Species coexistence, the question of how different species can coexist while competing for limiting resources, is a central question in ecology (Huston, ; Hutchinson, ). A classic example of species coexistence is found among four ant species that inhabit the ant‐plant Acacia (also referred to as Vachellia) drepanolobium. The Whistling‐Thorn Acacia, A. drepanolobium, is an East African Savannah tree that engages in a defensive mutualism with ants, providing the ants with extra‐floral nectar and housing in hollow, swollen‐thorn “domatia” in return for defense from herbivory (Hocking, ; Young, Stubblefield, & Isbell, ; Figure ). At a well‐studied field site in Kenya, four species of ants are commonly hosted by the acacia. Three of them, Crematogaster mimosae, C. nigriceps, and Tetraponera penzigi, are “phytoecious,” or obligate inhabitants of the ant‐plant of A. drepanolobium, while the fourth, C. sjostedti, is free‐living, nesting under bark and in rotting wood (Stanton, Palmer, & Young, ). Almost every mature tree of A. drepanolobium is occupied by a single ant colony (although individual colonies can range over a number of adjacent trees), and competition among ants for these trees is intense (Palmer, Young, Stanton, & Wenk, ). In light of this, much research has focused on how these four species are able to coexist on a single resource (Palmer, ; Palmer et al., ; Stanton et al., ; Young et al., ), in violation of theory suggesting that this situation should be ecologically unstable (Gause, ; Hardin, ).
Ants inhabit Acacia drepanolobium trees on black cotton soils. On these soils, A. drepanolobium may account for 95% or more of trees, as shown on the left‐hand side (Young et al., ). Ants live in hollow, swollen thorns and patrol the tree against herbivores (right). Photographs: NEP (left) and JHB (right)
The best‐supported hypothesis to explain this coexistence is that a colonization‐competition trade‐off exists among the ant species: ants specialize either in colonizing new resources (i.e., unoccupied trees) or in competing for occupied resources. Observations of naturally occurring transitions from occupancy by one ant species to another have shown a competitive hierarchy among the ants, with C. sjostedti as the most dominant, followed by C. mimosae, C. nigriceps, and T. penzigi; this hierarchy has also been supported by experiments in which contests were staged by tying the canopies of neighboring trees together (Palmer et al., ). The degree to which a single colony extends over multiple trees (i.e., a form of polydomy, where a single colony has multiple nest chambers spread across several trees) is also correlated with the competitive hierarchy, with C. sjostedti occupying the greatest number of adjacent trees, and T. penzigi occupying the least (Palmer et al., ). Furthermore, more competitive ant species also occupy larger, presumably more valuable trees (Palmer et al., ; Young et al., ).
Consistent with the competition‐colonization trade‐off hypothesis, a colonization hierarchy runs counter to the competitive hierarchy, allowing species coexistence. Colonization ability has been measured using several metrics: production of foundress queens, recruitment of these foundresses to empty trees, ability of foundresses to win fights with each other over individual domatia on newly colonized trees, speed with which foundresses can produce workers that occupy the rest of the tree, and vulnerability to parasitism (Palmer et al., ; Stanton, Palmer, & Young, ; Stanton et al., ). This research has supported the existence of a colonization hierarchy in which T. penzigi is the best colonizer, followed by C. nigriceps, C. mimosae, and C. sjostedti, viz. the reverse order of the competitive hierarchy.
While differences in competitive and colonizing ability among A. drepanolobium's ant associates have been well described, our understanding of the mechanistic basis for these differences is still lagging. The higher competitive ability of dominant species, in particular, seems to be driven by larger worker populations (Palmer, ; Ruiz‐Guajardo, Grossenbacher, Grosberg, Palmer, & Stanton, ), but the proximate causes of these larger worker populations are unknown. A primary hypothesis proposed is that more competitive species are polygynous, that is, they have multiple queens per colony (Palmer, ; Rubin et al., ). Collectively, these queens are able to lay more eggs, thereby producing larger worker populations that can outcompete their neighbors. Across ant species, polygyny is associated with large colony sizes and ecological dominance (Boulay, Arnan, Cerdá, & Retana, ), including other acacia‐ant mutualisms (Kautz, Pauls, Ballhorn, Lumbsch, & Heil, ; McGlynn, ), and polygyny is also common among highly competitive invasive ant species (Tsutsui & Suarez, ). In the A. drepanolobium system, it is unknown whether higher worker populations are the result of polygyny or some other difference(s) among the different ant species. The only research to date on queen number in this system is that of Rubin et al. (), who used microsatellite markers to show that C. mimosae colonies are commonly polygynous. However, no further work on the remaining three species has been performed to test the hypothesis that queen number underlies competitive ability in these ants.
To learn more about the colony structure of all four common ants in this system, we genotyped multiple same‐colony workers for each of the four species of ant associates using double‐digest restriction‐site associated DNA sequencing (RADseq). This reduced‐representation genomic sequencing method generates DNA sequences of sites near restriction enzyme cut sites, providing a repeatable subset of the genome at a relatively low cost (Peterson et al. ). Using hundreds of single‐nucleotide polymorphisms for each of the four ant species, we reconstructed intra‐colony relationships and were able to examine the degree of polyandry and polygyny of the ant species inhabiting A. drepanolobium.
From February to April 2012, ants were collected from A. drepanolobium trees tagged in the long‐term monitoring plot of the Center for Tropical Forest Science‐Forest Global Earth Observatories (CTFS‐ForestGEO) at Mpala, Kenya. For each of the four species of ant, about 15 trees were selected, and at least eight workers collected into 95%–100% ethanol. Because only (female) workers were collected, all sequenced individuals were diploid. In June 2015, the sizes of the selected trees were measured using two metrics: height of the tallest part of the canopy, and diameter of the stem at 0.5 m height. The CTFS‐ForestGEO plot is divided into 20 m quadrats; to ensure that we did not sample multiple trees occupied by the same colony, we generally did not sample workers of the same species from trees that occupied the same or neighboring quadrats. When our method of random selection chose trees from the same or neighboring quadrats, we later checked to see whether workers across those colonies shared a parent; we did not find any examples of this. For C. sjostedti, which occupies substantially more trees per colony than the other ants (Palmer et al., ), we did find two trees sharing some parents that were two quadrats away (about 40 m). At this distance, it is difficult to determine whether these represent one extremely large colony (Palmer et al., found that C. sjostedti colonies occupy on average 22 trees, which represents an area about 12 meters in radius at our site), or two closely related colonies, and so we did not combine the colonies in subsequent analyses.
We extracted DNA from each worker using an AutoGenprep 965 Tissue/ES Cell DNA Extraction Kit, using the Mouse Tail protocol for animal tissue. For this and subsequent steps, we followed the manufacturer's recommended protocols except as described below. Genomic DNA was stored at −20°C before use.
The amount of genomic DNA was then increased by whole genome amplification, using the REPLI‐g mini kit in 15 or 20 μl reactions.
We used the double‐digest restriction‐site associated DNA sequencing (RADseq) protocol of Peterson, Weber, Kay, Fisher, and Hoekstra (). We modified their protocol in a number of respects: We started with an (amplified) genomic DNA mass of 150 ng, which we then digested with the restriction enzymes EcoRI‐HF and BfaI under the manufacturer's recommended conditions. Bead cleanups throughout the protocol were performed with a MagNA bead solution described by Rohland and Reich () in place of Agencourt AMPure beads. We added 1.5× volume MagNA beads to the solution to be cleaned, but otherwise followed the same default protocol provided with Agencourt AMPure beads. We used the 48 inline indices for EcoRI described in the Sequences‐S1 spreadsheet in the supplement of Peterson et al. (). We chose a range of 264–336 bp for the size selection step, which we performed using 2% ethidium bromide cassettes on a Sage Science Pippin Prep machine. The final PCR was set for 10 cycles.
These libraries were then sequenced in 100 bp, single‐end reads on four lanes of an Illumina HiSeq 2000 and six lanes of a HiSeq 2500 at the Harvard University Bauer Core Facility. The bulk of the libraries for C. sjostedti, C. mimosae, and C. nigriceps, along with a few libraries for T. penzigi, ran on six lanes of the HiSeq 2500. Most of the libraries for T. penzigi, along with a small number of libraries from the other species, were run on four lanes of the HiSeq 2000.
To demultiplex the Illumina libraries, as well as to align reads across worker ants and call single nucleotide polymorphisms (SNPs), we used the program Stacks version 1.21, using the default parameters for this and all software analyses except as described below (Catchen, Amores, Hohenlohe, Cresko, & Postlethwait, ; Catchen, Hohenlohe, Bassham, Amores, & Cresko, ). Reads were demultiplexed using the process_radtags function of stacks, rescuing barcodes and RAD‐tags, and disabling checking if the RAD site was intact.
We quality filtered reads using the FASTX‐Toolkit version 0.0.13 (
We then aligned all reads for all workers within each species using the denovo_map.pl script of Stacks, allowing five mismatches between loci when processing a single individual, and five mismatches when building the catalog. In addition, we explored several different values for these parameters and found that the above combination produced the most SNPs, without substantial increases in heterozygosity that could indicate that different loci were being inappropriately combined (see SI for details). To build the final matrix of SNPs, we culled individuals for which sequencing had failed or had produced too low coverage to be useful (i.e., had <20% SNP coverage when run through a preliminary populations run with ‐r = 0.5), leaving, on average, about six worker libraries per tree. We called SNPs using the populations program of Stacks. A SNP was only processed for the ants from a single tree if it was present in at least r of the individuals in the species (r cutoffs were set to produce around 500 SNPs total per species: for C. sjostedti: 0.5, C. mimosae: 0.5, C. nigriceps: 0.75, T. penzigi: 0.5). We also used the –max_obs_het flag to filter out all SNPs with an observed heterozygosity >0.5, and the –min_maf flag to filter out all SNPs with a minor allele frequency less than 0.02. Heterozygosity was calculated using the adegenet package version 2.0.1 (Jombart, ; Jombart & Ahmed, ) in R version 3.2.3 (R Core Team ).
We then compared the average relatedness of each worker ant to every other ant of the same species. We compared the relatedness values across species, for both (i) workers from the same tree (within‐tree) and (ii) workers from different trees (between‐tree). We determined relatedness values using the method of Lynch and Ritland () implemented in the R package related (Pew, Muir, Wang, & Frasier, ). We chose the Lynch and Ritland method because in simulations it performed better than four other methods of calculating relatedness also implemented in related: those of Queller and Goodnight (), Li, Weeks, and Chakravarti (), Ritland (), and Wang (). Using Family‐Sim version 1.0 (
To determine the relationship between individuals collected from the same tree, we used the program COLONY version 2.0.6.3 (Jones & Wang, ). COLONY estimates a number of paternal and maternal genotypes, assigning each reconstructed father or mother as a parent of one or more of the observed, genotyped individuals. We ran COLONY under the default run parameters, except for changing the mating system to polygamy for both males and females and the ploidy to haplodiploidy. We set each locus as codominant, with the allele frequency as “unknown,” with an allelic dropout rate of 0.0001 and an additional error rate of 0.0025. The genotypes for two queens, one each for C. nigriceps and T. penzigi, were included in the offspring genotypes with the worker genotypes. They were also given to COLONY as possible maternal genotypes (alongside any inferred maternal genotypes), with a prior probability of their being the mother of any one of the offspring set at .5 divided by the number of trees in the data set. We used the most likely sibship configuration output to calculate a Polygyny Index and Polyandry Index for each species. We defined the Polygyny and Polyandry Indices as the number of different mothers (i.e., queens) and fathers, respectively, that were estimated to give rise to the workers within each tree. The number of queens and males recovered from the sampled workers is likely to underestimate the total genetic diversity of all workers in a given colony due to the relatively low proportion of workers sampled per colony, but these indices nevertheless allow for the unambiguous comparison of relative degrees of polygyny or polyandry among the different ant species. Furthermore, for each estimated queen, we also looked for multiple mating by recording the number of different males estimated to be the father(s) of her worker offspring. For this purpose, only data from those queens that had at least four offspring among the genotyped workers were used. Finally, for each colony, we calculated a metric of queen dominance by calculating the proportion of the genotyped workers that were daughters of the queen with the most offspring in that colony; we did this for the male that sired the most worker offspring as well.
We recovered the estimated maternal genotypes from COLONY runs, using the same parameters as above, but excluding the possibility that workers from different trees shared a parent. Genotypes for any allele to which COLONY assigned a <.90 probability were recorded as missing data. To determine whether the mothers reconstructed from each tree were related to each other, we ran these putative maternal genotypes in COLONY again, using the same parameters as above, and recorded whether each pair of estimated mothers were full‐siblings, half‐siblings, or unrelated.
If colonies with more queens are better able to compete for large and valuable trees, this could produce a correlation between colony structure and tree size. We looked for this by testing whether tree size influenced within‐tree relatedness, Polygyny Index, Polyandry Index, and males per queen, using the Pearson correlation test when the data were approximately normal (or could be transformed to normality: male mates per queen data were square‐root transformed), and Spearman's rank correlation otherwise. We also took into account tree size and ant species using the lm function of R to perform an analysis of covariance (ANCOVA), with height or diameter as the covariate. For each test, there was no significant interaction between ant species and tree size, so we did not include an interaction term in the results presented below. Tree size was measured in two ways, height and diameter at 0.5 m above ground; we present only the results for height here, as height and diameter were strongly correlated and the results of the tests qualitatively identical. The results of tests on tree diameter may be found in Data S3 of the Supporting Information.
As we found no significant effect of tree size on any of these factors, we did not include tree size as a covariate in our final analyses. Comparisons among ant species for between‐tree relatedness, within‐tree relatedness, Polyandry Index, Polygyny Index, and males per queen were performed using analysis of variance (ANOVA) when the data were relatively normally distributed, or Kruskal–Wallis tests (KWT) otherwise. Post hoc comparisons were carried out using Tukey's honest significant difference test (Tukey's HSD) for ANOVA and the Nemenyi post hoc test for KWT.
For between‐tree relatedness, we compared each species’ distribution to zero using Student's one‐tailed t test.
For maternal relatedness, we compared the proportion of sibling queens within nests to the proportion of sibling queens between nests using Fisher's exact test.
Statistics were carried out in R. The Nemenyi post hoc tests were performed using the PMCMR package (Pohlert, ).
After DNA sequence filtering, alignment, and SNP calling, we produced genotypes for 300–750 SNPs for each species (Table ).
Results of RADseq genotyping: total reads, SNPs per worker ant, total SNPs, and average observed heterozygosity across all SNPsSpecies | Trees (colonies) | Workers/tree | Reads/worker | SNPs | Matrix completeness (%) | H obs |
Crematogaster sjostedti | 16 | 5.6 | 356,000 | 746 | 56 | 0.10 |
Crematogaster mimosae | 14 | 6.1 | 370,000 | 669 | 59 | 0.13 |
Crematogaster nigriceps | 18 | 6.6 | 420,000 | 764 | 84 | 0.18 |
Tetraponera penzigi | 13 | 5.8 | 428,000 | 309 | 58 | 0.11 |
Matrix completeness represents the proportion of loci across all individuals for which a genotype was determined. Hobs, or heterozygosity, is the proportion of individuals that have two different alleles for a given locus, averaged across all loci.
The average relatedness of ants within and between trees for each species is shown in Table and Figure a. The average relatedness between trees was not significantly greater than zero for any of the ant species (Student's t test, p > .05 for all). There were significant differences in the distributions of relatedness among the four species (KWT, p < .001; distributions and the results of the Nemenyi post hoc tests are shown in Figure a).
Relatedness of workers within and between trees in the CTFS‐ForestGEO plot at MpalaSpecies | Trees sampled | Between‐tree relatedness | Within‐tree relatedness | Polygyny Index | Queen dominance | Polyandry Index | Male dominance | Males per queen |
Crematogaster sjostedti | 16 | −0.12 ± 0.02 | 0.38 ± 0.05 | 1.4 ± 0.1 | 0.87 ± 0.05 | 4.1 ± 0.5 | 0.46 ± 0.08 | 3.7 ± 0.5 (n = 14) |
Crematogaster mimosae | 14 | −0.04 ± 0.01 | 0.26 ± 0.05 | 2.9 ± 0.4 | 0.68 ± 0.07 | 4.6 ± 0.4 | 0.35 ± 0.04 | 3.7 ± 0.3 (n = 9) |
Crematogaster nigriceps | 18 | −0.04 ± 0.00 | 0.58 ± 0.02 | 1.3 ± 0.2 | 0.97 ± 0.02 | 2.7 ± 0.3 | 0.72 ± 0.05 | 2.4 ± 0.3 (n = 18) |
Tetraponera penzigi | 13 | −0.05 ± 0.01 | 0.18 ± 0.04 | 3.5 ± 0.4 | 0.54 ± 0.06 | 4.6 ± 0.4 | 0.38 ± 0.04 | 3.0 ± 0.4 (n = 4) |
Values shown are means ± SE.
To calculate the Number of males with which each queen mated, we only considered those queens with at least four offspring among the workers; the number of these queens is given after the number of males per queen in parentheses. Queen dominance is the proportion of genotyped workers who are offspring of the queen with the greatest number of offspring among the genotyped workers. Male dominance is analogous, but for the male with the most offspring. The Polygyny Index is a relative measure that refers to the number of queens per tree as estimated using the data specified in Table . The Polyandry Index is similarly a relative measure of the number of males per mated queen estimated from the workers sequenced from each tree.
Average relatedness of workers between trees is close to zero, but relatedness within trees is high, and differs among ant species. (a) shows relatedness between ants on different trees (between‐tree comparisons); (b) shows relatedness between ants on the same tree (within‐tree comparisons). The species are arranged left to right in order from most to least competitively dominant. Boxplots show the median and inter‐quartile range for each species. Dots underlying each boxplot show the average relatedness between each pair of trees (a) or within each tree (b); they are jittered horizontally better to show their distribution. Lines above the boxplots denote significant differences between species as follows: *p < .05; **p < .01; ***p < .001. In (a), although the distributions are significantly different among the species, none are significantly greater than zero
Tree height did not correlate with within‐tree relatedness either across all ant species (Pearson's correlation test, p = .8) nor within species (ANCOVA, p = .7). However, the average within‐tree relatedness did vary among species (ANOVA, p < .001), as shown in Table and Figure b. Post hoc comparisons show that C. nigriceps had higher within‐tree relatedness than the other three species, and that C. sjostedti had a higher within‐tree relatedness than T. penzigi (Tukey's HSD test, p < .01); this pattern corresponds to the lower polygyny indices of C. nigriceps and C. sjostedti colonies, discussed below.
Across all four ant species, we found no overall correlation between the Polygyny Index and the height of that tree (Spearman's rank correlation, p = .4), nor did we find evidence for a correlation between Polygyny Index and height within ant species (ANCOVA, p = .8).
However, we did find a strong effect of ant species on degree of polygyny (KWT, p < .001). Tetraponera penzigi and C. mimosae typically had higher Polygyny Indices, while C. sjostedti and C. nigriceps both had Polygyny Indices close to 1 (Table , Figure a). Post hoc tests found significant differences between C. mimosae and T. penzigi on the one hand, and C. nigriceps on the other, as well as between T. penzigi and C. sjostedti (Nemenyi tests, p < .05). In both C. mimosae and T. penzigi, despite averaging multiple queens per colony, a single queen appeared to be the mother of a disproportionate number of offspring, accounting for 68% and 54%, on average, of the genotyped workers. Finally, for the two queens recovered during sampling, the C. nigriceps queen was recovered as the mother of the workers from that tree, while the T. penzigi queen was recovered as sister to her colony mates, rather than as their mother.
Ant species vary in Polygyny Index, Polyandry Index, and number of male mates per queen. (a) The number of queen genotypes recovered from each tree; (b) the number of male genotypes recovered from each tree; (c) the number of male genotypes recovered from the offspring of each recovered queen (including only those recovered queens with a minimum of four offspring sampled in our data set). The species are arranged left to right in order from most to least competitively dominant. Boxes show median and inter‐quartile ranges. Dots behind each plot show the number of genotypes recovered from each tree (from each queen for c); the values are jittered slightly to help display the data. Lines above the boxplots denote significant differences between species as follows: *p < .05; **p < .01; ***p < .001
Across all species, we found no significant correlation between the Polyandry Index and the height of that tree (Spearman's Rank Correlation, p = .6), or any correlations for one or more individual species (ANCOVA, p = .6).
The Polyandry Index differed among ant species (KWT, p < .01). For C. sjostedti, C. mimosae, and T. penzigi, the workers collected from each tree were fathered by about 5–6 males, whereas for C. nigriceps, workers were fathered by about half that many males (Table , Figure b). Post hoc tests found significant differences only between C. nigriceps on the one hand and C. sjostedti and C. mimosae on the other (Nemenyi tests, p < .05).
We found no significant correlation between the number of males with which each queen had mated (including only queens that were the mothers of at least four genotyped progeny) and the height of the tree occupied by those ants (Pearson's correlation test, p = .5). We also did not find evidence for a correlation between queen polyandry and tree size for any single ant species (ANCOVA, p = .9).
The queens of different species showed no significant differences in their number of matings (ANOVA test, p = .06). Queens of C. sjostedti and C. mimosae averaged 3–4 mates per queen, while C. nigriceps and T. penzigi were around 2–3 (Table , Figure c). These (nonsignificant) differences may be due to chance, or to a reduced sample size, as some queens were excluded from this analysis because they had fewer than four offspring among the workers.
For C. sjostedti and C. nigriceps, only a few of the inferred queens came from the same tree; however, some of these queens were related to each other (Table ). Crematogaster mimosae had multiple inferred queens per tree. These were also commonly siblings, at a higher rate than that found between queens from different trees (Fisher's exact test, p < .05). However, T. penzigi showed a different pattern: despite having multiple inferred queens per tree, these queens were very rarely siblings, and the rate was not significantly different from the rate of sibship between queens from different trees (p = .3). The queen we collected from a T. penzigi colony was determined by COLONY to be a sister to the workers in that tree.
Relatedness of inferred queensSpecies | Number of trees | Number of inferred queens | SNPs | Matrix completeness (%) | Proportion of related queens from the same tree | Proportion of related queens from different trees |
Crematogaster sjostedti | 16 | 21 | 746 | 100 | 0.20 (1/5) | 0.04 (8/205) |
Crematogaster mimosae | 14 | 35 | 669 | 100 | 0.20 (8/39) | 0.09 (52/556) |
Crematogaster nigriceps | 18 | 22 | 764 | 100 | 0.14 (1/7) | 0.01 (2/246) |
Tetraponera penzigi | 13 | 39 | 309 | 100 | 0.09 (4/44) | 0.06 (39/697) |
For each proportion, the raw number of related queens and possible comparisons is given in parentheses.
We found no evidence that the genetic structure of colonies—in terms of polygyny, polyandry, or within‐tree relatedness—underlies competitive ability, either within or between species, in the ant associates of A. drepanolobium.
Between species, there was no association between polygyny and competitiveness: Our results do not support the hypothesis that the competitive C. sjostedti and C. mimosae are more polygynous than the less competitive C. nigriceps and T. penzigi (Palmer, ; Stanton et al., ). Palmer () observed seven C. sjostedti queens in a single colony fragment, but we found little evidence for polygyny in this species and suspect that the observed queens were not yet mated, but were still in the process of budding off from their natal colony. C. sjostedti alates and foundress queens are rarely found, and this species is believed to reproduce primarily via colony budding (Stanton et al., ).
Our results also show that T. penzigi colonies are polygynous. A previous report indicates that this species was monogynous, based on the dissection of colonies (cited in Stanton et al., ). We have also observed that small trees containing colonies of T. penzigi tend to have only one laying queen, based on the collection of the ants inhabiting about 20 small (averaging 1.0 m high) trees of T. penzigi in 2016 (Boyle and Pierce, unpublished data). It is possible that the multiple maternities of workers observed a in single colony of T. penzigi are partly a relic of the colony founding event, as seedling stems of A. drepanolobium (considerably younger than the small trees surveyed for queens above) typically have a foundress queen in every domatium, and these foundresses are disproportionately T. penzigi (Stanton et al., ). Possibly the victorious foundress and/or her workers eliminate the competing queens, but tolerate their worker offspring, or continue to raise their brood, as do slave‐making ants. This scenario would result in a colony with a single queen, but a worker population with multiple mothers. This would also be consistent with our finding that a disproportionate number of workers are the offspring of a single queen (about half). This hypothesis could be tested by following individual colonies of T. penzigi over time, with the expectation that the colony would become more genetically homogenous as the absorbed workers died out and were replaced by the queen's daughters; if the colony remained genetically heterogenous over time, this would favor either multiple queens or the constant absorption of workers from neighboring T. penzigi colonies. Whatever the explanation, even if T. penzigi colonies are socially monogynous, it remains the case that polygyny does not underlie the competitive hierarchy, as only one of the two more competitive species, C. mimosae, showed evidence of polygyny.
The nature of polygyny also appears to differ among the different species of ants. In the polygynous colonies of C. mimosae, multiple queens are often related to each other, possibly due to daughter queens remaining in their natal nests. This was suggested by Rubin et al. for C. mimosae (), and it may also be the case for the rare colonies of C. sjostedti and C. nigriceps for which we found evidence of polygyny (i.e., a Polygyny Index > 1). These Crematogaster colonies also accepted unrelated queens (or at least, accepted the offspring of unrelated queens), although this appeared to be less common in these ant species than in T. penzigi. Queens in polygynous colonies of T. penzigi, in contrast to the other three species, were rarely related to each other, which is consistent with the possibility that the multiple maternity of T. penzigi workers is a relic of competing foundresses.
The Polygyny Index we present here is not an exact estimate of the true genetic diversity within a tree. When the number of queens and/or males is high relative to the number of workers sampled per tree, as for C. mimosae, then our estimates are likely to be underestimates. Further work with larger worker sample sizes will be necessary to infer the absolute degrees of polygyny and polyandry. However, to evaluate whether different colony structures underlie competitive ability, we only need to determine whether the competitively dominant species are more polygynous and/or polyandrous than the competitively subordinate species. Our results provide a sufficiently strong estimate of the relative degree of polygyny and/or polyandry among these four ant species that we can rule out this possibility.
Colonies of C. sjostedti and C. mimosae usually occupy multiple trees (and C. nigriceps moderately so; see Palmer et al., ), and if workers from different trees are not thoroughly mixed, then sampling from a single tree will only capture a subset of the genetic lineages in a colony. However, there is good reason to believe that the workers do mix well, as Young et al. () noted that C. sjostedti and C. mimosae ants readily move along the ground between trees, and we have observed this ourselves. Moreover, Palmer created artificial barriers to the flow of workers between different trees of the same colony and found that this reduced competitive ability to the extent that the colonization hierarchy could be reversed (). Both observations suggest that workers among trees within a single colony show sufficient movement that sampling from single trees, as we did, is adequate to capture the diversity of the entire colony, even if it is spread over more than one tree.
Our results also do not support the hypothesis that polygyny plays a role in intra‐specific contests. Across the four species, more competitive ants occupy larger, more valuable trees; however, we did not find an association between queen number and tree size, either within or across ant species. However, as single ant colonies can occupy multiple trees, it is still possible that more polygynous colonies spread across a greater number of trees of the same size class than do their less polygynous conspecifics.
Two lines of research arise naturally from the findings we present here. First, if polygyny does not contribute to interspecific (or intraspecific) variation in colony size, what factors do? Some alternative hypotheses, such as differences in how resources are exploited, or how they are allocated to workers versus reproductives, have already been proposed (Palmer, ) and could be explicitly tested. Second, the variation we do observe in polygyny merits greater investigation at both proximate and ultimate levels. Our data suggest that both polygynous species may commonly accept unrelated queens and/or their offspring, but that Crematogaster spp. colonies may also contain multiple related queens; however, a finer‐grained description of these patterns could also shed light on the consequences of polygyny (and polyandry) in these species. For instance, honeybee colonies with multiple patrilines reproduce more than single‐patriline colonies, possibly because a genetically diverse worker population is able to forage across a wider range of conditions (Mattila & Seeley, ). While polygyny and polyandry do not seem to affect colony size, they may still have consequences for the fitness both of the ant colonies in question and their host trees.
Our work demonstrates the utility of RADseq data in determining family structure, especially in nonmodel systems. RADseq has previously been used to identify parent–offspring relationships where the pool of possible parents is known and genotyped (Kess, Gross, Harper, & Boulding, ), and to search for related individuals within a population (Hellmann et al., ; Kjeldsen et al., ). To our knowledge, our study is the first to use RADseq data to determine the number of parents giving rise to a set of (potentially sibling) offspring, and the first to use RADseq data to determine any kind of kinship relationship in a social insect. This information is important in social insects, for which polygyny and polyandry are both of particular relevance in the evolution and maintenance of eusociality (Boomsma, Kronauer, & Pedersen, ). This analysis can also answer other questions, such as quantifying extra‐pair paternity. Although RADseq produces single‐nucleotide polymorphisms, which are individually less informative than microsatellite markers, it produces a great many of them, allowing relationships to be resolved with even greater specificity than with microsatellites. For instance, Weinman et al. found that 102 SNPs had power comparable to 15 microsatellites for identifying parentage in a cooperatively breeding bird, and in fact the SNPs performed better when parents were related (), as appears to be the case among some of the ant associates of A. drepanolobium. RADseq is especially useful in the many systems for which microsatellite markers have not yet been identified, as no pre‐existing genomic information is needed in order to recover RADseq markers (unlike microsatellites, for which loci must be identified and primers designed beforehand, a potentially expensive and time‐consuming process). In our case, RADseq markers allowed us to conclude that polygyny does not drive competition in the ant associates of A. drepanolobium, and we should investigate other factors that could promote differences in competitive ability between species, such as distribution of colony biomass among different castes and foraging differences (Palmer, ), or differences in relative rates of development, in diet, and/or abilities to form cohesive colonies across multiple trees.
Interactions among A. drepanolobium's ant associates are not uniform across East Africa. For example, Hocking noted that the proportion of trees occupied by particular ants varied widely from site to site: He rarely found C. sjostedti in his sites in the southern part of the A. drepanolobium range (). This ant, however, is the competitively dominant species in the northeastern part of the range of A. drepanolobium at the Mpala Research Centre where most of the research on this system has taken place. Similarly, competitively dominant ants in some habitats may be subordinate in others: Palmer found one site with a different soil profile where the competitive hierarchy was partially reversed, with C. nigriceps dominant over C. mimosae (). To understand how and why the competitive hierarchy changes across the range of A. drepanolobium, as well as the ecological consequences of these changes, it will be necessary to understand more about factors that promote competitive ability between the different ant species.
We thank Simon Akwam, Gilbert Busienei, Jeremy Longor, Julius Katero, Isaack Leting, Chris Baker, Richard Childers, Walker Darling, and Nanfang Yu for field assistance and advice. We are especially grateful to Anne Powys and Gilfrid Powys at Suyian for their gracious hospitality. We also thank Stuart Davies, Scott Miller, the Mpala CTFS‐ForestGeo team, and the Mpala Research Centre staff for making our fieldwork possible. Brant Peterson, Jesse Weber, and Hopi Hoekstra taught JHB how to use RADseq methods, and helped with the bioinformatics; Ian Butler, Rachel Hawkins, Lukas Rieppel, and Maggie Starvish provided advice and support in the laboratory. Jinliang Wang advised us on COLONY. The research benefited from the advice of Scott Edwards, Brian Farrell, and David Haig. We are grateful to the anonymous reviewers whose feedback improved this study. JHB was supported by a Graduate Fellowship from the Department of Organismic and Evolutionary Biology and the Smith Family Fellowship. DJM's work in Kenya is supported by the National Geographic Society, the Turkana Basin Institute, Suyian Trust, the National Museums of Kenya and Nature Kenya. This research was supported the Putnam Expeditionary Fund of the Museum of Comparative Zoology, an FQEB grant from the John Templeton Foundation, and NSF SES‐0750480 to NEP.
None declared.
Sequencing files may be found in the NCBI Sequence Read Archive, BioProject PRJNA414448. Scripts for filtering, SNP calling, etc., R scripts for statistical analyses, and tree size data may be found in dryad,
JHB, DJM, and NP designed the study. JHB, DJM, and JP did the fieldwork to collect the ants. PMM, SK, SKN, and DK provided data on the trees. JHB generated and analyzed genotype data. JHB and NP wrote the manuscript with the input of all co‐authors.
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Abstract
The Acacia drepanolobium (also known as Vachellia drepanolobium) ant‐plant symbiosis is considered a classic case of species coexistence, in which four species of tree‐defending ants compete for nesting space in a single host tree species. Coexistence in this system has been explained by trade‐offs in the ability of the ant associates to compete with each other for occupied trees versus the ability to colonize unoccupied trees. We seek to understand the proximal reasons for how and why the ant species vary in competitive or colonizing abilities, which are largely unknown. In this study, we use
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1 Department of Organismic and Evolutionary Biology, and Museum of Comparative Zoology, Harvard University, Cambridge, MA, USA; Department of Biology, The College of William and Mary, Williamsburg, VA, USA
2 Department of Organismic and Evolutionary Biology, and Museum of Comparative Zoology, Harvard University, Cambridge, MA, USA; Mpala Research Centre, Nanyuki, Kenya; Turkana Basin Institute, Stony Brook University, Stony Brook, NY, USA
3 Department of Integrative Biology, University of California, Berkeley, Berkeley, CA, USA
4 East African Herbarium, Botany Department, National Museums of Kenya, Nairobi, Kenya
5 Department of Land Resource Management and Agricultural Technology, University of Nairobi, Nairobi, Kenya
6 Mpala Research Centre, Nanyuki, Kenya
7 CTFS‐ForestGEO, Smithsonian Tropical Research Institute, Washington, DC, USA
8 Department of Organismic and Evolutionary Biology, and Museum of Comparative Zoology, Harvard University, Cambridge, MA, USA