myrmica scabrinodis
UK
Foreshore
Under stone
?
Morley 1945 [25]
18
Lasius flavus-Lasius niger
Finland; UK
Rocky outcrop;shore meadow, foreshore
In rock crevice/under stone
12; ?
Czechowski 2004 [34], Morley 1945 [25]
19
Lasius flavus-Lasius platythorax
Finland
Different successional series of rocky habitats
In rock crevice/under stone/overgrown soil
3
Czechowski 2004 [34]
20
Monomorium minimum-Pachycondyla harpax
USA
?
?
?
Wheeler 1901 [5]
21
Monomorium minimum-Pogonomyrmex barbatus
USA
?
?
?
Wheeler 1901 [5]
22
Monomorium minimum-Camponotus festinatus
USA
?
?
?
Wheeler 1901 [5]
23
Monomorium minimum-Camponotus sansabeanus
USA
?
?
?
Wheeler 1901 [5]
24
Monomorium minimum- Formica gnava
USA
?
?
?
Wheeler 1901 [5]
25
Myrmecina americana-Myrmica pinetorum
USA
?
In the sand
1
Wheeler 1905 [21]
26
Myrmecina americana-Pheidole picea
USA
?
?
?
Wheeler 1901 [5]
27
Myrmecina americana-Ponera pennsylvanica
USA
?
?
?
Wheeler 1901 [5]
28
Myrmecina americana-Formica gnava
USA
?
Under stone
1
Wheeler 1901 [5]
29
Myrmica rubra-Lasius niger
Finland
Shore meadow; at road
Under stone; between asphalt edge and grass
2
Czechowski 2004 [34]
30
Myrmica rubra-Lasius platythorax
Finland
Forest
In decaying wood
1
Czechowski 2004 [34]
31
Myrmica rubra-Leptothorax muscorum
Finland
Shore meadow
Under stone
1
Czechowski 2004 [34]
32
Lasius umbratus-Formica sanguinea
Poland
Clearings in a pine forest
In the sandy soil
1
Czechowski & Rotkiewicz 1997 [27]
33
Lasius umbratus-Polyergus rufescens
Poland
Clearings in a pine forest
In the sandy soil
1
Czechowski & Rotkiewicz 1997 [27]
34
Lasius umbratus-Lasius sabularum
Poland
Stand of oak trees
Under stone
1
Borowiec 2011 [40]
35
Pheidole picea-Lasius minutus
USA
Hardwood forest
In a stump
1
Gaige 1914 [23]
36
Pheidole picea-Lasius nearcticus
USA
Hardwood forest
Under rock
1
Gaige 1914 [23]
37
Camponotus fallax-Lasius brunneus
Poland
Urban park
In decaying wood
1
Czechowski 2004 [33]
38
Camponotus herculeanus-Lasius platythorax
Finland
?
In decaying wood
1
Czechowski 2004 [33]
39
Camponotus yogi-Temnothorax andrei
USA
Chaparral
In living stems ofHaplopappus pinifolius
1
Creighton & Snelling 1966 [26]
40
Camponotus modoc-Leptothorax calderoni
USA
Pine forest
In log/in stump
?
Wheeler 1917 [24]
41
Camponotus pennsylvanicus-Formica subaenescens
USA
Hardwood forest
Under log
1
Gaige 1914 [23]
42
Camponotus festinatus-Pachycondyla harpax
USA
At road
Under stone
2
Wheeler 1901 [5]
43
Camponotus sansabeanus-Pachycondyla harpax
USA
?
?
?
Wheeler 1901 [5]
44
Camponotus ligniperdus-Aphaenogaster subterranea
Hungary
Pine forest
Under stone
3
Lőrinczi (unpubl.)
45
Formica japonica-Tetramorium tsushimae
Japan
Urban area
In the soil
1
Czechowski & Yamauchi 1998 [28]
46
Formica rufa-Leptothorax muscorum
Sweden
?
?
?
Wheeler 1901 [5]
47
Myrmecina graminicola-Ponera coarctata
Hungary
Pine forest
Under stone
2
Lőrinczi (unpubl.)
48
Strumigenys pergandei-Formicaspp., and so forth
USA
?
In the soil
?
Wheeler 1905 [21]Recent studies on plesiobiosis revealed that two species,Formica fusca(Linnaeus, 1758) and Lasius flavus (Fabricius, 1782), can be considered as two of the most frequent plesiobionts, on the basis of the total number of their so far known plesiobiotic partner species (Table 1).Up to the present, at least 48 different plesiobiotic species pairs have been recorded from different habitats of the Holarctic region. Among these,F. fuscawas involved in 12 cases (25%), L. flavusin 8 cases (16.3%), Monomorium minimum in 5 cases (10.2%), M. rubraand Myrmecina americana in 4 cases (8.16%), respectively, and Pheidole picea andLasius umbratus in 3 cases (6.12%) each (Table 1). The total number of plesiobiotic associations—where the exact number of the observed cases was given—was 69, from which the two most frequent plesiobionts participated in 46 associations, F. fuscain 28 cases (60.9%) and L. flavus in 18 cases (39.1%) (Table 1). F. fusca established plesiobiotic associations with species belonging to 6 different genera of two subfamilies (Myrmicinae and Formicinae). Its typical plesiobiotic partners were Myrmica spp. (M. rubra andM. ruginodis), Tetramoriumspp. (T.cf.caespitum), Leptothorax spp. (L. acervorum), Lasius spp. (L. platythorax, L. niger, and L. flavus), and Camponotus spp. (C. vagus andC. herculeanus). Plesiobiotic partners of L. flavus belonged to 3 different genera, Formica spp. (F. fusca, F. cunicularia, F. fuscocinerea, andF. aquilonia), Tetramorium spp. (T.cf. caespitum), and interestingly other members of the genusLasius (L. nigerandL. platythorax).Although plesiobiotic partners usually belong to at least different genera, bothF. fusca and L. flavus occurred in plesiobiosis with species of the same genera. These untypical associations were, however, mostly formed between species of different subgenera with different behavioural features. There was only one exception to this rule in which two species from the subgenus Chthonolasius, namely, Lasius umbratusand Lasius sabularum occurred in each other’s close proximity, although the exact nature of this association is unknown [40]. Among the untypical plesiobiotic associations, the ones between F. fusca and wood ants (Formica lugubris, F. aquilonia, and F. truncorum) were the most peculiar cases considering the well known temporary social parasitic character of wood ants, whose young queens often use F. fusca as host for colony foundation [6]. Nevertheless, in one case F. fuscawas observed to move into an uninhabited part of the nest mound of a F. aquiloniacolony, which was possibly queenless, though this F. fusca colony still remained there after the reviving of the wood ants [29].


## 4.2. Background Factors and Driving Forces of Plesiobiosis

### 4.2.1. Role of Habitat Type and Food Supply

Plesiobiotic nests have been recorded from various habitat types, representing different stages of both primary succession and secondary succession. It is important to note, however, that a number of records on plesiobiosis were mere observations without any significant ecological information, for example, on habitat type, nesting site, and/or the number of observed cases of plesiobiotic pairs.Many of the recorded plesiobiotic species pairs have been described in rocky habitats in Finland. The spectrum of study sites ranged from earlier stages of primary succession, such as open rocky outcrops and shore meadows, to mature pine forests, which represented the last successional stage of rocky habitats. According to this study, most of the plesiobiotic associations involvingLasius s. str. were observed in earlier stages of primary succession. This observation confirmed the hypothesis by Czechowski [31], stating that plesiobiosis is especially frequent in habitats lacking suitable nesting sites, and the scarcity of these is one of the main factors promoting the formation of plesiobiotic associations between ant colonies [34].Another investigation was conducted in a sand dune complex in Finland, where only one plesiobiotic association was observed, which was betweenF. fusca and M. rubra [32]. The reason for this may be that each successional stage of the sand dunes represents more homogenous habitats and larger areas optimal for nesting than rocky habitats [32].Species that prefer to inhabit stumps can be suitable objects for studying the effect of the amount of potential nesting sites on the frequency of plesiobiotic associations. Włodarczyk et al. [36], for instance, studied clearcuts in a managed forest in western Poland, where stumps that were left on clearcuts served as suitable nesting sites for several species. Although clearcuts represented the initial stage of secondary succession, the amount of potential nesting sites for ants preferring stumps was relatively high, and almost half of the available stumps were occupied by colonies of 9 different ant species [36]. Of the 512 stumps that were checked, five were inhabited by more than one ant species, representing plesiobiotic associations, with F. fusca as one of the partners in all cases (F. fusca, Tetramorium caespitum in three cases; F. fusca, Myrmica ruginodis in one case and F. fusca, L. platythorax in one case) [36]. Although clearcuts offered a high number of stumps suitable for nesting, the sparse vegetation cover provided poor trophic conditions for aphid-related ant species compared with forest patches [36], resulting in the presence of fewer species competing for the available nesting sites.Investigations on plesiobiosis betweenF. fusca and C. vagus were conducted in patches of pine and poplar forests in central Hungary (Kanizsai, unpubl.). It was shown that both the density of nests and the number of plesiobiotic associations were influenced by the age of forest patches, and there were more plesiobiotic relationships in older patches than in younger ones. A possible explanation can be that the higher nest density of either species may have facilitated the formation of plesiobiotic associations in older patches.


### 4.2.2. Role of Nest Density and Intraspecific Competition

Two main habitat properties may contribute to the formation of plesiobiotic associations: the scarcity of suitable nesting sites as a forcing factor [34] and the sufficient amount of food sources available, which significantly influence the abundance and reproductivity of ant colonies [41]. When colony density is high, the depletion of food resources by neighbouring colonies may be more intensive, resulting in an increased mortality, especially in the case of incipient colonies [42]. According to former studies ([43] and references therein), the spacing pattern of the nests of F. fusca and L. flavus (the two most frequent plesiobionts) was, or tended to be regular, when the density of their colonies were high in a suitable habitat. Although competition can produce any type of spacing pattern [44], the regular spatial arrangement of conspecific nests may indicate an intensive intraspecific competition for the same resources [42, 45–49]. Owing to similar food requirements, intraspecific competition supposed to be stronger than interspecific competition [43, 48–50]. The regular dispersion of conspecific nests can reduce the overlapping of foraging areas, thereby minimising intraspecific competition [43, 46, 49]. To effectively utilise foraging areas, it can be advantageous in these cases to maximise the distance between conspecific colonies with similar food requirements and foraging ranges [48]. Thus, it is more favourable for colonies if their nearest neighbours are rather heterospecifics with less overlapping requirements, resulting in a kind of “dear enemy” effect. Therefore, strong intraspecific competition can also contribute to the formation of plesiobiotic associations.


### 4.2.3. Significance of Differences between Plesiobiotic Partners

Potential Role of Competition: Position of the Plesiobionts in the Interspecific Competitive Hierarchy.Recent studies have revealed that F. fusca is one of the most frequent plesiobionts among the studied ants. Similarly to other common plesiobionts, F. fuscais also a submissive species in the three-level classification of the competitive hierarchy in ants [51, 52]. The submissive behaviour and the opportunistic character of this species can be considered as one of the main features that contribute to its frequent cooccurrence with other species in plesiobiotic associations. Although most of the plesiobiotic partners of F. fuscaoccupied a higher level in the interspecific competition hierarchy, it established plesiobiotic relationships with species that are also submissive (e.g., with M. rubra, L. flavus, and Leptothorax acervorum).Being also submissive,Myrmica spp. are also able to coexist with aggressive ant species. For example, M. ruginodis and M. scabrinodis were observed to shift their foraging to periods with lower temperature. Accordingly, in areas where territorial competitors were also present, they visited baits at night instead [53].In the case of the subterranean, cryptic speciesL. flavus, competitive ability may play a less significant role regarding the coexistence with other species. While the two above-mentioned plesiobionts are surface foragers, that is, they mostly search for food on or above the ground, the colonies of L. flavus, however, were found to be associated with various species of root aphids [54]. Thus, for subterranean Cautolasius species, the importance of vertical separation in foraging seems more significant than other mechanisms for reducing competition.Contrary to the afore-mentioned species, severalCamponotus species are typically regarded as encounter species that is, they defend not only their nests but the discovered resources as well [51, 52]; therefore only submissive species can be expected to be their plesiobiotic partners.Conflict Avoidance: Differences in the Foraging Strategy of Plesiobiotic Partners and Resource Partitioning.As plesiobiotic partner colonies share the same microhabitat [1], they have overlapping foraging area and home ranges owing to the small distances between their associated nests. Accordingly, the probability of an encounter between the members of the two colonies increases as the distance between their nests decreases [55]. Due to the close neighbourhood of the associated colonies, they are expected to interact most intensely with each other. A common outcome of interspecific competition is the minimising of spatial and/or temporal overlapping during foraging, that is, differing from each other in their daily and/or seasonal activity, foraging area, or diet [56–59]. Beside partitioning spatially and/or temporally, different foraging strategies (e.g., individual searching, tandem running and other types of recruitment systems) may also contribute to the coexistence of different species [39, 60, 61]. Although body size can also influence the foraging range, the existence of food recruitment systems makes ants less constrained by their morphology than what can be seen in the case of other animals [60, 62, 63]; thereby, the effects of behavioural features seem more important than those of morphological ones. On the other hand, differences in body size can promote resource partitioning by reducing the overlap in resource use [64]. Although differences in body size cannot explain food-resource partitioning alone, these can still contribute to the formation of a number of plesiobiotic relationships.


## 4.2.1. Role of Habitat Type and Food Supply

Plesiobiotic nests have been recorded from various habitat types, representing different stages of both primary succession and secondary succession. It is important to note, however, that a number of records on plesiobiosis were mere observations without any significant ecological information, for example, on habitat type, nesting site, and/or the number of observed cases of plesiobiotic pairs.Many of the recorded plesiobiotic species pairs have been described in rocky habitats in Finland. The spectrum of study sites ranged from earlier stages of primary succession, such as open rocky outcrops and shore meadows, to mature pine forests, which represented the last successional stage of rocky habitats. According to this study, most of the plesiobiotic associations involvingLasius s. str. were observed in earlier stages of primary succession. This observation confirmed the hypothesis by Czechowski [31], stating that plesiobiosis is especially frequent in habitats lacking suitable nesting sites, and the scarcity of these is one of the main factors promoting the formation of plesiobiotic associations between ant colonies [34].Another investigation was conducted in a sand dune complex in Finland, where only one plesiobiotic association was observed, which was betweenF. fusca and M. rubra [32]. The reason for this may be that each successional stage of the sand dunes represents more homogenous habitats and larger areas optimal for nesting than rocky habitats [32].Species that prefer to inhabit stumps can be suitable objects for studying the effect of the amount of potential nesting sites on the frequency of plesiobiotic associations. Włodarczyk et al. [36], for instance, studied clearcuts in a managed forest in western Poland, where stumps that were left on clearcuts served as suitable nesting sites for several species. Although clearcuts represented the initial stage of secondary succession, the amount of potential nesting sites for ants preferring stumps was relatively high, and almost half of the available stumps were occupied by colonies of 9 different ant species [36]. Of the 512 stumps that were checked, five were inhabited by more than one ant species, representing plesiobiotic associations, with F. fusca as one of the partners in all cases (F. fusca, Tetramorium caespitum in three cases; F. fusca, Myrmica ruginodis in one case and F. fusca, L. platythorax in one case) [36]. Although clearcuts offered a high number of stumps suitable for nesting, the sparse vegetation cover provided poor trophic conditions for aphid-related ant species compared with forest patches [36], resulting in the presence of fewer species competing for the available nesting sites.Investigations on plesiobiosis betweenF. fusca and C. vagus were conducted in patches of pine and poplar forests in central Hungary (Kanizsai, unpubl.). It was shown that both the density of nests and the number of plesiobiotic associations were influenced by the age of forest patches, and there were more plesiobiotic relationships in older patches than in younger ones. A possible explanation can be that the higher nest density of either species may have facilitated the formation of plesiobiotic associations in older patches.


## 4.2.2. Role of Nest Density and Intraspecific Competition

Two main habitat properties may contribute to the formation of plesiobiotic associations: the scarcity of suitable nesting sites as a forcing factor [34] and the sufficient amount of food sources available, which significantly influence the abundance and reproductivity of ant colonies [41]. When colony density is high, the depletion of food resources by neighbouring colonies may be more intensive, resulting in an increased mortality, especially in the case of incipient colonies [42]. According to former studies ([43] and references therein), the spacing pattern of the nests of F. fusca and L. flavus (the two most frequent plesiobionts) was, or tended to be regular, when the density of their colonies were high in a suitable habitat. Although competition can produce any type of spacing pattern [44], the regular spatial arrangement of conspecific nests may indicate an intensive intraspecific competition for the same resources [42, 45–49]. Owing to similar food requirements, intraspecific competition supposed to be stronger than interspecific competition [43, 48–50]. The regular dispersion of conspecific nests can reduce the overlapping of foraging areas, thereby minimising intraspecific competition [43, 46, 49]. To effectively utilise foraging areas, it can be advantageous in these cases to maximise the distance between conspecific colonies with similar food requirements and foraging ranges [48]. Thus, it is more favourable for colonies if their nearest neighbours are rather heterospecifics with less overlapping requirements, resulting in a kind of “dear enemy” effect. Therefore, strong intraspecific competition can also contribute to the formation of plesiobiotic associations.


## 4.2.3. Significance of Differences between Plesiobiotic Partners

Potential Role of Competition: Position of the Plesiobionts in the Interspecific Competitive Hierarchy.Recent studies have revealed that F. fusca is one of the most frequent plesiobionts among the studied ants. Similarly to other common plesiobionts, F. fuscais also a submissive species in the three-level classification of the competitive hierarchy in ants [51, 52]. The submissive behaviour and the opportunistic character of this species can be considered as one of the main features that contribute to its frequent cooccurrence with other species in plesiobiotic associations. Although most of the plesiobiotic partners of F. fuscaoccupied a higher level in the interspecific competition hierarchy, it established plesiobiotic relationships with species that are also submissive (e.g., with M. rubra, L. flavus, and Leptothorax acervorum).Being also submissive,Myrmica spp. are also able to coexist with aggressive ant species. For example, M. ruginodis and M. scabrinodis were observed to shift their foraging to periods with lower temperature. Accordingly, in areas where territorial competitors were also present, they visited baits at night instead [53].In the case of the subterranean, cryptic speciesL. flavus, competitive ability may play a less significant role regarding the coexistence with other species. While the two above-mentioned plesiobionts are surface foragers, that is, they mostly search for food on or above the ground, the colonies of L. flavus, however, were found to be associated with various species of root aphids [54]. Thus, for subterranean Cautolasius species, the importance of vertical separation in foraging seems more significant than other mechanisms for reducing competition.Contrary to the afore-mentioned species, severalCamponotus species are typically regarded as encounter species that is, they defend not only their nests but the discovered resources as well [51, 52]; therefore only submissive species can be expected to be their plesiobiotic partners.Conflict Avoidance: Differences in the Foraging Strategy of Plesiobiotic Partners and Resource Partitioning.As plesiobiotic partner colonies share the same microhabitat [1], they have overlapping foraging area and home ranges owing to the small distances between their associated nests. Accordingly, the probability of an encounter between the members of the two colonies increases as the distance between their nests decreases [55]. Due to the close neighbourhood of the associated colonies, they are expected to interact most intensely with each other. A common outcome of interspecific competition is the minimising of spatial and/or temporal overlapping during foraging, that is, differing from each other in their daily and/or seasonal activity, foraging area, or diet [56–59]. Beside partitioning spatially and/or temporally, different foraging strategies (e.g., individual searching, tandem running and other types of recruitment systems) may also contribute to the coexistence of different species [39, 60, 61]. Although body size can also influence the foraging range, the existence of food recruitment systems makes ants less constrained by their morphology than what can be seen in the case of other animals [60, 62, 63]; thereby, the effects of behavioural features seem more important than those of morphological ones. On the other hand, differences in body size can promote resource partitioning by reducing the overlap in resource use [64]. Although differences in body size cannot explain food-resource partitioning alone, these can still contribute to the formation of a number of plesiobiotic relationships.


## 5. Conclusions

On the basis of the above considerations, we define plesiobiosis as the occasional or regular nesting of heterospecific colonies of certain species in close proximity to each other without biological interdependence.Based on the currently available data, members of the subfamily Formicinae establish plesiobiotic relationships the most frequently, and the most common plesiobionts among them seems to beF. fusca. The opportunistic and submissive behaviour of this species makes it a typical plesiobiont, and it is also a frequent host of both temporary social parasites and slave makers [6, 65].As a rule, plesiobiosis can be formed between ant species that differ from each other in behaviour—primarily in their competitive ability—and in foraging strategies. Other subordinate species with different behaviour or species with higher competitive ability can also be potential partners as plesiobionts.Beside the lack of suitable nesting sites, the appropriate amount of available food sources may also play a role in the formation of plesiobiosis, contributing to higher colony densities. The overlap in diet can enhance intraspecific competition, which may force colonies into the vicinity of heterospecific nests. Owing to higher colony density, nesting in each other’s close neighbourhood will also occur more frequently. Plesiobiotic associations formed this way may promote a persistent coexistence in cases where the differences are considerable between the partners, which can lead to the formation of other types of interspecific associations with higher levels of biotic interactions.It is important to note, that the currently available data concerning plesiobiosis are far from being representative. Only a couple of studies have dealt with this topic, and these are restricted to a small number of habitat types of few countries in the northern latitudes. Moreover, most of these studies reported only observations of plesiobiotic cases without additional ecological information, like the regularity of such associations between the species in question. Therefore, to get a more comprehensive picture about plesiobiosis, it would be essential to collect more and detailed data globally.


## 6. Open Questions

Regarding our present knowledge on plesiobiosis in ants, there are still many open questions that need to be answered, which are important for a better understanding of this kind of interspecific relationship.(1)Persistence of plesiobiosis. Plesiobiosis can be formed occasionally between heterospecific colonies, but we still do not know how persistent these associations are. Although ant colonies have typically been treated as spatially fixed entities, inhabiting a given nesting site permanently, it seems that periodic nest relocation is an important aspect of the behaviour of many ant species [66–68]. It is also uncertain what effects may trigger the disaggregation of plesiobiotic colonies and force the relocation of one of the associated plesiobionts.(2)The role of nesting shelters and “ecosystem engineering.” It also provides a basis for further investigation, to what extent the type of nesting shelters (e.g., logs, stumps, and rocks) promotes the formation of plesiobiotic associations and how the already established colonies facilitate the settlement of colonies due to their nest constructions. In temperate regions, a large number of species occupy dead logs and stumps or nest in the soil under rocks [6]. Due to their thermal properties, colonies occupying these shelters are allowed to enter to colony growth stage earlier and they are less vulnerable to unsuitable humidity and temperature values. These beneficial conditions can lead to the joint nesting of two or more species in or under the same shelter, especially if the number of suitable nesting sites is low. For example, the nest mounds of wood ants may provide suitable nesting sites for other species owing to their unique microhabitat conditions [69]. This may serve as an explanation for the untypical plesiobiotic associations observed between F. fusca and the members of Formica s. str., where the former species frequently settles into the uninhabited parts of the nest mounds of wood ants [29]. Similarly, many Camponotus species create their nest galleries in trunks and stumps [70–72], which may promote the establishment of colonies of other species in these microhabitats. Owing to this “ecosystem engineering,” plesiobiotic associations may develop from an occasional to a regular relationship even without direct interactions between the associated colonies.(3)The “close” proximity of heterospecific colonies.Former definitions of plesiobiosis emphasise the importance of the close proximity of plesiobiotic colonies, though it is not clear how close this proximity should be or whether these colonies should use the same nesting shelter. In Table 1 we listed only those cases where the plesiobiotic colonies occupied the same nest (i.e., they were under the same stone or in the same log). It is a question, however, whether the frequent neighbouring arrangement of the nests of certain species pairs (when their nests do not necessarily border on one another) can be considered as a plesiobiotic relationship.(4)Plesiobiotic associations of arboreal species. Most of the recorded cases of plesiobiotic associations are between species that inhabit nests located on or under the ground surface. Arboreal species, however, are also known to frequently create their nests in the vicinity of each other on the same tree, as it was, for instance, observed in the case of Camponotus fallax, Lasius brunneus, andTemnothorax affinis [73]. Actually, it was demonstrated that the former two species can occur in a plesiobiotic relationship [33]. It is an interesting question how frequently arboreal species nest in one another’s neighbourhood, and to what extent these cases can be considered as plesiobiosis.



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*Source: 238602-2013-05-29.xml*