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Why Get Along? Dietary and Molecular Influences on Cooperation in an Ant-Plant Symbiosis
by
Kyle Matthew Turner
A thesis submitted in conformity with the requirements for the degree of Masters of Science
Graduate Department of Ecology and Evolutionary Biology University of Toronto
© Copyright Kyle Matthew Turner, 2013
ii
Why Get Along? Dietary and Molecular Influences on
Cooperation in an Ant-Plant Symbiosis Kyle Matthew Turner
Masters of Science
Graduate Department of Ecology and Evolutionary Biology
University of Toronto
2013
ABSTRACT
In mutualisms, individuals exchange goods and services for net benefit. However, many
sources of variation in these interactions remain unexplored. To examine why plant-
dwelling ants protect their host plants by killing herbivores, I shifted the macronutrient
balance of their background diets. Providing ants with supplemental protein caused them
to invest less in patrolling and defence activities, likely because the availability of low-
cost protein made hunting for herbivores relatively less profitable. In contrast,
supplemental sugar caused an increase in ant activity, possibly because carbohydrates
serve as ‘fuel’ for patrolling. To examine a second source of variation in this interaction,
I treated ants with an activator of PKG, a protein encoded by foraging, a gene with
behavioural functions in other taxa. PKG activation caused ants to become more
aggressive towards herbivores, causing their host plants to experience less herbivory.
This suggests that an ortholog of foraging may influence cooperation in this system.
iii
ACKNOWLEDGEMENTS
This is a thesis about cooperation, and it could not have been produced without the help
of many others. First, I want to thank Megan Frederickson, my supervisor and mentor.
Megan is a truly great mind, and has consistently supported me, pushed me, and
encouraged me to take risks I never would have taken alone. I also want to acknowledge
the contributions of John Stinchcombe, James Thomson, and Marla Sokolowski, who
served on my supervisory committee; they were sometimes tough and intimidating, but
always fair and insightful. Thank you also to Marc Johnson and Helen Rodd for agreeing
to sit on my exam committee. And thank you to Ben Gilbert for always giving in to my
pestering for advice on statistics.
There are many people who directly helped me out with my experiments, and I want to
extend my deepest thanks to them. Thank you to Antonio Coral for invaluable help in the
field – I don’t think I would have found half my plants without his keen eye. I want to
give the most sincere thanks to the undergraduate students who helped me out: to Jackie
Awad, Shannon Meadley Dunphy, Margaret Thompson, and Kriti Saxena, thank you for
helping me and thank you even more for putting up with me. Thanks also to Stephanie
Fox, Erik Dean, and Gnanushan Krishna – though the work that they helped with did not
make it into this thesis, their help greatly enriched my graduate experience.
The Department of Ecology and Evolutionary Biology is intellectually strong, and I want
to thank the faculty for fostering that environment. I would also like to thank the
iv
administrative, maintenance, and janitorial staff – I fear that their contribution to our
work often goes unrecognized.
I also have to give my deepest thanks to the members of my lab and the other students in
the department. You have served as assistants, sounding boards, debate partners, and
above all, friends. Thank you to Kirsten Prior, Lina Arcila Hernández, Adam
Cembrowski, Rebecca Batstone, Eric Youngerman, and Jackie Day for making my time
in the Frederickson Lab wonderful. Thank you also to Jane Ogilvie, Ali Parker, Eddie
Ho, Emily Austen, Susana Wadgymar, Sandy Watts, Alex De Serrano, Jordan Pleet,
Natalie Jones, Kelly Carscadden, and Rachel Germain for the innumerable ways that you
have supported and helped me. And I am very grateful to the Pierce Lab at Harvard for
taking me in and becoming my fast friends.
And thank you finally to my family. I would not be where I am now had my parents not
provided me with a warm, supportive environment, and always encouraged curiosity and
exploration. Their support has never wavered, and their gestures of help made all the
difference in the tougher times of these projects. To everyone, I will forever appreciate
your help… and your cooperation.
v
TABLE OF CONTENTS
ABSTRACT ...................................................................................................................... ii
ACKNOWLEDGEMENTS ............................................................................................ iii
LIST OF FIGURES........................................................................................................ vii
LIST OF APPENDICES ..................................................................................................ix
GENERAL INTRODUCTION ........................................................................................1
CHAPTER ONE - Satiation and Cooperation: Diet Affects Protective Behaviour in
a Plant-Dwelling Ant .........................................................................................................6
Abstract............................................................................................................................6
Introduction .....................................................................................................................6
Methods .........................................................................................................................10
Study System .............................................................................................................10
Experiment.................................................................................................................11
i) Ant Activity........................................................................................................11
ii) Ant Aggression .................................................................................................12
Statistical Analysis ....................................................................................................13
Results ...........................................................................................................................15
i) Ant activity.........................................................................................................15
ii) Ant Aggression .................................................................................................17
Discussion......................................................................................................................18
References .....................................................................................................................23
vi
Figures ...........................................................................................................................30
CHAPTER TWO - Activation of Protein Kinase G (PKG) makes plant-protecting
ants better mutualist........................................................................................................37
Abstract..........................................................................................................................37
Introduction ...................................................................................................................37
Methods .........................................................................................................................41
Study System .............................................................................................................41
Experiment.................................................................................................................42
Ant Aggression Assays..............................................................................................42
Herbivory and Plant Traits ........................................................................................43
Statistical Analysis ....................................................................................................44
Results ...........................................................................................................................45
Discussion......................................................................................................................46
References .....................................................................................................................51
Figures ...........................................................................................................................61
CONCLUDING REMARKS ..........................................................................................67
WORKS CITED ..............................................................................................................71
APPENDIX ......................................................................................................................87
vii
LIST OF FIGURES
Figure 1.1. Mean (± SE) number of workers on (a) old leaves and (b) young leaves in
the four diet treatments…………………………………………………..……....30
Figure 1.2. Mean (± SE) numbers of workers found in the domatium attached to the
young leaves..……………………………...…………………………………….32
Figure 1.3. Mean (± SE) aggression score (average attacks on grasshoppers across each
minute for five minutes) measured four weeks after treatment..…..………….....33
Figure 1.4. Area of damaged tissue on the focal set of young leaves vs aggression score
(average attacks on grasshoppers across each minute for five minutes), with least-
squares regression line..……………………………………………………….....34
Figure 1.5. Mean (± SE) area of damaged tissue on the focal set of young leaves in
plants in part ii, by treatment..…………………….……………………………..35
Supplementary Figure 1.1. Activity of workers on young leaves at final vs initial
counts, in the sugar, mixed, control, and protein treatments……………...……..36
Figure 2.1. Schematic of the experimental set-up on a C. nodosa branch..…….…….....59
Figure 2.2. Mean (± SE) number of attacks on grasshoppers per minute in the control
and PKG activator treatments.……………………….………………………......60
Figure 2.3. Aggression score (attacks on grasshoppers averaged over five minutes)
before and after treatment, in control (a) and PKG activator-treated (b) colonies,
with least-squares regression lines. ……………………………………………..61
viii
Figure 2.4. Mean (± SE) area of herbivore damage in the control and PKG activator
treatments. …………………………………………………………………….....63
Supplementary Figure 2.1. Damaged leaf area vs leaf size (the width of the largest leaf
in the whorl) in the control and activator treatments. …………………………...64
ix
LIST OF APPENDICES
APPENDIX A – Pilot study: The effect of PKG on cooperation may vary across
systems…………………………………………………………………………84
1
GENERAL INTRODUCTION
Cooperative interactions can facilitate radical shifts in a species’ ecology, opening new
dietary niches, creating enemy-free space, and allowing colonization of new habitats
(Redecker et al. 2000, Janson 2008, Corradi & Bonfante 2012). In these mutualistic
interactions, species provide partners with goods or services, and in exchange acquire
resources that would be impossible or too costly to produce alone (Bronstein 1994a,
Bronstein et al. 2006). By definition, both partners obtain a net benefit. These
interactions can lead to coevolution, as interacting species evolve traits to attract and
retain partners, and to maximize the net gain from their interactions. This process can
drive diversification and the evolution of specialized morphologies and behaviours
(Powell 1992, Weiblen & Bush 2002, Ramírez et al 2011). As with other forms of
evolution, however, coevolution in cooperative interactions requires variation for
selection to act upon (Thompson 1988).
The outcomes of mutualistic interactions do frequently vary over space and time (e.g.
Thompson & Cunningham 2002, Rudgers & Strauss 2004). The net benefit of mutualism
can, for instance, depend on age or size class, partner density, or the abundance of third
parties like competitors or predators (Thompson 1988, Bronstein 1994b, Frederickson et
al. 2012a). Outcomes can also fluctuate with variability in the resources required for
cooperative phenotypes (e.g. Folgarait & Davidson 1995, Pringle et al. 2011), or with the
availability of alternative sources of the resource gained from the interaction (Kiers et al.
2006, Ness et al. 2009, Kiers et al. 2011). Genetic variation in cooperative phenotypes
2
can also have a substantial impact on the outcome of cooperation, for both partners
(Brock et al. 2011, Friesen 2011, Vantaux et al. 2011, Soares et al. 2012). But though all
these sources of variation will affect the fitness of interacting partners, they will not have
equivalent effects on coevolution. For cooperative traits to evolve, there must be a
genetic component to phenotypic variation (Thompson 1988). Strong environmental
variation in the outcomes of mutualism, in contrast, could slow coevolution, as strong
selection is only experienced in some contexts (Bronstein 1994b).
Many authors writing on mutualism are particularly concerned with how mutualisms
remain stable in the face of the apparent threat of cheating, that is, the potential for a
partner to reap the benefits of the interaction without paying the cost (e.g. Ferriere et al.
2002, Kiers et al. 2006, Heath & Tiffin 2009, Jandér & Herre 2011, Oono et al. 2011).
There are several potential mechanisms that stabilize mutualism by selecting for
cooperation (Sachs et al. 2004, Weyl et al. 2010, Archetti et al. 2011), including
preferential association with high-quality partners (‘partner choice’), derived traits
reducing the fitness of low-quality partners (‘host sanctions’), and links between the
fitness of both partners (‘partner fidelity feedback’). Though there is disagreement about
the relative importance of these alternative mechanisms, all require that variation in
partner quality have a genetic basis.
In this thesis, I explored some of the potential sources of variation in myrmecophytism, a
specialized ant-plant defensive interaction. In this interaction, plants produce hollow
structures (‘domatia’) in stems, thorns, or leaf pouches as nesting sites for ants (Heil &
3
McKey 2003). Ant colonies that live on these plants also derive food from their host
plants, either directly through food bodies (Janzen 1966, Folgarait & Davidson 1995,
Solano et al. 2005), or indirectly through scale insects, which feed on plants and secrete
honeydew for ants (Fonseca 1993, Pringle et al. 2011, Frederickson et al. 2012a). More
than 100 plant genera contain examples of myrmecophytism (Heil & McKey 2003), and
myrmecophytic plants are a conspicuous part of many tropical communities.
My work primarily focused on the interaction between the treelet Cordia nodosa
(Boraginaceae) and its ant partner, Allomerus octoarticulatus (Formicidae: Myrmicinae).
While both species associate with multiple partners (Yu & Pierce 1998, Frederickson
2009), A. octoarticulatus is the most common defender of C. nodosa at my field site in
southeastern Peru. A single, monogynous colony inhabits one C. nodosa tree, raising
brood (eggs, larvae, and pupae) and tending scale insects (Hemiptera: Sternorrhyncha:
Coccoidea) within the domatia (Frederickson et al. 2012a). The protective activities of
these ants reduce folivory (Yu & Pierce 1998, Frederickson 2005, Frederickson et al.
2012a) and promote plant growth (Frederickson & Gordon 2009, Frederickson et al.
2012a). Ants benefit from their protective behaviour because plant growth increases
available nesting space, reducing colony mortality and increasing reproduction (Yu &
Pierce 1998, Frederickson 2006, Frederickson & Gordon 2009, Frederickson et al.
2012a). The net benefit for plants, however, is dependent on the presence of herbivores:
when they are excluded, plants incur a net cost of hosting ants (Frederickson et al.
2012a).
4
In my first chapter, I explore whether this interaction might also be sensitive to variation
in the availability of resources in the environment. Foraging A. octoarticulatus workers
completely restrict their activity to the plant surfaces (Yu & Pierce 1998, Frederickson &
Gordon 2009), obtaining food from cellular food bodies produced on the young tissues of
C. nodosa (Solano et al. 2005), honeydew excreted by scale insects, and the invertebrates
that land on their host plant (Yu & Pierce 1998, Frederickson et al. 2012a). Herbivores
appear to be an important source of food for the ants, as they construct elaborate carton
galleries on stems to trap their prey (Dejean et al. 2005, Ruiz-González et al. 2011).
Since ants’ protective behaviour is based in food acquisition, it may be affected by
optimal foraging (Charnov 1976). Particularly, ants have been found to reject food items
when they are less profitable than the expected gain rate from alternative sources in the
environment (Kay 2002); the availability of alternative protein sources may therefore
reduce ants’ investment in hunting and killing insect herbivores. Conversely, additional
carbohydrate sources might increase defensive behaviour, either by acting as fuel for
high-tempo activity (Davidson 1997, Grover et al. 2007, Pringle et al. 2011, González-
Teuber et al. 2012), or, as a macronutrient complementary to nitrogen, increasing ant
‘hunger’ for protein (Dussutour & Simpson 2009, Cook & Behmer 2010, Cook et al.
2012). Chapter One describes field studies exploring these possibilities.
In Chapter Two, I explore a second source of variation in ant defence: behavioural
genetics. Recent study has revealed genes linked to learning, mating, dominance, and a
number of other ecologically-relevant behaviours (Fitzpatrick & Sokolowski, Fitzpatrick
et al. 2005). One of these genes, foraging, has been linked to food-seeking behaviours
5
and activity levels across taxa (Osborne et al. 1997, Ben-Shahar et al. 2002, Tobback et
al. 2008), including in ants (Lucas & Sokolowski 2009, Ingram et al. 2011). Since plant
protection in A. octoarticulatus represents both foraging and nest defence, I predicted
that the activity of PKG, the enzyme encoded by foraging, would influence the level of
protection ants provide. Chapter Two describes a field study in which I
pharmacologically activated PKG to test this prediction. As the effects of foraging
orthologs are known to vary across systems, I also tested for an influence of PKG in
another system, the interaction between Acacia drepanolobium and two of its partner ant
species, Crematogaster nigriceps and Crematogaster mimosae. Though this work was
hindered by high ant mortality in the greenhouse population studied, the results,
described in Appendix A, have implications for our understanding of the genetic basis of
cooperation.
The relationship between ants and myrmecophytic plants is a highly specialized
interaction. Understanding how the ants’ cooperative behaviour might be sensitive to diet
and the activity of PKG helps us understand why they continue to cooperate, and how
plants might maximize their benefit from the interaction. But many cooperative
interactions involve the exchange of food, and all mutualisms involving animals will be
influenced by behaviour. Learning more about how cooperation is influenced by diet and
genetics thus extends our understanding of how a diverse array of mutualistic interactions
might function and coevolve.
6
CHAPTER ONE
Satiation and cooperation: diet affects protective behaviour in a plant-dwelling ant
Abstract
In mutualisms, organisms get goods or services by cooperating with a partner. However,
the value of these rewards can vary with the availability of alternative sources. Here, we
use the cooperative interaction between Allomerus octoarticulatus ants and the Cordia
nodosa trees they inhabit and protect to test whether changing the food available to the
animal partner might change its level of cooperation. When we supplemented the diets of
A. octoarticulatus colonies with protein, ants patrolled less, recruited to wounds less
readily, and became less aggressive towards herbivores placed on the plant. Thus, with
alternative, less-costly sources of protein, colonies invested less in hunting herbivores
and protecting their hosts. Under sugar supplementation, in contrast, a subset of colonies
increased the intensity of patrolling activity on young tissues of the plants. This supports
the hypothesis that excess carbohydrates fuel high-tempo activity in ants. Though ants
benefit indirectly from protective behaviour through the growth of their host plants, the
direct role of food rewards is also important for understanding cooperation in this system.
Introduction
Mutualisms are phylogenetically and functionally diverse, but are unified by an exchange
of goods and services benefiting both partners (Bronstein 1994, Bronstein et al. 2006).
Nearly universally, food is used as a reward for animal partners in plant-animal
7
mutualisms. Animals receive food in exchange for dispersal of plant gametes
(pollination, Bronstein et al. 2006) or offspring (frugivory, Herrera 1984; ant seed-
dispersal, Gammans et al. 2005), parasite removal (cleaner fish, Soares et al. 2012), or
other protection against natural enemies (hemipteran-tending by ants, Way 1963). In
many cases, the partner itself is eaten (e.g. leafcutter ant-fungal interactions, Quinlan &
Cherrett 1978). However, food in mutualism can serve a more complicated role than
simply as currency.
One interaction involving food exchange is myrmecophytism. Found in more than 100
plant genera (Heil & McKey 2003), myrmecophytic plants produce hollow or hollowable
structures (‘domatia’) for ants. ‘Plant-ants’ nest in the domatia and protect their host
plants from herbivores, pathogens, or competitors (Trager et al. 2010). Many plant
species produce food bodies or extrafloral nectar for ants (e.g., Müllerian and pearl
bodies in Cecropia spp., Folgarait & Davidson 1995; Beltian bodies and EFN in Central
American Acacia spp., Janzen 1966; food bodies in Cordia nodosa, Solano et al. 2005).
After water, lipids often form the major component of these food bodies, followed by
protein and soluble carbohydrates like sugars (Heil et al. 1998, Fischer et al. 2002, Heil
et al. 2004). Ants may also acquire plant-derived food via the honeydew-producing scale
insects they often tend (Fonseca 1993, Pringle et al. 2011). In plants that are facultatively
visited by ants, nectar composition is known to affect the attraction of partners (Heil
2011), but the optimal composition of food rewards in myrmecophytes is less clear.
8
Food plays a dual role in this interaction. First, as many plant-ant species restrict their
foraging to the plant, plant-derived food sustains the colony. More food may increase
colony size, possibly providing the plant with a larger defensive force to reduce
herbivory (Heil et al. 2001, Pringle et al. 2011). But food could more directly affect
defensive behaviour. Excess carbohydrates, for instance, might fuel active, ‘high tempo’
foraging and patrolling activity (Davidson 1997). Moderately high levels of sucrose were
associated with high activity and aggression in an ecologically dominant ground-nesting
ant (Grover et al. 2007), and a high-sucrose diet increased anti-herbivore aggression in
lab colonies of the plant-ant Azteca pittieri (Pringle et al. 2011). Thus, plant-derived food
sustains ants, but its composition may also specifically influence ants’ ability to sustain
high-energy defensive behaviours.
Food may have a particularly strong impact in systems where defending ants are
predatory. Some plant-ants just repel threatening herbivores (e.g. Madden & Young
1992, Fonseca 1993) or remove them from plant surfaces (e.g. Letourneau 1983), but
many kill and eat them (e.g. Dejean et al. 2005, 2010). Thus, background diet may
additionally affect ants’ defensive behaviour by changing the relative value of herbivores
as a food source. As outlined by Kay (2002), ants can make foraging decisions based on
optimal foraging, foraging on food sources until their marginal gain drops below the
expected gain from other sources in the environment. The ants’ decisions to attack prey
items should therefore be dependent on the availability of more profitable alternative
sources of the nutrients commonly present in insect prey (Charnov et al. 1976).
9
Alternative sources of protein may thus affect ants’ investment in hunting insect prey, but
this may also be affected by carbohydrate availability. Because of behavioural and
physiological demands, ant species have characteristic carbon:nitrogen ‘target ratios’ in
their diets (Davidson 2005, Ness et al. 2009). Prolonged exposure to diets with
suboptimal ratios can be physiologically costly (Grover et al. 2007, Dussutour &
Simpson 2009, Cook et al. 2009), so ants have evolved strategies to deal with unbalanced
food, including hoarding (Cook et al. 2009), selective extraction (Dussutour & Simpson
2009), and preferential collection of foods with ratios that counter standing imbalances
(Kay 2004, Cook & Behmer 2010, Cook et al. 2012). Davidson (2005) suggested that the
latter mechanism explained ant defence of plants, hypothesizing that nitrogen-deprived
ants were more likely to aggressively attack protein-rich herbivores. Ness et al. (2009)
demonstrated such an effect in the myrmecophilous cactus Ferocactus wislizeni, which is
facultatively visited by ants: supplementation with sugary syrup increased ant
aggressiveness and preference for proteinaceous baits, while supplementation with meat
had the opposite effect. Ferocactus wislizeni’s nectar is too carbohydrate-biased to meet
ants’ nutritional needs, and Ness et al. (2009) argued that compensating for this
imbalance drives ants to aggressively hunt herbivores.
In Ness et al.’s (2009) study, ants only facultatively visited the cacti, and received
primarily direct food benefits from killing herbivores. However, in obligate ant-plant
interactions, ants additionally receive indirect benefits from anti-herbivore defence.
Protection promotes plant growth (e.g. Frederickson & Gordon 2009, Frederickson et al.
2012a), which increases nesting space and thus ant colony size (Fonseca et al. 1993,
10
Pringle et al. 2011, Handa et al. 2013), and, in turn, ant reproduction (Yu & Pierce 1998,
Frederickson & Gordon 2009). Because of these indirect benefits, obligate plant-ants
may have evolved defensive behaviours that are less sensitive to environmental variation.
In this study, we use the interaction between the tropical plant Cordia nodosa and its
symbiotic Allomerus octoarticulatus ants to explore how food affects plant defence in an
obligate ant-plant interaction.
Methods
Study System
Studies were conducted at the Los Amigos Research Centre (12°34’S, 70°05’W;
elevation ~270 m), in the Peruvian Amazon. The myrmecophyte Cordia nodosa Lam.
(Boraginaceae) is common at the field site. Each node on C. nodosa is directly associated
with a whorl of four leaves, as well as two additional leaves on the internode below.
Almost all of these nodes are swollen into hollow domatia, which serve as nesting sites
for plant-ants. Plants also produce cellular food bodies on all young tissues (Solano et al.
2005), though the nutritional contents of these food bodies is unknown. At our study site,
C. nodosa is most often inhabited by Allomerus octoarticulatus Wheeler (Formicidae:
Myrmicinae). Single monogynous colonies of this ant aggressively defend host plants,
reducing herbivory and promoting plant growth (Frederickson 2005, Frederickson &
Gordon 2009, Frederickson et al. 2012a). Allomerus octoarticulatus workers kill and eat
herbivores (Yu & Pierce 1998), constructing complex galleries on stems in order to trap
and capture prey (Dejean et al. 2005, Ruiz-González et al. 2011).
11
Experiments
i) Ant Activity
In late June and early July 2011, we selected 40 individual C. nodosa with at least one
incompletely expanded whorl of young leaves, as both herbivory and ant defence are
concentrated on young leaves (Edwards et al. 2006). If the young leaves were originally
too high off the ground, we used cord to secure the branch in a position low enough to
observe.
To measure ant activity, we counted the total number of ants on the upper and lower
surfaces of the whorl of young leaves, as well as a comparable set of fully-expanded old
leaves at least two internodes away. To test how ants would respond to herbivory cues,
we randomly selected one of the three largest young leaves and used clean forceps to
make a 1 cm incision, 1 cm from the midvein and halfway down the length of the leaf.
Then, we counted the number of ants that recruited to the wound over five minutes.
We measured eight plants per day and randomly assigned two plants each to one of four
treatments: control, sugar, protein, and mixed. After counts, we affixed a 1.5 mL micro-
centrifuge tube to each plant, one node below the young domatium. This tube contained 1
mL of a treatment solution. In the “sugar” treatment, this tube contained a 0.15 g/mL
sucrose solution in distilled water. In the “protein” treatment, the tube contained a 0.17
g/mL solution of whey protein powder, equivalent to 0.15 g/mL of protein. The “mixed”
treatment solution contained 0.075 g/mL of sucrose and 0.085 g/mL of whey protein, and
12
the control tubes contained only distilled water. Solutions were replaced weekly, and we
saw ants feeding on all the treatment solutions.
The experiment ended after four weeks. We repeated ant counts and wounding trials,
making a fresh incision on the same leaf. At this time, we also counted the number of
domatia on each plant, and measured the stem diameter at ground level, to see whether
plant size (as a proxy for colony size) might also affect ant behaviour. For 24 plants (6
per treatment), we counted the number of larvae, pupae, and workers in the domatium
attached to the young leaves.
ii) Ant Aggression
To test whether diet would directly affect attacks on herbivores, we conducted a similar
experiment in July 2011, using 36 plants from the same population, again each with
young leaves. Before the experiment, we measured the plants’ stem diameter at ground
level and height, and counted domatia. If necessary, we used cord to secure the branch
bearing young leaves in a lower position at least 24 hours before observations.
We tested the response of ants to herbivores. We tethered a eumastacid grasshopper to a
pin pushed through the largest of the four leaves attached to the domatium below the
whorl of expanding, young leaves. These grasshoppers, which are frequently found on C.
nodosa plants and consume their leaves, were collected the day before trials. In our trials,
the grasshoppers rarely attempted to feed, but moved about on the leaf until attacked by
ants. Each minute for ten minutes following placement, we counted the number of ants
13
that were attacking (biting, stinging, or climbing on) the grasshopper. As attacks
generally plateaued after five minutes, we averaged the final five counts to generate an
aggression score.
We measured six plants per day, and assigned two to each of three treatments: sugar,
protein, and control. As in the previous study, 1 mL of treatment solution (0.20 g/mL
sucrose, 0.20 g/mL whey protein, or distilled water) was provided in a 1.5 mL micro-
centrifuge tube attached on the stem below the leaves on which grasshoppers were tested.
We replaced the food tubes weekly, and ran the experiment over the course of a month.
We conducted grasshopper trials before the experiment, and after two and four weeks.
We also photographed leaves before treatment and again after four weeks. We used
ImageJ (v. 1.43u, 2012 National Institutes of Health) to analyze the leaf photographs, and
measured accumulated herbivory as the difference in damage between the before and
after measures.
Statistical Analysis
In i), we analyzed the final counts of ants on young leaves, on old leaves, and recruiting
to wounds in models including treatment and the corresponding initial ant count as a
covariate, to control for natural variation in ant activity. For ant activity on old leaves and
recruitment to wounds, the treatment by covariate interactions were non-significant and
thus excluded (Engqvist 2005). For ant activity on young leaves, this interaction was
significant, and thus the data did not meet the ANCOVA assumption of homogeneity of
14
regression slopes. When this assumption is violated, the main treatment effect depends
on the covariate value. Following Hendrix et al. (1982), we repeated the analysis, re-
centering the covariate to find the region in which treatment groups significantly
differed. Plant size measures (number of domatia and stem diameter) and date of
measurement were also tested for inclusion in the models but did not improve model fit.
We tested for treatment effects on counts of larvae, pupae, and workers in domatia in
similar models. Since initial counts would have required us to open (and destroy)
domatia, the initial number of active workers on the young leaves was instead included in
the model as a covariate. We also regressed final ant activity on young leaves against the
number of workers in domatia to see if this might explain treatment effects.
In ii), aggression scores were similarly analyzed in models including treatment and initial
aggression as a covariate, with the non-significant covariate by treatment interaction
excluded. Plant height was also included after a separate study (see Chapter 2) suggested
a strong influence on ant aggression, likely because plant size and colony size are
correlated (Frederickson & Gordon 2009, Frederickson et al. 2012a).
All of these data were highly over-dispersed, and so were modeled using generalized
linear models with a negative binomial error distribution, in R v 2.15.2. In each case, we
used the Vuong test (Vuong 1989) to confirm that the negative binomial distribution
improved fit over a comparable Poisson model. This test also indicated an excess of
zeroes in the data from ii), and so a zero-inflated negative binomial model was used.
15
Effects of model terms were tested using Wald X2 tests. Multiple comparisons were
conducted using Tukey-corrected Wald Z-tests.
We measured herbivory as the difference in damaged area between initial and final
photographs. Three plants (two in the carbohydrate treatment, one in the control) were
excluded as entire leaves were lost, which can be caused by relatively small areas of
damage (e.g. on the basal portion of the midvein). Area of herbivore damage was log-
transformed to improve normality and was tested for treatment effects using GLMs with
a Gaussian error distribution. Additionally, we tested for an association between ant
aggression and herbivory using least-squares regression, as well as quantile regression, a
technique that tests for how predictor variables affect the median and other quantiles of a
response, rather than the mean (Cade & Noon 2003).
Results
i) Ant activity
Protein treatment lowered final ant activity on old leaves. Diet treatment had a significant
effect on the number of ants patrolling the surfaces of old leaves (X2=14.12, df=3,
p=0.0027, Fig. 1.1a). Final patroller counts were also higher in plants that had had high
initial counts (X2=25.51, df=1, p<0.0001), but plants in the protein treatment had lower
final counts than in the control (multiple comparison: Wald Z=-3.06, Tukey p=0.012) or
sugar treatments (Wald Z=-3.54, Tukey p=0.0023). Eight of ten plants treated with
protein had no active patrollers on older leaves at the end of the experiment.
16
Diet treatment also affected final ant activity on most young leaves (Fig. 1.1b). On young
leaves, initial ant densities strongly influenced final measures (X2=6.14, df=1, p=0.013).
On the average leaf, treatment had a significant effect on patroller activity (X2=11.36,
df=3, p=0.0099), but the significant interaction between treatment and the initial activity
covariate (X2=15.72, df=3, p=0.0013) meant that the effect of treatment depended on the
value of this covariate. Re-analyzing the data centered at several covariate values showed
that treatment significantly (p<0.05) affected final ant counts on plants that had initial
counts up to 38 ants, which included 65% of plants (supplementary Fig. 1.1). In this
range, the sugar and mixed treatments had higher final ant counts than the control and
protein treatments, with significant contrasts (Tukey p<0.05) from the minimum to
median covariate values. Thus the presence of sugar led to higher ant activity on most
plants.
Protein supplementation resulted in fewer workers recruiting to wounds. Colonies that
recruited more initially also recruited more after treatment (X2=20.95, df=1, p<0.0001),
and recruitment was also affected by treatment (X2=20.10, df=3, p=0.0002). None of the
ten colonies in the nitrogen treatment showed any recruitment to the wound at the end of
the experiment, whereas workers did recruit on some plants in each of the other
treatments (mean workers ± SE: control, 3.1 ± 2.5; sugar, 1.9 ± 1.6; mixed, 3.0 ± 2.1;
protein, 0 ± 0).
Diet treatment also affected the number of workers inside the domatium attached to the
young leaves. After controlling for initial variation between ant colonies, worker counts
17
within domatia were affected by treatment (X2=8.01, df=3, p=0.046; Fig. 1.2).
Specifically, domatia in the protein treatment had fewer workers than those in the sugar
treatment (Wald Z=-3.06, Tukey p=0.021). The treatment effects on the activity of
workers on leaves (Fig. 1.1b) were not explained by these differences in workers in the
domatia, as the regression of activity against domatium worker counts was not significant
(X2=1.86, df=1, p=0.17). Treatment did not affect the number of larvae (X2=0.52, df=3,
p=0.91) or pupae (X2=0.82, df=3, p=0.84) in the domatium.
ii) Ant Aggression
In ii), protein also reduced ants’ attacks towards herbivores. Treatment significantly
affected the attack score after a month (X2=8.56, df=2, p=0.014; Fig. 1.3), and ants
attacked grasshoppers less in the protein than control treatment (Wald Z=-2.92, Tukey
p=0.0092). Plant height (X2=2.63, df=1, p=0.11) did not predict final aggression to
herbivores, though ants that were more aggressive initially were also more aggressive in
final measures (X2=4.15, df=1, p=0.042). After only two weeks of treatment, initial
aggression significantly predicted aggression score (X2=6.90, df=1, p=0.0086), and
neither treatment (X2=2.22, df=2, p=0.33) nor plant height (X2=0.62, df=1, p=0.43) had
an effect.
Leaves with more aggressive ants tended to suffer less damage (X2=3.71, df=1, p=0.054;
Fig. 1.4), though the effect of treatment was not significant (X2=0.57, df=2, p=0.75; Fig.
1.5). Quantile regression showed that while the least-damaged plants had no or low
damage regardless of ant aggression levels (5th percentile of damage: t=0.00, p=1; 10th
18
percentile: t=0.00, p=1; 25th percentile: t=-0.20, p=0.84), the maximum level of damage
suffered was much higher when plants had less aggressive ants (90th percentile: t=-4.39,
p=0.00012; 95th percentile: t=-3.88, p=0.00051). Thus, plants with less aggressive ants
had greater variation in damage.
Discussion
Allomerus octoarticulatus ants invest less in hunting herbivores and defending their host
plants when provided with alternative sources of protein. On both young and old leaves,
ants were less active in the protein treatment. Additionally, protein supplementation
completely eliminated recruitment to wounds and reduced ants’ attacks towards
grasshoppers. Allomerus octoarticulatus ants receive indirect benefits from protection of
their host trees: ants promote host growth, which benefits the ants through larger colony
sizes, reduced colony mortality, and increased reproduction (Yu & Pierce 1998,
Frederickson 2006, Frederickson & Gordon 2009, Frederickson et al. 2012a). But here,
we have shown that in large part, ants cooperate to accrue the direct benefits of food
acquisition. Though the net benefit of hunting insect herbivores is likely positive
(Frederickson et al. 2012a), constructing carton traps and subduing large prey are also
likely quite costly (Ruiz-González et al. 2011). Thus, when ants could obtain protein
from an alternative source without incurring these costs, they reduced investment in
hunting less-profitable insect prey, consistent with predictions of optimal foraging
(Charnov 1976, Kay 2002).
19
Sugar supplementation typically increased ant activity on young leaves. Ants recognize
carbohydrates and protein as distinct resources, and high abundance of one should not
increase rejection of the other (Kay 2002). Instead, supplemental sugar appeared to fuel
high activity, as some authors have proposed (Davidson 1997, Pringle et al. 2011).
However, colonies did not increase recruitment to wounds or attacks on herbivores, and
so our results do not provide strong support for the hypothesis that carbohydrates fuel
predation by increasing the need for protein (Ness et al. 2009). However, plants could
still benefit from increased ant activity alone, if they remove pathogens from plants
(Letourneau 1998) or if herbivores are deterred by ant pheromones (Offenberg et al.
2004).
Compared with protein, the effects of carbohydate supplementation on ant behaviour
seem more variable (Petry et al. 2012). While several studies have reported positive
effects of carbohydrate supplementation on worker activity and aggression (Grover et al.
2007, Gonzalez-Teuber et al. 2012; aggression but not activity, Pringle et al. 2011),
others have suggested that increased activity may sometimes simply reflect increased
colony size (Kay et al. 2010). Some studies have even shown negative effects of
carbohydrates on activity levels (Cook et al. 2009, Grover et al. 2007, at high
carbohydrate levels), with knock-on effects on mutualists (Petry et al. 2012). We found
that the effects of sugar depended on initial activity levels: while sucrose boosted ant
activity in colonies with low to average initial activity, it did not affect colonies with very
high initial activity. These unaffected colonies may have simply had dietary treatment
effects diluted by higher worker numbers. Thus, the effect of carbohydrate addition is
20
variable, but for the majority of colonies in our study, sugar supplementation led to
higher patroller activity.
Diet treatment may additionally have effects on colony demographics, as protein-treated
colonies had lower numbers of workers in their domatia compared with sugar-treated
colonies, after controlling for variation in initial densities. As we examined only the
single domatium associated with the young leaves and not the whole colony, it is
possible that protein supplementation causes ants to recruit in lower numbers to the
growing branch, as fewer workers are needed to collect the easily-accessible dissolved
protein. However, it is also possible that augmented protein caused higher worker
mortality, as increased mortality with excess dietary nitrogen has been reported in several
ant species (Dussutour & Simpson 2009, Cook et al. 2009, Kay et al. 2012). Mortality in
nitrogen-biased diets is likely associated with higher levels of the N-rich waste product
uric acid (Kay et al. 2012), as well as reduced worker lipid content (Cook et al. 2009).
Cook et al. (2009) argued that poor worker condition might have explained the reduced
foraging intensity they observed in their nitrogen-biased treatment. A similar effect may
have been at play in our study, as changes in worker numbers alone did not explain the
treatment’s effects on patroller activity.
In our study, colonies with more aggressive ants suffered lower herbivory. In the same
system, domatia containing more worker ants also had reduced herbivory on the
associated leaves (Frederickson et al. 2012b). Thus, by reducing aggression and the
density of workers in domatia, excess protein available to ants is likely harmful for
21
plants. Though we were unable to detect a direct effect of diet treatment on leaf damage,
these effects were likely swamped by high variability in herbivory over the short time
scale of this study. On a whole plant level, persistent changes in diet would almost
certainly have effects on herbivory, and in turn, plant growth and fitness (Yu & Pierce
1998, Frederickson et al. 2012b).
Because protein depressed ant protection, while sugar increased ant activity, our results
agree with the suggestion that plants would benefit from producing high-carbohydrate,
low-nitrogen food (Davidson 2005, Ness et al. 2009). This may explain why extrafloral
nectar available to ants tends to be highly carbohydrate-biased (Ness et al. 2009), and
why hemipterans, which siphon carbohydrate-rich plant sap to ants, are ‘permitted’ by
the vast majority of ant-plants (Pringle et al. 2011). In this light, it is interesting that the
food bodies produced by many myrmecophytic plants are reasonably high in protein (e.g.
Heil et al. 1998, Fischer et al. 2002, Heil et al. 2004). In many of these cases, however,
ants are highly or exclusively dependent on plant-produced food for nourishment. Thus
plants must more closely match the nutritional requirements of their ants in order to
sustain defending colonies. This may also explain why lipids are often common in food
bodies (e.g. Heil et al. 1998, Fischer et al. 2002), even though ants may also hunt insects
as a source of this macronutrient (Thompson 1973). To better understand how ant-plants
balance keeping ant colonies healthy and keeping them aggressive, future work should
focus on plants like Cordia nodosa, whose ants are not so completely reliant on food
bodies or nectar.
22
Though plant-ants like Allomerus octoarticulatus gain indirect fitness benefits by
protecting their host trees (Yu & Pierce 1998, Frederickson 2006, Frederickson &
Gordon 2009, Frederickson et al. 2012a), we have shown that food acquisition is a
significant proximate reason why ants protect host plants. When provided with a highly
profitable alternative source of protein, ants invested less in hunting prey, reducing their
activity, recruitment to wounds, and aggression towards herbivores. In contrast,
supplemental sugar appeared to fuel increased ant activity. Diet also affected the density
of workers in domatia, either by changing worker allocation within colonies, or by
affecting mortality. Thus, even in an obligate ant-plant system, cooperation can vary
depending on the availability of different resources.
Acknowledgements
We thank Antonio Coral, Shannon Meadley-Dunphy, and Jackie Awad for field
assistance; Jon Sanders, Lina Arcila Hernández, and Adam Cembrowski for assistance
with experimental design; the Amazon Conservation Association and the staff at Los
Amigos for support; and members of the Frederickson, Gilbert, Agrawal, and Thomson
Labs for comments on this manuscript. We thank MINAG-DGFFS for permits to do
research in Peru (RD No. 299-2011-AG-DGFFS-DGEFFS and RD No. 278-2012-AG-
DGFFS-DGEFFS). We thank funding from an NSERC Discovery Grant, a Connaught
New Researcher Award, and the University of Toronto to MEF, and from a Sigma Xi
Grant-in-Aid-of-Research to KMT.
23
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30
Figures
31
Figure 1.1. Number of workers on (a) old leaves and (b) young leaves in the four
treatments. Counts are presented as least-squares means (± SE) to correct for significant
effects of the covariate. In (a), groups sharing letters are not significantly different
according Tukey multiple comparisons. Multiple comparisons for (b) varied according to
the value of initial worker densities (see text).
32
Figure 1.2. Mean (± SE) numbers of workers found in the domatium attached to the
young leaves. Groups sharing letters are not significantly different according Tukey
multiple comparisons.
33
Figure 1.3. Mean (± SE) aggression score (average attacks on grasshoppers across each
minute for five minutes) measured four weeks after treatment. Groups sharing letters are
not significantly different according Tukey multiple comparisons.
34
Figure 1.4. Area of damaged tissue on the focal set of young leaves vs aggression score
(average attacks on grasshoppers across each minute for five minutes), with least-
squares regression line. Each point represents a plant.
35
Figure 1.5. Mean (± SE) area of damaged tissue on the focal set of young leaves in
plants in part ii, by treatment.
36
Supplementary Figure 1.1. Activity of workers on young leaves at final vs initial counts,
in the sugar (black circles), mixed (white circles), control (black triangles) and protein
(white triangles) treatments. Diet treatment had a significant effect on final worker
counts on plants with initial worker counts less than 38 (grey line). Each point represents
a plant.
37
CHAPTER TWO
Activation of protein kinase G (PKG) makes plant-protecting ants better mutualists
Abstract
Almost nothing is known about the molecular basis of cooperation in plant-animal
mutualisms. In the Peruvian Amazon, we used a pharmacological manipulation to
examine the interaction between a plant-dwelling ant species (Allomerus octoarticulatus)
and the host plants it protects against herbivores (Cordia nodosa). We tested for an effect
of protein kinase G (PKG), an enzyme encoded by the gene foraging, as this enzyme has
been linked to relevant behaviours in other taxa. When we added the PKG activator 8-Br-
cGMP to the ants’ diet, ants behaved more aggressively towards herbivores, resulting in
less herbivore damage to their host plants. Our finding strongly suggests that foraging
mediates this ant-plant interaction.
Introduction
Almost all organisms are involved in cooperative interactions within or between species
(Bronstein 1994, Wilson & Hölldobler 2005, Bronstein et al. 2006, Clutton-Brock 2009).
These interactions have driven major ecological and evolutionary transitions (Redecker
et al. 2000, Bronstein et al. 2006, Janson 2008, Ramírez et al 2011, Corradi & Bonfante
2012), but the molecular basis for cooperation in most systems is unknown. Within
species, recent work has identified the genetic elements behind higher levels of social
organization (e.g. Ross et al. 2003, Ott et al. 2011, Wang et al. 2013). In mutualisms
38
between species, the existence of inter-clone (Brock et al. 2011, Vantaux et al. 2011) and
inter-population (Rudgers & Gardener 2004) variation in cooperative phenotypes
suggests a genetic basis for these traits, but the actual molecular basis for mutualism
remains almost completely unknown, especially outside plant-microbe mutualisms.
Understanding molecular mechanisms lends insight into mutualism evolution. For
instance, in three clades of a tropical plant family, Zhang et al. (2012) demonstrated that
shifts in the community of pollinators led to convergent changes in floral signaling genes,
suggesting a common genetic predisposition towards certain signal changes. In legumes
and rhizobia, identifying nodule production genes and examining them for signatures of
selection has increased our understanding of the adaptive history of these mutualisms
(Oldroyd & Long 2003, Ané et al 2004, De Mita et al. 2007). Associating variation in
cooperation with allelic variation can also advance our understanding of mutualism
stability. If less cooperative partners are “cheaters” (or “defectors”), then they should
benefit from uncooperative behaviour, and less cooperative alleles should show signs of
recent positive selection. If less cooperative partners are simply “defective” (sensu
Friesen 2012), and not cooperating is maladaptive, then we should detect purifying
selection on the locus of interest, in response to partner feedbacks (or other proposed
mechanisms that maintain cooperation; Sachs et al. 2004, Weyl et al. 2010, Archetti et al.
2011). However, in most systems such analyses are impossible because we do not know
which genes affect mutualist quality.
39
In animals, cooperation depends largely on behaviour, making it possible to leverage our
growing understanding of behavioural genetics to study the molecular underpinnings of
animal cooperation (e.g. in social insects, Ben-Shahar et al. 2002, Lucas & Sokolowski
2009, Ingram et al. 2011). Recent work has identified a number of genes involved in
feeding, learning, mating, social interactions, and other behaviours (Fitzpatrick &
Sokolowski 2004, Fitzpatrick et al. 2005). Despite the ecological relevance of these
traits, the impacts of these genes on the wider environment (their “extended phenotypes”;
Dawkins 1982) have rarely been explored, though Weber et al. (2013) recently
demonstrated the extended phenotype of loci involved in deer mouse nest construction.
The potential to detect extended phenotypic effects is particularly high in intimate
interspecific interactions, such as symbioses. Hoover et al. (2011) showed that a viral
gene induces climbing behaviour in its host, thereby increasing transmission of the
parasite to new hosts. In plant-animal mutualisms, animal phenotypes extend to the
performance and fitness of their plant partners, and feedback through this process drives
coevolution. Yet the genes underlying extended phenotypes in plant-animal mutualisms
are completely unknown.
One taxonomically and ecologically abundant example of plant-animal cooperation is
myrmecophytism, a protective mutualism between ants and plants (Heil & McKey 2003,
Bronstein et al. 2006, Trager et al. 2010). Myrmecophytic plants produce hollow housing
structures and often food rewards for ants (Janzen 1966, Folgarait & Davidson 1995,
Solano et al. 2005). ‘Plant-ants’ living in these housing structures (‘domatia’) patrol plant
structures and often deter herbivores, pathogens, and encroaching plant competitors
40
(Trager et al. 2010). Ants collect plant-derived food and often kill and eat insect
herbivores, and therefore they forage, defend their nest, and protect host plants through
the same activities (e.g. Yu & Pierce 1998, Dejean et al. 2005, 2010). The gene foraging
influences movement and feeding in several taxa (Fitzpatrick & Sokolowski 2004), and
so we predicted that an ortholog of foraging might be involved in this interaction. This
gene encodes one form of cGMP-dependent protein kinase (PKG), and was originally
identified as influencing movement during feeding in Drosophila melanogaster (Osborne
et al. 1997). Allelic differences also affect response to sucrose (Belay et al. 2007) and
resilience to starvation in these flies (Donlea et al. 2012). Throughout social
Hymenoptera, foraging workers have shown different PKG activity or foraging gene
expression than nursing workers (Ben-Shahar et al. 2002, Ingram et al. 2005, Tobback et
al. 2008, Kodaira et al. 2009, Ingram et al. 2011, Tobback et al. 2011), and in the ant
Pheidole pallidula, PKG mediated a trade-off between foraging and nest-defence
behaviour (Lucas & Sokolowski 2009). Experimentally, providing organisms with 8-
bromoguanosine 3’,5’-cyclic monophosphate (8-Br-cGMP) increased PKG activity and
caused them to express the same behavioural phenotypes associated with high expression
of the gene (Ben-Shahar et al. 2002, Lucas & Sokolowski 2009). These manipulations,
however, occurred in a laboratory setting, and only measured the effects on the single
species of interest.
Here, we examined whether PKG might influence cooperation between the tropical ant
Allomerus octoarticulatus and its Cordia nodosa host trees, as ants’ foraging and nest
defence behaviour form the basis of plant protection. Working with colonies inhabiting
41
trees in the field, we fed the ants the PKG activator 8-Br-cGMP and measured the effects
of this treatment on ant aggression towards herbivores, and plant performance. Thus, we
asked: Does PKG influence workers’ attacks on herbivores? And do these effects extend
to affect the amount of herbivory plants experience?
Methods
Study System
We studied the ant-plant Cordia nodosa Lam. (Boraginaceae) and its most common ant
associate, Allomerus octoarticulatus Wheeler (Formicidae: Myrmicinae), at the Los
Amigos Research Center (12°34’S, 70°05’W; elevation ~270 m) in the Peruvian
Amazon. This site is mostly primary tropical rain forest, with a mix of floodplain and
terra firme habitats. A single A. octoarticulatus colony lives in one individual C. nodosa
tree. Workers patrol leaves, especially young leaves, and aggressively defend their plant
against herbivores (Frederickson et al. 2012a), which promotes plant growth
(Frederickson 2005, Frederickson & Gordon 2009). Cordia nodosa trees produce hollow
stem swellings (domatia, see Fig. 2.1) whether or not ants are present. There is one
domatium per internode, and each domatium is associated with a whorl of four leaves;
two additional leaves are on the stem below (Fig. 2.1). Inside the domatia, ants rear their
young (eggs, larvae, and pupae, collectively called brood) and also tend scale insects
(Hemiptera: Sternorrhyncha: Coccoidea) and eat the honeydew these scale insects
produce (Frederickson et al. 2012a). The ants also eat many of the insect herbivores they
attack, as well as the miniscule food bodies that grow on C. nodosa’s young leaves (Yu
& Pierce 1998, Frederickson et al. 2012a).
42
Experiment
In January 2012, we selected 40 individuals of Cordia nodosa occupied by Allomerus
octoarticulatus that had young (i.e., incompletely expanded) leaves, as both herbivory
and ant defence are concentrated on young leaves (Edwards et al. 2006). If young leaves
were initially too far off the ground to observe with ease, we used cord to secure the
branch in a lower position, at least 24 hours before observations. On each of the first four
days of the experiment, we measured initial ant aggression and standing herbivory (see
below) on ten plants and then randomly assigned them to two treatments (control or PKG
activator) after stratifying by estimated herbivore damage. In both treatments, we
attached a 2-mL micro-centrifuge tube containing a sugar solution to the stem below the
leaves where we measured aggression (Fig. 2.1). In the activator treatment, this tube
contained a 2.5 mM 8-Br-cGMP solution with 20% w/v sucrose. The control treatment
was 20% w/v sucrose only. We replaced the food tubes 7 and 13 days after initial
measurements, and then measured ant aggression and herbivory again on the 14th day.
We regularly observed ants in both treatments feeding on the solutions in the tubes.
Ant Attacks
We measured ant attacks towards common herbivores of C. nodosa, grasshoppers in the
family Eumasticidae (cf. Paramastax spp.). These grasshoppers are commonly found on
C. nodosa and other ant-associated plants, and did consume C. nodosa leaves in
preliminary trials. Because Lucas and Sokolowski (2009) showed that PKG can affect
ant aggression towards conspecific ants from other colonies, we also measured ant
43
aggression towards virgin queens from a different A. octoarticulatus colony (hereafter,
alates), which ants may recognize as conspecific intruders, and not herbivores. We
collected alates (from source colonies which were not among the 40 in our experiment)
and grasshoppers (from Cordia nodosa and other ant-plants) one to three days before use.
We tethered each insect to a leaf by tying the insect to a pin with thread and pushing the
pin through the leaf (about 2 cm from the domatium entrance, see Fig. 2.1). Expanding
young leaves are very fragile, so we tethered insects to leaves associated with the
domatium below the young leaves (Fig. 2.1). We measured ant aggression towards one
grasshopper and one alate per tree, presenting the two insects in random order. Every
minute for five minutes, we counted the number of ants stinging, biting, or walking on
the insect, and then removed the insect. We waited five minutes between trials, and then
attached the other insect to the opposite leaf (Fig. 2.1) and again measured how many
ants responded. We generated an aggression score for each insect by averaging the five
counts. We used the same protocol to measure ant aggression to herbivores and alates
both before and after the two-week experiment.
Herbivory and Plant Traits
At the beginning of the experiment, we also counted the number of domatia on the plant,
measured height to the highest point, and measured stem diameter at ground level. We
also measured the width and length (excluding the petiole) of the four young leaves
attached to the domatium. Before and after the experiment, we photographed damaged
leaves against a transparent grid (for scale). We analyzed the photographs in ASSESS (v.
1.0, 2002 American Phytopathological Society), a program that allows the user to
44
measure total leaf area and damage by selecting green, brown, or missing areas (see Prior
& Hellman 2010).
Statistical Analysis
We used generalized linear models with a negative binomial error distribution (in R v.
2.15.2) to analyze ant aggression scores for grasshoppers and alates, with treatment as a
main effect and initial aggression as a covariate. Because colony size may affect the
number of ants responding to a tethered insect and is correlated with plant size
(Frederickson & Gordon 2009, Frederickson et al. 2012a), we also included plant height
as a covariate; plant height predicted aggression more strongly than our other measures
of plant size (stem diameter and domatium counts). Finally, we included the date of the
behavioral assays as a random factor, to account for possible effects of variation in
weather. Interactions between the treatment and covariates were non-significant and were
excluded from the model (Engqvist 2005).
Herbivore damage was log-transformed to improve normality, and analyzed using
generalized linear models with a Gaussian error distribution. We excluded one control
plant and two treatment plants whose focal leaves were all missing, as many factors can
cause plants to shed leaves. Herbivory peaked on mid-sized leaves (supplementary Fig.
2.1), and so our analyses of herbivory included treatment and a quadratic leaf size
covariate (the linear term was not significant and was excluded). The treatment by
covariate interaction was significant, so the data did not meet the assumption of
homogeneity of regression slopes. Because this assumption was violated, the main effect
45
of treatment depended on the value of the covariate; following White (2003), we used the
Johnson-Neyman procedure to isolate the range of leaf sizes where herbivory differed
between treatments. We also ran separate quadratic regressions to confirm that treatment
changed the relationship between leaf size and herbivory.
Results
PKG activation changed how many ants attacked herbivores. Activator treatment
significantly increased ant aggression towards grasshoppers (X2=6.07, df=1, p=0.014;
Fig. 2.2). Colonies on larger plants were also more aggressive (X2=7.46, df=1,
p=0.0063), and colonies that were initially more aggressive remained more aggressive in
final measures (X2=7.91, df=1, p=0.0049). Analyzing the treatments separately, the final
aggression of ants in the control was correlated with their initial aggression (X2=7.68,
df=1, p=0.0056; Fig. 2.3a), but PKG activator treatment broke down this relationship
(X2=0.75, df=1, p=0.39; Fig. 2.3b). Ants’ attacks towards conspecific alates were not
affected by treatment, plant size, or initial aggression (results not shown).
Leaves received less damage in the PKG activator than in the control treatment (Fig.
2.4). For average-sized leaves, damage was significantly higher on control than PKG
activator treated plants (X2=9.72, df=1, p=0.0077), but since the treatment by leaf size
interaction was significant (X2=5.12, df=1, p=0.024), the treatment effect depended on
leaf size. The damage in the control plants was significantly higher (p<0.05) for leaves in
whorls in which the largest leaf was greater than 1.5 and more than 6.5 cm wide
(supplementary Fig. 2.1), which represents over half of the leaves measured. Separate
46
quadratic regressions on the two treatments confirmed that leaf damage peaked on mid-
sized leaves in the control (X2=6.66, df=1, p=0.0099), but remained low on leaves of all
sizes in the PKG activator treatment (X2=0.19, df=1, p=0.67; supplementary Fig. 2.1).
Thus, PKG activator treatment reduced herbivory on mid-sized leaves.
Discussion
When we fed A. octoarticulatus ants with the PKG activator, patrolling workers became
more aggressive towards herbivores. This effect extended to impact the ants’ host plants,
protecting them from damage during a developmental window when they may be most
vulnerable to folivory. We have thus shown for the first time that the behavioural effects
of PKG activation are detectable in a field setting. Though we did not directly assay
enzyme activity or gene expression, in flies (e.g. Dawson-Scully et al. 2010) and other
Hymenoptera (Ben-Shahar et al. 2002, Lucas & Sokolowski 2009), applying the PKG
activator has increased PKG activity and elicited the same behaviours normally
associated with high foraging gene. This suggests that the defensive behaviour we
measured here was similarly influenced by an ortholog of that gene. If so, then foraging’s
extended phenotype acts through ant aggression to impact plant performance in this
system.
Ant aggression also displayed substantial natural variation. Colonies on larger plants
were more aggressive; since plant and colony size are correlated in this system
(Frederickson & Gordon 2009, Frederickson et al. 2012a), this likely reflects an effect of
colony size on protection, which has been previously demonstrated (Heil et al. 2001,
47
Pringle et al. 2011). However, even after accounting for this effect, initially aggressive
colonies remained highly aggressive at the end of the experiment, particularly in the
control treatment. This may reflect other variation in the demographics of ant colonies
(e.g. number of brood or alates) or in background dietary state (see Chapter One), but
could also indicate persistent variation in the expression of foraging or other genes
affecting behaviour. Further study of the genetic architecture of these behavioural
phenotypes will illuminate precisely which genes these might be and their sensitivity to
environmental context, but the fact that PKG activation broke the association between
initial and final aggression suggests an overriding role for a foraging ortholog.
Even with substantial variation in aggression, we detected effects of PKG activation on
leaf damage. This effect was restricted to mid-sized leaves, as very small and large leaves
had low herbivory in both treatments. Grangier et al. (2008) similarly found that the
presence of Allomerus decemarticulatus ants affected herbivory only on mid-sized leaves
of their Hirtella physophora host plants; as in our study, very small and very large leaves
suffered negligible herbivory regardless of ants’ presence. Large, expanded leaves were
likely effectively protected by chemical and structural defences (e.g. toughness; Coley
1983, Kursar & Coley 1992, Frederickson, unpublished data). Very small leaves, in
contrast, were likely protected by high trichome density (Grangier et al. 2008) or by
biotic defence – food bodies are produced primarily on young leaves in C. nodosa
(Solano et al. 2005), and ant densities tend to be highest on these leaves in C. nodosa
(Edwards et al. 2006), as in many myrmecophytes (e.g. Gaume et al. 1997, Linsenmair et
al. 2001, Debout et al. 2005). As they grow, leaves may commonly experience a period
48
of vulnerability as biotic defences fall off, before abiotic defences reach full
effectiveness. However, treatment with the PKG activator reduced this vulnerability,
extending the defensive activity of ants to protect mid-sized leaves (supplementary Fig.
2.1). Though in the present study the activator’s effect was restricted to this size class, by
definition all leaves will pass through it while expanding. A longer study would likely
detect a broader effect of PKG activation on herbivory.
Such a long-term study would likely also show effects of PKG activity on the fitness of
both partners. Over the two weeks of our study, plants lost an average of 15 and 6 cm2 of
leaf tissue in the control and activator treatments, respectively, corresponding to
approximately 4.3% and 1.6% of leaf area. In the same population, Frederickson et al.
(2012b) showed that comparable differences in folivory had substantial effects on plant
height and domatium production. As larger plants produce more fruit (Yu & Pierce
1998), and house colonies with reduced mortality and increased reproduction
(Frederickson & Gordon 2009), increased PKG activity and expression should be
beneficial for both partners.
However, the high pleiotropy of foraging may suggest potential costs of higher activity
of expression. foraging orthologs are known to influence the allocation of workers to
different tasks in social insects (Ben-Shahar et al. 2002, Ingram et al. 2005, Lucas &
Sokolowski 2009, Tobback et al. 2008, Ingram et al. 2011), so increasing allocation to
protection may be costly to ants through reduced allocation to other tasks like nursing.
foraging may also affect other behavioural or physiological traits. In D. melanogaster
49
fruit flies, for instance, alternative alleles are associated with differences in sleep,
courtship, habituation, learning, and memory formation, as well as resistance to sleep
deprivation, starvation, anoxia, and high temperatures (Belay et al. 2007, Mery et al.
2007, Dawson-Scully et al. 2010, Chen et al. 2011, Burns et al. 2012, Donlea et al. 2012,
Eddison et al. 2012). Expression differences also influence sleep, habituation, and
movement in C. elegans (L’Etoile et al. 2002, Fujiwara et al. 2002, Raizen et al. 2008),
as well as more physiological traits like body size, fat storage, and longevity (Raizen et
al. 2006). Thus, while high PKG activity has short-term benefits for plants, the long-term
effects on ants may be more complex.
Regardless, if foraging is important to ant-plant cooperation, it suggests several avenues
for future research. For instance, the pleiotropic effects of foraging described above (e.g.
costs to fat storage, longevity; Raizen et al. 2006) suggest hypotheses for tradeoffs and
costs that plant-defending ants might experience. If foraging plays a role in this
interaction, it also suggests mechanisms by which host plants might manipulate ant
behaviour to their benefit. PKG is activated by cGMP, which is also a known signaling
molecule in plants (Isner et al. 2012) – our results suggest that plants could benefit if it is
possible to provide cGMP to ants through food bodies, or even through phloem sap via
scale insects. PKG activity is also responsive to starvation (Lucas & Sokolowski 2009,
Sokolowski 2010), and so our results may suggest a molecular reason why
myrmecophytic plants often feed ants (e.g. Folgarait & Davidson 1995, Solano et al.
2005): it may allow plants to keep ants’ PKG activity at optimal levels. How PKG
50
mediates cooperation in this and other systems merits further exploration, but our results
suggest some immediate directions.
The molecular basis for cooperation between plants and animals is largely unexplored,
precluding the kind of evolutionary genetic studies that have illuminated the adaptive
history of other mutualisms (e.g. De Mita et al. 2007). Here, we show that PKG, an
enzyme with diverse behavioural effects across taxa, also affects the protection that ants
provide to their host plants. Future work is needed to confirm a role for the foraging gene
in this interaction, but our study suggests that it does influence ants’ cooperative
behaviour, and that its phenotype extends to affect the performance of their plant
partners.
Acknowledgments
We thank Antonio Coral and Adam Cembrowski for field assistance; the Amazon
Conservation Association and the staff at Los Amigos for support; and members of the
Frederickson, Gilbert, Agrawal, and Thomson labs at the University of Toronto for
comments on this manuscript. We thank MINAG-DGFFS for permits to do research in
Peru (RD No. 299-2011-AG-DGFFS-DGEFFS and RD No. 278-2012-AG-DGFFS-
DGEFFS). We thank funding from an NSERC Discovery Grant, a Connaught
New Researcher Award, and the University of Toronto to MEF, and from a Sigma Xi
Grant-in-Aid-of-Research to KMT.
51
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Figures
Figure 2.1. Schematic of the experimental set-up on a C. nodosa branch. Domatia (dark
grey) occur at nodes, and are each associated with a whorl of four leaves, as well as two
leaves on the branch below. Herbivory was measured on young leaves (light grey). We
placed alates and grasshoppers at the base of leaves (*). The treatment food tube was
attached to the stem at the point indicated by X.
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Figure 2.2. Mean (± SE) number of attacks on grasshoppers per minute in the control
and PKG activator treatments.
63
64
Figure 2.3. Aggression score (attacks on grasshoppers averaged over five minutes)
before and after treatment, in control (a) and PKG activator-treated (b) colonies, with
least-squares regression lines. Each point represents a plant.
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Figure 2.4. Mean (± SE) area of herbivore damage in the control and PKG activator
treatments.
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Supplementary Figure 2.1. Damaged leaf area vs leaf size (the width of the largest leaf
in the whorl) in the control (black) and activator (white) treatments. The difference
between treatments was significant on mid-sized leaves (the region bounded by grey
lines). Each point represents a plant.
67
CONCLUDING REMARKS
Cooperative interactions are abundant, diverse, and implicated in many of the major
innovations in the evolutionary history of life (Bronstein 1994a, Bronstein et al. 2006).
Understanding how these interactions function and how their outcomes vary is important
for understanding the coevolutionary relationships between interacting partners.
Organisms cooperate when the benefits of doing so outweigh the cost, but on a proximate
scale, what drives cooperation? In this thesis, I have explored how organisms’
cooperative behaviours can vary, even when their partners’ contributions to the
interaction remain fixed. Using a specialized, symbiotic interaction between ants and
plants, I showed how cooperative behaviours change with the availability of different
resources. I also showed how a key enzyme linked to behaviour might influence
cooperation.
Colonies of Allomerus octoarticulatus protect their Cordia nodosa hosts by patrolling
plant tissues and killing herbivores that attempt to feed on the plant (Yu & Pierce 1998,
Frederickson 2005, Frederickson et al. 2012a). In Chapter One, I changed the
background diet of A. octoarticulatus colonies to examine whether this might disrupt
defensive behaviour. Provided with low-cost sources of proteinaceous food, colonies
invested less in hunting and attacking herbivores. This is likely an optimal strategy for
ants: hunting also provides the colony with protein, but is probably quite costly (e.g.
Ruiz-González et al. 2011). In nature, ants could gain access to protein through fungal
spores, pollen, or feces that land on their host plants; though the nutrient inputs from
68
such sources would seem to be low, the ant Tetraponera penzigi is reported to subsist
entirely on these types of materials gleaned from the surfaces of its host plant, Acacia
drepanolobium (Palmer et al. 2008). My results suggest that fluxes in the availability of
such sources may generate variation in the level of protection ants provide to their host
plants. The abundance of non-herbivorous insects that land on the plant could also affect
the interaction through diet, because ants would obtain protein from these insects, but
killing them would not benefit the plant. Variation in any exogenous food sources could
generate variation in plant fitness. Future study should explore how the components of
ants’ diets vary over time and space, and how the system may have evolved to buffer this
variation.
In Chapter Two, I explored how ant protection might also be influenced by PKG, an
enzyme encoded by the gene foraging. After I fed ants with a PKG activator, they
became more aggressive towards herbivores, and, in turn, their host plants benefited from
reduced herbivory. Further studies, currently underway, will examine whether natural
variation in foraging expression is similarly associated with variation in ants’ behaviour
and their efficacy as an anti-herbivore defence. My results suggest a number of avenues
to further explore this and other cooperative interactions. First, on a practical level, my
study demonstrates the utility of the PKG activator in manipulating behaviour in
ecologically meaningful ways. Many studies test the benefits of ant defence by removing
colonies from plants or by associating plant performance with natural variation in colony
size (Trager et al. 2010); the PKG activator makes it possible to manipulate behaviour
without immediately changing ant numbers. Second, if an ortholog of foraging is
69
conclusively shown to influence cooperative behaviour in ants, it will permit the kind of
evolutionary genetic studies that have illuminated the adaptive history of other
partnerships, like that between legumes and rhizobia (e.g. De Mita et al. 2007).
Both chapters of my thesis suggest ways in which plants could manipulate their resident
ant colonies to maximize protection. Myrmecophytic plants frequently produce food for
their resident ants (e.g. Janzen 1966, Folgarait & Davison 1995, Solano et al. 2005), and
the results of Chapter One suggest that plants will obtain the highest levels of defence by
keeping protein levels in this food relatively low. They may instead benefit from
producing high levels of sugars or other carbohydrates, as I found this to promote ant
activity in some colonies. Diet may also influence the interaction through effects on
PKG, as PKG activity changes in response to food deprivation in both flies (Sokolowski
2010) and ants (Lucas & Sokolowski 2009). PKG activity may be particularly responsive
to certain macronutrients, and so plants may have evolved a nutrient balance in their food
that optimally affects PKG activity and ant behaviour. Further, the activator that I used in
my experiment is 8-Br-cGMP, a non-hydrolysable, membrane-permeable form of cGMP,
the cyclic nucleotide that naturally activates PKG. The fact that cGMP also serves as a
signaling molecule in plants (Isner et al. 2012) suggest the tantalizing additional
possibility that plants could directly manipulate PKG activity if some similarly non-
hydrolysable form of the molecule is present in the food plants produce for ants. Thus,
both diet and behavioural genetics may interact to drive cooperation between plants and
their ant bodyguards.
70
Overall, I have highlighted two major potential sources of variation in cooperation
among species. As many mutualisms involve an exchange of food, and all involve the
exchange of resources or services, it is important to be cognizant of how the background
availability of those resources might change the value of rewards on offer, even when the
actual level of reward provided appears to be fixed. Additionally, there is an enormous
gulf of knowledge yet unexplored in terms of how genes like foraging might influence
cooperation. The work I have presented shows that it is important to consider both diet
and genes involved in behaviour to fully understand cooperation between ants and plants,
and among other species involved in mutualism.
71
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APPENDIX A
Pilot study: The effect of PKG on cooperation may vary across systems
Abstract
Mutualisms are abundant in nature, yet we know very little about the molecular basis of
cooperative behaviours. In Chapter Two, we provided evidence that PKG, an enzyme
encoded by the gene foraging, influences protective behaviour in a plant-dwelling ant.
Here, we tested whether similar effects could be found in other cooperative interactions
by feeding an activator of PKG to two species of Crematogaster ants living on Acacia
drepanolobium plants. In one of the two species, C. nigriceps, PKG activation caused
ants to be somewhat less responsive when the plant was disturbed, and to recruit less
readily to protein baits. In the other species, C. mimosae, activator treatment had no
effect on any behaviour measured. We suggest that some inconsistencies between species
may be due to differences in genetic architecture, though others may be due to
differences in context or in the behaviour studied.
Introduction
Many species participate in mutually beneficial interactions with other species, and such
interactions are implicated in major ecological and evolutionary shifts throughout the
history of life (Bronstein 1994, Redecker et al. 2000, Bronstein et al. 2006, Janson 2008,
Ramírez et al 2011). Understanding the molecular basis for these interactions makes it
possible to examine their adaptive history by screening genes involved in the interaction
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for signatures of selection (e.g. De Mita et al. 2007). Identifying the genes involved in
convergent coevolutionary shifts (e.g. Zhang et al. 2012) also deepens our understanding
of what genetic or genomic conditions allow those shifts to occur. However, knowledge
of the molecular underpinnings of cooperation between plants and animals remains
limited.
Plant-animal interactions, including pollination, seed dispersal, third-party defence,
inevitably involve basic behaviours like movement, foraging, and learning. Recent work
in behavioural genetics has identified a number of genes influencing these behaviours
(Fitzpatrick & Sokolowski 2004, Fitzpatrick et al. 2005), generating a list of candidate
genes that may influence cooperative interactions. The foraging gene, for instance,
influences food-related behaviours and activity levels across taxa (Osborne et al. 1997,
Ben-Shahar et al. 2002, Fitzpatrick & Sokolowski 2004, Tobback et al. 2008). In social
Hymenoptera, the shift from nursing work to foraging has been linked with changes in
both the expression of foraging orthologs, and with the activity of foraging’s product, the
enzyme protein kinase G (PKG; Ben-Shahar et al. 2002, Ingram et al. 2005, Tobback et
al. 2008, Ingram et al. 2011). Lucas and Sokolowski (2009) also demonstrated that PKG
influences nest defence in the ant Pheidole pallidula. Since PKG influences food
collection and aggression, among other traits, it likely plays a role in a variety of species
interactions.
In Chapter Two, we examined the potential effects of PKG on a symbiotic interaction
between ants and plants, myrmecophytism. In this interaction, plants produce hollow
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housing structures and food for ants, and ants in exchange patrol plant surfaces and deter
herbivores (Heil & McKey 2003, Bronstein et al. 2006). In our experiment, we provided
plant-dwelling Allomerus octoarticulatus ants with a PKG activator (8-Br-cGMP), which
caused the ants to become more aggressive towards herbivores. Their Cordia nodosa
host plants, in turn, benefited from reduced herbivory. However, PKG may not affect
other myrmecophytic interactions in the same way, as the effects of foraging orthologs
are known to vary across taxa. In D. melanogaster larvae, for instance, high movement
while feeding is associated with a high-expression allele of the gene; in constrast, high
movement during feeding is associated with low PKG levels in C. elegans nematodes
(Fitzpatrick & Sokolowski 2004). Even within ants, associations vary: while foraging
workers in Pogonomyrmex occidentalis harvester ants have elevated foraging expression
(Ingram et al. 2011), in Pheidole pallidula, high expression is associated with reduced
foraging (Lucas & Sokolowski 2009). Thus, we wanted to explore how the effects of
PKG on cooperative behaviour, as described in Chapter Two, might also vary among
taxa.
To examine this possibility, we performed a study on two of the ant partners of
myrmecophytic Acacia drepanolobium. This small tree dominates certain soil types in
East Africa (Young et al. 1997), and is protected from herbivory by both spines and
active colonies of ants that inhabit swollen thorns and feed on extrafloral nectar (Hocking
1970). Unlike in Cordia nodosa, where insect herbivores cause the majority of damage
(Dejean et al. 2004), damage by large vertebrates has the strongest influence on growth
in A. drepanolobium (Stanton & Palmer 2011). In this study, we focused on two of the
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four primary associates of A. drepanolobium, Crematogaster mimosae and C. nigriceps.
Crematogaster mimosae is more responsive to herbivores (Stanton & Palmer 2011),
recruits more actively to protein baits (Palmer 2003), and is often successful in territorial
conflicts over C. nigriceps (Palmer et al. 2000). Crematogaster nigriceps is a poorer
competitor, and a less active defender (Palmer et al. 2000). It also crops axillary buds on
its host trees, directing growth away from competitor colonies (Stanton et al. 1999). In
this study, we explored whether PKG activation might influence cooperation between
these ants and their host trees, and whether the effect was consistent between the two ant
species.
Methods
Study System
We took advantage of a greenhouse population of A. drepanolobium at Harvard
University. Seeds were collected in Laikipia, Kenya (0°17’ N, 37°52’ E, ~1800 m
elevation) in March, 2011, and grown in the greenhouse. Colonies of Crematogaster
nigriceps and C. mimosae were collected from the same population in March, 2012, and
maintained in containers with their clipped domatia and water tubes in an environmental
chamber. Between April and early October, 2012, a single colony was introduced to each
tree. For this experiment, we used 16 colonies of C. mimosae, and 20 of C. nigriceps.
Experiment
The experiment was conducted in October, 2012. On the first day of the experiment, we
counted the number of swollen thorns on the plants, and then measured each colony of
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both species for ant activity, swarming, and recruitment to baits (see below). Then, we
assigned each colony randomly to one of two treatments, PKG activator or control, after
stratifying by the number of ants on the plant. In both treatments, we attached a 1 mL
centrifuge halfway up the plant. In the PKG activator treatment, this contained 0.4 mL of
a 3.5 mM 8-Br-cGMP in distilled water, with 10% w/v sucrose added as a feeding
stimulus. In the control, this tube contained only 0.4 mL of 10% sucrose in distilled
water. These feeding tubes were replaced on the third and fourth days of the experiment,
and we repeated the activity, swarming, and recruitment measures on the third and fifth
days, after which we ended the experiment.
Ant Activity and Swarming
To measure ant activity, we counted the total number of worker ants visible on the plant
(i.e. outside the swollen thorns). To examine allocation to foraging vs allocation to plant
defence, we also counted the subset of ants that were feeding at extrafloral nectaries, and
that were crawling on leaves.
After these counts, we subjected trees to a disturbance simulating vertebrate herbivory.
We vigorously shook each plant across a ~10° arc for 10 seconds, then counted the
number of ants swarming on the plant every 30 seconds for five minutes. Similar trials
have successfully elicited ant responses in A. drepanolobium previously (e.g. Madden &
Young 1992). Ant responses rapidly diminished after 30 seconds, so we only analyzed
counts at that time point.
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Recruitment
After activity and swarming measures, we affixed three bait tubes halfway up the plant,
to measure the recruitment of ants to different food sources. One tube contained ~0.15
mL of pure clover honey, and the second contained ~0.15 cm3 of tuna meat. Since C.
nigriceps destroys axillary buds (Stanton et al. 1999), the third tube contained a single
axillary bud cushion collected from one of four source plants not used in the experiment.
At 10, 20, and 30 minutes following the attachment of the tubes, we counted the number
of worker ants found in the interior of each.
Statistical Analyses
We used generalized linear models with negative binomial errors in R (v. 2.15.2) to
analyze all data. We first tested all response variables with species, treatment, and their
interaction as predictors. As we were interested in how each species responded to
treatment, we additionally ran each model for the two species separately. Swarming
responses were highly variable between colonies, and so the models for swarming also
included pre-treatment (first day) swarming counts as a covariate, as well as the number
of swollen thorns on the plant, as a proxy for potential colony size. Covariate interactions
were not significant, and we excluded them from the model (Engqvist 2005).
Results
Species Differences
Crematogaster mimosae colonies recruited more to some food baits than C. nigriceps,
but we generally failed to detect differences between the two species (Table I). On the
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third day of the experiment, C. mimosae recruited more than C. nigriceps to honey baits,
but the difference was only significant 20 minutes after placement. Crematogaster
mimosae also recruited more to tuna baits on the fifth day, but the difference was only
significant at the 10- and 30-minute time points. No other responses significantly
differed between species (Table I), though swarming and recruitment to tuna showed
marginal species by treatment interactions, so we tested for treatment effects in each
species separately.
Ant Activity and Swarming
For C. nigriceps, PKG activator treatment somewhat decreased swarming in response to
a disturbance. On the final day of the experiment, Crematogaster nigriceps colonies in
the PKG activator treatment had marginally fewer ants swarming (X2=2.83, df=1,
p=0.092; Fig. 1). Colonies that had strong responses before treatment had similarly
strong responses after treatment (X2=20.42, df=1, p<0.0001), and colonies on plants with
more swollen thorns were also marginally more responsive (X2=3.70, df=1, p=0.054).
The effect of PKG activator treatment was not present on the third day of the experiment
(results not shown), and treatment did not affect the total activity of ants or their
allocation to nectaries or leaves (Table II).
Crematogaster mimosae colonies were completely unaffected by treatment. On the third
day of the experiment, swarming counts were significantly predicted by the same
measure before treatment (X2=23.03, df=1, p<0.0001), and plants with more swollen
thorns had marginally more responsive ants (X2=2.84, df=1, p=0.092), but treatment had
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no effect (X2=2.21, df=1, p=0.14; Fig. 2). On the fifth day, colonies that had been more
responsive before treatment were still more responsive (X2=22.09, df=1, p<0.0001), but
there was no effect of swollen thorn numbers (X2=1.36, df=1, p=0.24) or treatment
(X2=1.06, df=1, p=0.30). Ant activity was also unaffected by treatment (Table II)
Recruitment
The PKG activator also depressed the response of C. nigriceps to the tuna bait (Fig. 2).
On the fifth day, immediate recruitment (10 minutes after the bait was placed) was
significantly lower in the PKG activator treatment, though the treatment difference
attenuated over time, and was only marginally significant after twenty and thirty minutes
(Table II). Again, this difference was not present on the third day of treatment. There
were also no effects of treatment on recruitment to honey or axillary buds. Treatment had
no effect on the recruitment of C. mimosae to any bait type (Table II).
Discussion
The effect of the PKG activator on ants’ protective behaviour was limited. The activator
treatment did depress recruitment to protein baits in Crematogaster nigriceps, which is
consistent with Lucas & Sokolowski’s (2009) finding that activator treatment made
Pheidole pallidula ants less inclined to collect mealworms. However, activator treatment
also appeared to depress the response of C. nigriceps to shaking of the tree. This result is
inconsistent with the findings reported in Chapter Two, where we found that PKG
activation made Allomerus octoarticulatus workers more aggressive towards herbivores
that threatened their host plants. Treatment did not affect the total number of ants active
95
on the plants, nor their allocation to nectaries or leaves. It also did not affect their
recruitment to honey or axillary buds. In C. mimosae, no measures were affected by
treatment.
There are a number of potential explanations for the inconsistencies between this study
and that described in Chapter Two, and between the two species studied here. First, it is
highly likely that the genetic architecture underlying the traits of interest varies across
taxa. The effect of foraging orthologs on food-related behaviour varies between
Drosophila melanogaster and C. elegans (Fitzpatrick & Sokolowski 2004), as well as
within Hymenoptera (Ben-Shahar et al 2002, Tobback et al. 2008, Kodaira et al. 2009,
Tobback et al. 2011) and within ants in particular (Ingram et al. 2005, Lucas &
Sokolowski 2005, Ingram et al. 2011). The effect of foraging orthologs on plant-defence
behaviours could be similarly variable. Though strong variation in gene regulation seems
unlikely to explain differences between two species within the same genus, differences
may have arisen due to demographic differences: C. mimosae has higher worker densities
per thorn (Palmer 2004), and this could dilute any perturbations to their behaviour. Thus
species could simply differ in the way PKG activity is regulated or affected by treatment.
Differences in results between this study and the one described in Chapter Two could
also indicate that the behaviours measured are in fact not comparable. In Chapter Two,
we measured how many ants attacked grasshoppers, as invertebrate herbivores are the
major defoliators of Cordia nodosa (Dejean et al. 2004); in this study, we measured
swarming after trees were disturbed, since this behaviour deters vertebrate herbivores
96
(Madden & Young 1992), which are more important to Acacia (Stanton & Palmer 2011).
Though these behaviours are both, broadly, ‘anti-herbivore behaviours’, we would not
necessarily expect them to have the same genetic basis. This may also explain
inconsistencies among previous studies. For instance, though Lucas and Sokolowski
(2009) and Ingram et al. (2011) found opposing associations between foraging
expression and food-collection behaviour, this comparison was between seed-collecting
and predatory ants, respectively. Seed-carrying and prey-hunting behaviours may have
distinct evolutionary origins, and so we would not expect the genetic basis to be
identical, even though they are both generally foraging behaviours.
Finally, it is likely that much of the failure to detect consistent treatment effects can be
attributed to issues with the study. The study was conducted across a short time scale
(five days, as compared with two weeks in Chapter Two), and suffered from low sample
sizes, reducing statistical power. Indeed, though the differences between the two
Crematogaster species are well established (e.g. Palmer et al. 2000, Stanton & Palmer
2011), we failed even to detect consistent differences between them, though the
differences we did detect (some evidence of higher recruitment to food by C. mimosae)
are consistent with expectations (Palmer 2003). While the greenhouse setting was
intended to minimize variation in environmental conditions, the setting was highly
unnatural. Colonies were removed from their original host trees and re-introduced to new
ones, sometimes after several months. Further, ants patrolling the trees encountered
herbivores and competitors they would not face in a natural setting, including mealybugs,
spider mites, and Cardiocondyla obscurior ants. These factors introduced substantial
97
variation into their responses, and obscured treatment effects that may have been present.
The unnatural context also makes it difficult to conclude that the limited effects detected
would be similar in a natural setting.
However, the limited results do suggest that it would be worthwhile to repeat a similar
study with a larger number of plants in a natural setting. Additionally, this study still may
indicate that the influence of genes on ecological interactions can vary substantially
between taxa. However, it also demonstrates that it is important to measure consistent,
comparable behaviours across species in order to draw any firm conclusions about how
gene effects change between systems. And finally, it demonstrates that the effects of
genes on species interactions may be quite subtle, and easily swamped by other sources
of variation, or affected by differences in context. It remains clear that there is much left
to be explored in terms of how genes may influence cooperation between species.
Acknowledgments
We thank the Pierce Lab at Harvard for collection of the plant population, and for access
to lab space and equipment. We thank Chris Baker, Julianne Pelaez, Jignasha Rana, and
Kadeem Gilbert for maintaining colonies and for assistance with the experiment.
Research was supported by a John Templeton Grant to Naomi Pierce, and KMT was
supported by an NSERC Michael Smith Foreign Study Supplement.
98
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Tables
Table I. Results (X2, p-value) for tests of differences between Crematogaster mimosae
and C. nigriceps, and between the PKG activator treatment and the control. Response
variables are ant activity counts, swarming counts, and recruitment, on the third and fifth
days of the experiment. For recruitment tests, results are shown for counts of ants 10, 20,
and 30 minutes after placement of the bait. Marginally significant differences are
highlighted in italics, and significant differences are highlighted in bold. In all cases,
there is one degree of freedom.
predictor response species treatment species x
treatment total ant activity day three 1.52, 0.22 0.74, 0.39 0.18, 0.67 day five 1.17, 0.28 0.52, 0.47 0.04, 0.85 ants on leaves day three 1.14, 0.29 0.61, 0.43 0.03, 0.85 day five 0.31, 0.58 0.06, 0.80 0.12, 0.73 ants at nectaries day three 0.02, 0.89 0.05, 0.82 0.02, 0.90 day five 0.17, 0.68 0.18, 0.67 0.01, 0.92 swarming day three 0.00, 0.99 2.27, 0.13 3.54, 0.06 day five 0.08, 0.78 0.94, 0.33 2.63, 0.10 recruitment to tuna day three: 10 minutes 2.14, 0.14 0.01, 0.92 0.01, 0.93 20 minutes 1.22, 0.27 0.00, 0.98 0.32, 0.57 30 minutes 1.72, 0.19 0.00, 0.97 0.77, 0.38 day five: 10 minutes 5.55, 0.02 0.05, 0.83 1.78, 0.18 20 minutes 2.09, 0.15 0.03, 0.86 0.87, 0.35 30 minutes 4.34, 0.04 0.06, 0.81 2.88, 0.09
103
Table I continued
predictor response species treatment species x
treatment recruitment to sugar day three: 10 minutes 2.24, 0.13 0.12, 0.73 0.79, 0.37 20 minutes 5.11, 0.02 0.03, 0.87 1.60, 0.21 30 minutes 1.88, 0.17 0.04, 0.85 0.90, 0.34 day five: 10 minutes 0.22, 0.64 1.58, 0.21 0.70, 0.40 20 minutes 0.06, 0.80 2.89, 0.09 1.27, 0.26 30 minutes recruitment to buds day three: 10 minutes 0.66, 0.42 0.08, 0.78 0.04, 0.85 20 minutes 0.99, 0.32 0.46, 0.50 0.62, 0.43 30 minutes 0.43, 0.51 0.50, 0.48 0.69, 0.41 day five: 10 minutes 0.16, 0.69 0.01, 0.93 0.27, 0.61 20 minutes 0.00, 0.96 0.00, 1.00 0.02, 0.90 30 minutes 0.06, 0.80 0.45, 0.50 0.03, 0.87
104
Table II. Results for tests of effects of PKG activator treatment (vs. control) in
Crematogaster nigriceps and C. mimosae, on the third and fith days of treatment. For
recruitment tests, results are shown for counts of ants 10, 20, and 30 minutes after
placement of the bait. On the fifth day, no C. nigriceps workers recruited to sugar.
Marginally significant differences are highlighted in italics; the significant difference is
highlighted in bold. In all cases, there is one degree of freedom.
C. nigriceps C. mimosae response X2 p X2 p recruitment to tuna day three: 10 minutes 0.060 0.81 0.0082 0.93 20 minutes 0.71 0.40 0.00064 0.98 30 minutes 1.41 0.24 0.0019 0.97 day five: 10 minutes 4.53 0.033 0.033 0.86 20 minutes 2.64 0.10 0.87 0.35 30 minutes 3.46 0.063 0.47 0.49 recruitment to sugar day three: 10 minutes 1.39 0.24 0.11 0.74 20 minutes 0.18 0.67 0.032 0.86 30 minutes 1.11 0.29 0.034 0.85 day five: 10 minutes -‐ -‐ 1.17 0.28 20 minutes -‐ -‐ 2.03 0.15 30 minutes -‐ -‐ 1.45 0.23 recruitment to buds day three: 10 minutes 0.00 1 0.070 0.79 20 minutes 0.18 0.67 0.45 0.50 30 minutes 0.24 0.63 0.43 0.51 day five: 10 minutes 0.62 0.43 0.067 0.80 20 minutes 0.05 0.83 0.00 1 30 minutes 0.25 0.61 0.48 0.49
105
Table II continued
C. nigriceps C. mimosae response X2 p X2 p total ant activity day three 0.12 0.73 0.71 0.40 day five 0.33 0.56 0.42 0.52 ants on leaves day three 0.34 0.56 0.72 0.39 day five 0.55 0.46 0.078 0.78 ants at nectaries day three 0.22 0.64 0.042 0.84 day five 0.14 0.71 0.13 0.72
106
Figures
Figure 1. Mean (±SE) number of C. nigriceps ants swarming on plants in the control and
PKG activator treatment 30 seconds after a simulated vertebrate disturbance, after four
days of treatment.
107
Figure 2. Mean (±SE) number of C. mimosae ants swarming on plants in the control and
PKG activator treatment 30 seconds after a simulated vertebrate disturbance.
108
Figure 3. Mean (±SE) number of C. nigriceps ants, four days after treatment, in tuna
baits in the control (black) and PKG activator (white) treatment 10, 20, and 30 minutes
after bait placement. The treatment difference is significant (p = 0.033) at 10 minutes,
and marginally significant at 20 (p=0.10) and 30 (0.063) minutes.