2009 NORTHEASTERN NATURALIST 16(1):113–124
Demography and Reproduction in the Cavity-dwelling Ant
Stenamma diecki (Emery) (Hymenoptera: Formicidae)
Vickie L. Backus1,* and Joan M. Herbers2
Abstract - Stenamma diecki is a small ant with a widespread distribution. Systematic
plot excavations in two locations have allowed us to collect data on a large number of
S. diecki nests in order to examine seasonal and spatial differences in nest demography
and allocation decisions within this species. Populations of this species from New York
and Vermont nest in cavities far more commonly than has been reported, and thus we
could compare our results with data on this species and with patterns of demography
and reproduction for two other well-studied cavity-dwelling ants. We found nests were
monogynous at all locations, but showed considerable variation in mean queen number
and mean worker number. Most nests did not produce any males or reproductive
females in a season, and this pattern was also site specific. Sexual and reproductive allocation
was similar for all sites tested. Finally, demographic patterns within a site over
3 seasons are consistent with those predicted by seasonal polydomy.
Introduction
Stenamma diecki (Emery) (subfamily Myrmicinae, tribe Stenammini) is
a small, cavity- and soil–dwelling ant with a widespread distribution in the
US and southern Canada (Bolton et al. 2007). Its small size and cryptic habits
have meant that few researchers have reported on its natural history. Cole
(1940) reported that it is typically found in wet forests and Picea rubens
Sarg. (Red Spruce) forests in the Great Smoky Mountains National Park.
Subsequent reports have confirmed this habitat preference in populations
as far north as near Montreal, PQ, Canada (Francoeur 1965, 1966; Letendre
and Pilon 1972) and across the US, including Michigan (Talbot 1975) and
California (Smith 1957, Snelling 1973). Where nests have been censused,
worker numbers are typically low (mean worker number ranges from 31.8
per nest [Francoeur 1965] to 56.0 per nest [Talbot 1975]). Nests are generally
headed by a single queen (Francoeur 1965, Letendre and Pilon 1972,
Talbot 1975), although 0 queen nests are occasionally found (Letendre and
Pilon 1972); polygyny seems to be absent from this species (Talbot 1975).
While these reports seem to provide a complete description of the natural
history for this species, they have several limitations. In all cases, sample
size is low: n = 7 in Francoeur (1965), n = 10 in Letendre and Pilon (1972),
and n = 15 in Talbot (1975). In these studies, the collection of nests was
made using a non–systematic sampling scheme, and in two cases (Letendre
and Pilon 1972, Talbot 1975), over a time span of several years.
1Department of Biology. Middlebury College, Middlebury VT 05753. 2Department
of Evolution, Ecology, and Organismal Biology, Aronoff Laboratory, OH State
University, 318 West 12th Avenue, Columbus, OH 43210. *Corresponding author -
backus@middlebury.edu.
114 Northeastern Naturalist Vol. 16, No. 1
Recent work in northeastern temperate forests have shown that important
nest parameters such as number of queens, number of workers, and
both sexual and reproductive allocation ratios can vary both in time and
space for a guild known as the small, cavity-dwelling, northern temperate
forest ants. Two species in particular have been well studied: Temnothorax
(formerly Leptothorax) longispinosus (Roger) (Backus 1995, Herbers
1990), and Myrmica puncitventris Roger (Backus et al. 2006; Banschbach
and Herbers 1996a, b; DeHeer et al. 2001). Detailed analysis of these two
species has shown that reports focused on a single season, a single location,
or with low sample sizes such as those listed above for S. diecki may
miss important patterns in temporal and geographic variation in basic lifehistory
traits for a species.
Systematic plot excavations in New York and Vermont starting in 1980
by our laboratory have allowed us to collect data on a large number of S.
diecki nests, far exceeding the data available in the literature. Analysis of
these data and comparison with the published data on other cavity-dwelling
ants from the northern temperate forest will allow us to present a clearer
picture of the natural history of this small ant. In this paper, we examine
seasonal and spatial differences in nest demography and allocation decisions
within this species in order to present a more complete representation
of its natural history.
Methods
Table 1 shows the sources of the data we have included in this analysis;
data are available in Supplemental File 1 (available only online at http://
dx.doi.org/10.1656/N695.s1). Collection methods for each of the sources
varied. The data obtained from nests in Quebec (Francoeur 1965, Letendre
and Pilon 1972) as well as the nests collected in Michigan (Talbot 1975)
were collected at large.
The new data reported here used a systematic nest-excavation technique
described elsewhere (Herbers 1990). Two locations were extensively
sampled: the Edmund Niles Huyck Preserve in Albany County, NY and
Mallet’s Bay (now Niquette Bay) State Park in Chittenden County, VT.
Briefly, at each location, 25-, 36- or 49-m2 plots were set up, and every
potential nesting place was examined for ants. While our sampling methods
are not designed to explicitly detect soil–nesting species, all litter was
Table 1. Data sets used in this study. Nests are defined as those that contain at least 1 queen and
≥1 worker or 0 queens and ≥5 workers.
Site Source Number of defined nests
Michigan Talbot 1975 12
Quebec Francoeur 1965, Letendre and Pilon 1972 9
New York Our data 101
Vermont Our data 58
2009 V.L. Backus and J.M. Herbers 115
removed from the forest floor, and the bare soil was observed for the presence
of ants. Typically, S. diecki nests located in soil are superficial and
located underneath a covering rock or piece of wood (Smith 1957), and we
are confident that we have been able to find the majority of the nests in each
plot. The type of nest material being used was recorded at the time of collection.
Nests were brought, intact, to the laboratory where the species identity
was confirmed and the nests were censused. The census data we analyzed
below includes: number of dealate queens, number of workers, number of
male pupae and adult males, number of queen pupae and virgin queens, and
number of worker pupae. We weighed individual dealate queens, males,
and alate queens from several nests. Voucher specimens have been deposited
in the collection maintained by the University of Vermont (Burlington, VT)
and in J.M. Herbers’ personal collection.
These counts and weights were used to determine several commonly
reported socio-biological measures. The number of dealate queens in a
nest is a measure of that nest’s gyny level; monogynous nests are defined
as those with 1 queen present, whereas nests with greater than 1 dealate
female are defined as being polygynous. Worker number is a standard
estimate of the size of the nest. There are two commonly calculated
investment ratios that are reported for ant nests. The first, the sexual investment
ratio is the biomass of males reared relative to total biomass
of new sexuals corrected by the individual female:male energetic cost
ratio (Boomsma 1989). For this analysis, we used the energetic cost ratio
published by Trivers and Hare (1976). The second investment ratio is the
reproductive allocation ratio, calculated as the biomass of both male and
female sexuals reared relative to all new biomass, including workers; this
calculation estimates the nest’s investment in reproduction compared to
growth (Herbers and Banschbach 1998).
Preliminary examination of the data showed that some of the nests
brought to the laboratory were very small with no queens present, which may
represent transient groups of foragers. Thus, in order to be conservative, we
have chosen to limit the analysis to nests that had either: at least 1 queen
and ≥1 worker or 0 queens and ≥5 workers. Incipient nests (those with just 1
queen) were excluded from the analysis. For this analysis, we use the word
nest to refer to a group of individuals, as defined above, which occupies a
place at the same time. Colonies represent a group of genetically related ants
that may occupy multiple nests. Since we have not undertaken a detailed genetic
analysis of this species, we are able to present data for nests only. For
many of the sites and years data had been collected for fewer than 10 nests,
requiring us to combine sets for years in order to ask questions about site
effects on nest demographics. Preliminary analysis showed that there was no
effect of year on nest demography (V.L. Backus and J.M. Herbers, unpubl.
data), and thus we are confident that we are not confounding questions of the
effect of site with the effect of year in this analysis.
Results
Over the years, we excavated 73 plots in NY and 54 in VT. We found
S. diecki nests in 37 and 26 of those plots, respectively. Most plots had
no S. diecki nests, while a few had high density (Fig. 1). To determine
if nests were distributed in space randomly, we compared the observed
number of nests per plot with those expected if nests were distributed
randomly under a Poisson distribution. The difference between the observed
number of nests and expected was significantly different for both
sites (NY: χ2 = 127.10, df = 3, P < 0.001; VT: χ2 = 89.74, df = 3, P <
0.001 for nests collected in the summer only). This species therefore has
a patchy spatial distribution, and we were unable over the years to tie its
occurrence to any obvious ecological variable such as litter depth, canopy
cover, or soil moisture. Rather, nests occur in some parts of the forest and
not in others; such a patchy distribution is the rule rather than the exception
for this guild of forest ants.
Previous studies have reported that the preferred nest material for S.
diecki is in shallow soil nests or in the soil under rocks and logs (Cole 1940,
Smith 1957), and the data from MI and PQ sites confirm these reports. In
contrast, we found 67.7% of the NY nests and 87.5% of the VT nests were
in cavities (empty nuts, empty acorns, and intact sticks) compared to noncavity
sites (litter, soil, or rotten sticks). There was a significant difference
between the NY and VT populations (G = 7.76, df = 1, P < 0.05) with VT
nests being in cavities more often than their NY counterparts.
There was a wide difference in the mean number of queens found in the
nests for the sites (Fig. 2A). At each site, except PQ, a few nests had more
than 1 queen present. Nests in NY and VT tended to have more nests with 0
Figure 1. Density of nests per m2 for the NY and VT sites. The number of plots
sampled was 73 in NY and 54 in VT.
queens than those in MI or PQ. A G test of Independence showed that queen
presence was site specific (G = 24.36, df = 6, P < 0.001) with the NY and VT
sites having more 0 queen nests than reported for other sites.
Worker number was also variable between the sites. Nests from PQ and
MI were larger than nests from VT and NY (Fig. 2B) (F = 17.16, P < 0.0001).
The mean number of workers was similar for nests from MI and PQ and nests
from VT and NY were similar in size and significantly smaller than those
from MI and PQ.
As with the demographic measures, patterns of production were quite
variable for new females, males, and workers (Table 2). While most nests
produced some offspring each year, a small proportion of the nests in NY and
Figure 2. Nest demographic patterns for the 4 sites. A. Number of nests at each location
that contained 0 queen, 1 queen, or >1 queen. B. Mean ± SE number of workers
per nest.
118 Northeastern Naturalist Vol. 16, No. 1
VT failed to rear any brood to eclosion in a season. Following the classification
used by Herbers (1990), we assigned each nest to a producer class: none
(produced 0 sexuals), minor (produced 1–4 sexuals) or major (5 or more
sexuals produced). Due to sample size problems (Fig. 3), only nests from
VT and NY were statistically compared to determine if there was an effect
of site on sexual production. Nests from Vermont were assigned to the major
producer class more often than nests in NY, which tended to show very little
reproduction (G = 15.25, df = 2, P < 0.05).
Two additional measures were calculated: sex allocation and reproductive
allocation. In order to reduce the skewing of the data by nests that produced
very few sexuals we used the convention of Herbers (1990) to determine allocation
patterns for nests only in the major producer class. Low sample size
meant that nests from PQ were excluded from the analysis. While it appears
as if the nests from NY produced slightly more males than females (Fig. 4A),
there was no significant difference in sexual allocation between the 3 sites
tested (ANOVA on arcsine transformed proportions F = 2.94, P > 0.05). In
addition, there was no effect of site on the allocation of resources between
Figure 3. Percentage of nests in each producer class at each site. Classes are defined as
follows: none = no reproductives produced that season, minor = 1 to 4 reproductives
produced that season, and major = 5 or more reproductives produced that season.
Table 2. Production data for the MI, NY, and VT sites. Values are the percent of nests producing
at least 1 offspring of each type. The PQ site has not been included due to low sample size.
Type of offspring MI NY VT
Males 69.2 42.7 60.7
Females 61.5 25.6 57.1
Workers 100.0 85.4 89.3
No brood 0.0 11.0 5.3
2009 V.L. Backus and J.M. Herbers 119
sexual production and growth (new workers) (Fig. 4B) (ANOVA on arcsine
transformed proportions F = 0.83, P > 0.05).
One explanation for the nest size differences observed between the
populations may be geographic variation in seasonal polydomy. Polydomy
occurs when colonies fragment to occupy multiple nest sites at one time.
Colonies can be polydomous year round or seasonally; in the latter case,
colonies divide into subunits during the spring and fuse into a single nest
before overwintering. Sample sizes across seasons were sufficient for the
demographic analysis of NY nests only. The data show a pattern consistent
Figure 4. Allocation in nests during a season. A. Population-wide proportional investment
in males based on dried weight. P(m) = 1.0 means that all sexual biomass
was invested in males. B. Mean ± SE. proportional investment in sexuals based on
dried weight. PR = 1.0 means all new biomass produced was invested in sexuals with
no growth (workers) produced.
120 Northeastern Naturalist Vol. 16, No. 1
with that predicted by a model of seasonal polydomy (Fig. 5 A, B), that is,
nests have significantly more queens and more workers in the spring and in
the autumn (during the coalescent phase of polydomy) and fewer queens and
workers present in the nest during summer when the colony has undergone
fission (ANOVA on square root transformed number: Queens—F = 4.09, P =
0.02; Workers—F = 10.62, P < 0.0001).
Discussion
The data presented here allow us to add to the existing body of knowledge
concerning the natural history of Stenemma diecki and allow us to suggest
some fruitful directions for future studies on this ant.
Figure 5. Nest demography for NY nests only over 3 seasons. A. Mean ± SE number
of queens per nest. B. Mean ± SE number of workers per nest.
2009 V.L. Backus and J.M. Herbers 121
Our data represent an order of magnitude more nests than have previously
been reported in the literature. Furthermore, by using a systematic
collection scheme, we have a more complete idea of the range of nesting
behavior and demography for this species than hitherto available. The results
show that S. diecki uses cavities (empty nuts, empty acorns, and hollow,
intact sticks) much more often than has been previously reported. Thus, this
species clearly belongs to the guild of northeastern, temperate forest, cavitydwelling
ants that has been the focus of our research starting with Herbers
(1986). Species in this guild have been well characterized on several important
life-history traits, and we proceed to compare our results on S. diecki to
species better known.
S. diecki nests tend to have 0 or 1 queen; multiple-queen nests occur
only rarely. Indeed, Talbot (1975) concluded that this species was monogynous
in spite of data showing that 2 of the 15 nests she collected had >1
queen. Our larger collections from VT and NY show that the proportion of
multiple-queen nests in each population is very low but detectable. Talbot
(1975) attributed the extra queens as new alates that were produced during
that year; while reasonable, testing this hypothesis will require dissection
and genetic analysis.
The absence of clear evidence of polygyny in this species is somewhat
surprising given both the widespread existence of polygyny in other
cavity-dwelling ants from the same locations that we sampled, including:
Temnothorax longispinosus (Herbers 1990), T. ambiguus (Emery) (Herbers
and Grieco 1994), and Myrmica puncitventris (Banschbach and
Herbers 1996a). Polygyny is a remarkably labile trait (c.f. Herbers 1993)
and its causes and consequences are not well understood. Indeed populations
of a single species (M. puncitventris) reported on here at the NY site have
changed in their tendency to be polygynous over time (Backus et al. 2006,
DeHeer et al. 2001); thus, it will be interesting to follow S. diecki to see if
queen number is labile in this species as well.
We found strong geographic variation in the number of workers in a S.
diecki nest. In large part, the differences in demography between MI and
PQ populations and the VT and NY populations probably reflect collecting
technique. Our systematic plot excavation methods in NY and VT insured
that smaller nests were collected, whereas larger, more obvious nests were
undoubtedly over-represented from MI and PQ.
On the other hand, geographic variation in nest demography is well documented
for other cavity-dwelling temperate forest ants collected in these
sites (Banschbach and Herbers 1996a, Herbers 1990) and it is possible that
the differences between the MI and PQ populations and the NY and VT nests
may be confirmed by systematic collection in the first two locations. Thus,
more research is needed in order to understand how site affects demography
in this guild.
One-third to one-half of S. diecki nests failed to rear any sexuals in
a given year. Failure to reproduce may reflect the high cost of rearing
122 Northeastern Naturalist Vol. 16, No. 1
reproductives; it may be difficult for these small ants to accumulate enough
resources to produce new males and females. Indeed, for a small proportion
of nests, it seemed that producing any brood during a season was difficult.
This interpretation is supported by our observation that VT nests had more
major producers and fewer nests that failed to produce any brood than NY
nests. The VT ant community is richer and denser than the NY community
(Herbers 1989), and this robustness may be a function of increased resource
availability at this location.
Given that life-history allocation decisions for social insects are
often affected by location (Backus 1995, Herbers 1990), we were surprised
to find no effect of site on either proportional allocation to males
or allocation to reproduction. One reason for this result may be lack of
statistical power. Studies of sex allocation and reproductive allocation
in social insects require large sample sizes (Crozier and Pamilo 1996)
and application of sophisticated multivariate techniques (Backus 1995).
Our relatively small number of nests in any given season allowed us to
ask only the simplest of questions from our data. Therefore a fuller understanding
of what determines life-history allocation decisions in this
species must await a much larger effort.
We provide strong evidence here, for the first time, that S. diecki colonies
exhibit seasonal polydomy. This process is characterized by colonies
that undergo fission in the summer to occupy multiple cavities and then
coalesce in the autumn to overwinter. There are three lines of evidence
to support an inference of seasonal polydomy for this species. Firstly, the
non-random, patchy distribution of nests is characteristic for species that
exhibit seasonal polydomy as satellite nests tend to be located close to the
main nest. Secondly, the large number of queenless nests found in VT and
NY are consistent with polydomy, with monogynous colonies including
many satellite nests with workers and brood but no queen. Finally, the demographic
patterns shown in Figure 4 clearly show that nests are bigger in
the spring (after overwintering underground) and again in the autumn (prior
to returning underground to overwinter) than in the summer. An alternative
explanation for the demographic shifts from summer to autumn involves
eclosion of new workers and adoption of newly mated queens by orphaned
nests in the autumn. The only alternative explanation, however, for the
change in demography from spring to summer is extremely high (and unlikely)
worker mortality. In addition, preliminary microsatellite data (V.L.
Backus and J.M. Herbers, unpubl. data) are consistent with those expected if
nests undergo late spring fission followed by autumn fusion and lend support
to a hypothesis that S. diecki undergoes seasonal polydomy. Thus, we are
confident that S. diecki, like so many other species in its guild, has colonies
that display an annual cycle of subdivision and recoalition.
Polydomy is a common phenomenon in cavity-dwelling ants and differences
in levels of polydomy between populations in a species are
accompanied by broad-scale differences in social organization (Banschbach
2009 V.L. Backus and J.M. Herbers 123
and Herbers 1996a, b). Changes in a population’s pattern of polydomy can
be accompanied by dramatic changes in social organization including sexual
allocation strategies (Backus et al. 2006). Thus, long-term studies on polydomy
in this species may be fruitful.
The cavity-dwelling ants of the north temperate forest are a remarkable
group of ants. Long-term studies of multiple populations reveal interesting
patterns for practically all life-history traits examined. Our data show that
S. diecki fits firmly within this guild, and therefore it is likely that additional
long-term studies of this species will prove useful for additional insights into
forest ant ecology.
Acknowledgments
Funding for this research has been provided to J.M. Herbers from the National
Science Foundation and to V.L. Backus from the Edmund Niles Hyuck Preserve and
Middlebury College.
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