Exploring whether and how ants (Hymenoptera: Formicidae) affect reproductive fitness in Senna mexicana var. chapmanii (Fabaceae).
Many studies have identified food-for-protection mutualisms between ants and plants (Koptur 1992; Rosumek et al. 2009). In some cases, plants provide domatia and food bodies, as well as EFN, and the resulting interactions may be highly specialized. Janzen (1966) observed that Acacia cornigera (L.) Willd. (Fabaceae) plants succumbed to herbivory when resident Pseudomyrmex ferruginea Smith (Hymenoptera: Formicidae) ants were experimentally removed. Plants that provide only EFN are normally involved only in facultative interactions with ants (Rosumek et al. 2009). Despite the less specialized nature of these interactions, significant fitness benefits for plants have been reported (Koptur 1979; Koptur 1984; Oliveira 1997; Rudgers 2004; Kopturetal. 2013).
The presence of ants may benefit plants in a number of ways. Aggressive ants have been shown to reduce herbivore numbers on many plant species (Letourneau & Barbosa 1999; Dejean et al. 2010), and numerous studies have observed reduced rates of herbivore damage in the presence of ants (Janzen 1966; Bruna et al. 2004; Del-Claro et al. 2006; Jones et al. 2017). Extrafloral nectar is found on the fruits of many species. Indeed, production of EFN has been shown to increase during fruit production, in line with optimal defense theory (Wackers & Bonifay 2004; Holland et al. 2009). These observations suggest a role for ants in the protection of developing fruit. In addition to the provision of defense, the proximity of ant nests may benefit plants by enhancing soil nutrient concentrations (Wagner 1997; Wagner & Nicklent 2010). Wagner (1997) found that nests of Formica perpilosa Wheeler (Hymenoptera: Formicidae) at the base of Acacia constricta Benth. (Fabaceae) shrubs enhanced nitrate, ammonium, and phosphorus availability in the surrounding soil. Plants with nests at their base produced significantly more seeds than plants without nests (Wagner 1997).
Despite these well-documented benefits, plants may also suffer a range of costs associated with their ant partners. Some less aggressive ant species consume nectar, but provide no defensive benefits for plants (Freitas et al. 2000; Ruhren 2003). Indeed, in a few cases ants have even been seen to affect plant defense negatively (Frederickson & Gordon 2007; Mooney 2007; Rosumek et al. 2009). Conversely, overly aggressive ants may deter beneficial insects such as predators (Torres-Hernandez et al. 2000; Nahas et al. 2012), parasitoids (Styrsky & Eubanks 2007; Rosumek et al. 2009), and pollinators (Ness 2006; Hernandez-Cumplido et al. 2010; Assuncao et al. 2014). Several studies have shown that pollinators recognize the dangers posed by aggressive ants (Hernandez-Cumplido et al. 2010, Assuncao et al. 2014). Assuncao et al. (2014) placed plastic ants on the petals of Heteropterys pteropetala A. Juss. (Malpighiaceae) and found that flowers with plastic ants produced significantly less fruit than control flowers.
Ant-plant associations occur not in isolation, but within a complex web of biotic interactions, and in a framework provided by the abiotic environment. In the cactus Ferocactus wislizeni Engelm. (Cactaceae), plants defended by Solenopsis xyloni McCook (Hymenoptera: Formicidae) ants exhibit reduced herbivory and increased flowering. These plants, however, receive fewer and shorter visits from pollinators, which are deterred by the same ferocious ants (Ness 2006). Understanding the outcome of ant-plant interactions, therefore, requires that we focus on the broader multi-guild, multi-trophic interactions of which they are a part. While the presence of ants has been shown to boost reproductive fitness in a number of EFN producing species (Oliveira 1997; Freitas et al. 2000; Rudgers 2004; Rosumek et al. 2009; Heil et al. 2015), the specific mechanisms by which ants facilitate increased plant fitness are not fully understood for many species. In the present study, we aimed to determine not just whether, but how ants increase plant reproductive fitness in the known myrmecophile, Senna mexicana var. chapmanii (lsely) H. S. Irwin & Barneby.
Senna mexicana var. chapmanii (hereafter referred to as 5. chapmanii) is native to south Florida and the Caribbean. This species grows in pine rockland habitat and rockland hammock edges as an upright or sprawling subshrub up to 1.2 m in height, spreading broader than tall. Flowers offer no nectar to floral visitors and are visited by bees collecting pollen by 'buzzing' the anthers (Koptur, personal observation). Extrafloral nectaries occur on the pedicels of flowers in the inflorescences, as well as throughout the foliage between basal leaflets. Previous work with 5. chapmanii has shown that EFN production is responsible for the recruitment of ants to plants (Jones & Koptur 2015). Ants also remove key herbivores (Koptur et al. 2015), and plants with ants excluded suffer increased herbivore damage and reduced seed set (Jones et al. 2016).
We conducted an 8 mo field study (Oct-May), encompassing 1 entire flowering season for 5. chapmanii. The presence of ants on test plants was manipulated to address the question: how does the presence of ants increase reproductive fitness in 5. chapmanii? We determined the effects of ants on rates of flowering, fruit set, and seed production. We observed changes in plant size over the course of the study. Finally, we observed the effects of ants on the activity and effectiveness of pollinators and on pre-dispersal seed predators. We predicted that the presence of ants would lead to increased plant size and increased flower production. We also predicted that ants would have a neutral or negative effect on pollination rates, but that those flowers that did set fruit would be more likely to reach maturity in the presence of ants. During previous studies, we have regularly seen ants patrolling developing fruit, and therefore we hypothesized that a reduction in pre-dispersal seed predation would account for much of the difference in seed set between plants with and without ants.
Materials and Methods
This field study was conducted at the University of Florida, Tropical Research and Education Center (TREC) in Homestead, Florida, USA. The climate is subtropical, with average minimum and maximum temperatures of 3.2 to 24.8 [degrees]C in Jan and 22.7 to 32.4 [degrees]C in Jul (Koptur et al. 2015). The study site consisted of flat calcareous limestone rocklands that have been rock-ploughed for agriculture. We used a 2 acre plot, previously overgrown with exotic pest plants, which had been cleared of vegetation except for a few large native trees. Adjacent to the western edge of the plot is a fragment of pine rockland habitat, a protected natural area.
Senna chapmanii plants were grown from seeds in a greenhouse at Florida International University (FIU), Miami, Florida. Seeds were collected from multiple individuals in a single population on Big Pine Key, in the lower Florida Keys (under Research Permit # FFO4RFKD-2014-0, National Wildlife Refuge System, National Key Deer Refuge). Three mo after germination, 30 plants were transplanted into the experimental site. Plants were mulched with wood chips and watered for 2 mo, beginning in Aug 2014, until they were established. Plants were installed in an evenly spaced array, at least 4 m from their nearest neighbor, and divided into 2 treatments: (1) ants present (control) and (2) ants excluded. In the ants excluded treatment, a sticky resin (Tanglefoot[TM]) was painted around the base of the stem 1 mo prior to the start of data collection. Tanglefoot[TM] was re-applied every 2 wk for the duration of the experiment. Treatments were assigned systematically to ensure an even distribution across the site. Data were collected over a period of 8 mo from Oct 2014 to May 2015.
Each week, 1 active inflorescence was chosen from all plants that were in flower, and used as a census locale. Each chosen branch was studied over a period of 2 min, and the numbers and species of ants, herbivores, and predators were recorded. Any new species were collected and brought back to the lab at FIU for identification.
In addition to surveys of insects on the inflorescences, monthly ant surveys were conducted throughout the experiment, both to verify that ant exclusion treatments were working and to determine any temporal changes in ant activity at the study site. A single non-flowering branch was chosen from each plant and observed for 2 min. The number and species of ants observed on the branch were recorded.
Pollinator observations were conducted on a weekly basis. Plants with active inflorescences were observed for periods of 15 min, and the number of flower visitors was recorded. The identity of each visitor and the length of the visit were recorded. For each plant observed, the number of inflorescences at the time of the observation was recorded, so that the effects of inflorescence number on pollinator attraction could be determined. Pollinator observations were carried out between 8 am and 5 pm, and over 15 h of observation time was accumulated, equally distributed between treatment and control plants.
Senna chapmanii is a sprawling subshrub, growing broader than tall and commonly branching from nearthe base. As such, the number of branches is an effective proxy for plant size. Plant size was estimated monthly throughout the study by counting the number of branches. A branch was classified as any growing stem with at least 10 leaves.
PLANT REPRODUCTIVE FITNESS
During the course of the experiment, 3 open flowers were collected from each study plant to determine the average number of ovules per flower. Although flowers were collected from each plant on an opportunistic basis, each week, an equal number of flowers were collected from treatment and control plants. Where possible, flowers from an individual plant were taken from different inflorescences. Flowers were returned to the laboratory, and their ovaries were dissected under a light microscope to determine number of ovules. The mean number of ovules per flower was calculated for each plant.
Measures of gross plant reproductive output (numbers of inflorescences, flowers, mature fruit, and mature seeds) were measured on a weekly basis throughout the experiment. Each week, any new inflorescences were labelled with a numbered jewelry tag. The number of open flowers, new fruit set, and the number of mature fruit were then recorded for both new and previously marked inflorescences. All mature fruit were collected from each plant and returned to the lab. Fruit were dissected to determine the number of fertilized ovules, the number of intact seeds, and the number of herbivore-damaged seeds. The number of fertilized ovules could be determined by counting the seed chambers in the mature fruit. Because Senna species are buzzpollinated, and require an insect visitor to set seeds (Marazzi et al. 2015), the proportion of ovules fertilized in each plant can be used as a measure of pollinator effectiveness. Herbivore-damaged seeds were counted as any seeds with obvious herbivore damage, along with empty seed chambers that contained seed debris. Empty seed chambers that contained no evidence of herbivore activity were assumed to be aborted seeds.
The overall rate of pre-dispersal seed predation was calculated for each plant as the number of herbivorized seeds divided by the total number of developing seeds (fertilized ovules minus aborted seeds). Effective fecundity was calculated for each plant as the number of non-predated mature seeds divided by the total number of ovules. Herbivores found within seed pods were collected and identified. Larval herbivores were reared in the lab and identified as adults. Voucher specimens of these, and all other insects, were preserved and stored at FIU.
Extrafloral nectar production was measured in each plant, every 2 mo throughout the study. A single branch was selected from each plant, and any insects present were removed by hand. Nectaries were then washed by lightly spraying with water. Leaves were then dried with tissue paper, and branches were sealed within fine mesh bags to exclude insects. Bags were placed on branches at 7 PM, and removed 12 h later for nectar measurements at 7 AM.
Combined nectar volume from the 5 most apical leaves was measured with 1,2, and 10 [micro]L micropipettes. Nectar concentration was measured with a handheld refracto meter, and total sugar production ([micro]g) was estimated from the combination of these measurements (Jones & Koptur, 2014). In the results, EFN is expressed as total sugar production.
Due to the high number of zeros in the data, insect survey data, pollinator watch data, seed herbivory data, and plant reproductive fitness data could not meet parametric assumptions even after transformation. As such, median insect numbers from each guild were compared between treatments by Mann-Whitney U tests. The number and duration of pollinator visits, the rate of pre-dispersal seed predation, and median measures of plant reproductive fitness (numbers of inflorescences, flowers, fruits, and seeds) were compared between treatments by Mann-Whitney U tests. The relationship between pollinator visits and the number of active inflorescences was analyzed by 2-tailed Spearman correlation.
Repeated-measures ANOVAs were used to investigate the effects of ant presence or absence on the dependent variables of plant size and production of EFN. Plant size data were [log.sub.10] transformed to meet parametric assumptions. Extrafloral nectar data were [log.sub.10](x+l) transformed as the data set contained some zeros. All statistical analyses were performed with SPSS Version 23 and, in all cases, results were considered statistically significant when P values were [less than or equal to]0.05.
During our censuses, a total of 96 ants from 9 species were observed in the inflorescences of Senna chapmanii. The majority of ant activity within the inflorescences (84%) could be attributed to 4 species: Camponotus floridanus Buckley (Hymenoptera: Formicidae) (25%), Camponotus sexguttatus Fabricius (Hymenoptera: Formicidae) (23.9%), Camponotus planatus Roger (Hymenoptera: Formicidae) (19.8%), and Brachymyrmex obscurior Forel (Hymenoptera: Formicidae) (14.6%).
A total of 144 ants were observed on the foliage of S. chapmanii during monthly ant surveys. The same 4 species found on inflorescences accounted for the majority of ant activity on leaves, representing 15.5%, 9.7%, 9%, and 45% of ant activity, respectively. Brachymrmex obscurior was the dominant species on the foliage, while Camponotus species were seen most frequently in the inflorescences.
Ant numbers were significantly higher on control plants than on Tanglefoot[TM]-treated plants, both in the inflorescences (N = 30; df = 29; U = 12.5; P<0.001), and during monthly foliar ant surveys (N = 30; df = 29; U = 27.5; P< 0.001).
HERBIVORES AND PREDATORS
A total of 34 herbivores were observed in the inflorescences of 5. chapmanii, of which the most abundant were pierid caterpillars (Lepidoptera: Pieridae) belonging to 3 species, Abaeis nicippe (Cramer) (the sleepy orange), Phoebis philea (L.) (the orange-barred sulfur), and Phoebis sennae (L.) (the cloudless sulfur). Thirteen pierid caterpillars were recorded, accounting for 38.2% of herbivore observations. The 2nd most abundant herbivore was the leucaena psyllid, Heteropsylla cubana Crawford (Hemiptera: Psyllidae). Eight groups of psyllid nymphs were observed in inflorescences, accounting for 23.5% of herbivore observations. Numbers of pierid caterpillars (N = 30; df = 29; U = 97; P = 0.539) and psyllid nymphs (N = 30; df = 29; U = 107; P = 0.758) did not differ between treatments.
A total of 21 predators were observed in the inflorescences of 5. chapmanii. Predators included spiders (14), coccinellid beetles (4), and predatory wasps (3). The total number of predators observed did not differ significantly between treatments (N = 30; df = 29; U = 89.5; P = 0.3).
PRE-DISPERSAL SEED PREDATORS
Although evidence of pod-boring seed predators (i.e., frass and residue from predated seeds) was often observed, the herbivores themselves were only recovered on 4 occasions, 3 times from control plants, and once from plants with ants excluded. The pod borers observed belonged to 2 species: 1 coleopteran and 1 lepidopteran. The rate of seed predation did not differ between treatments (N = 30; df =29; U = 112.5; P= 1.0) (Fig. 1A).
A total of 14 pollinator visits were observed during 63 observations (15 h and 45 min). Ten of those visits (71%) were by the sweat bee, Augochlora pura Say (Hymenoptera: Halictidae). The remaining visits involved the honeybee, Apis mellifera L. (Hymenoptera: Apidae) (2), a metallic hoverfly, Ornidia obesa F. (Diptera: Syrphidae) (1), and a skipper butterfly, Euphyes arpa Boisduval & Le Conte (Lepidoptera: Hesperiidae) (1). Augochlora pura was the only visitor observed that is able to remove pollen from the poricidal anthers of S. chapmanii flowers. As such, analyses of pollinator visits took into account only this visitor.
Plants with ants present were visited by pollinators significantly more frequently than plants from which ants were excluded (Control N = 33, Tanglefoot[TM] N = 30; df = 62; U = 348; P = 0.003). The mean duration of pollinator visits was also significantly longer on plants with ants present (Control N = 33, TanglefootTM N = 30; df = 62; U = 346; P = 0.003) (Fig. 2). Pollination efficiency (number of fertilized ovules per total number of ovules produced), however, did not differ between plants with and without ants (N = 30; df = 29; U = 108; P = 0.818) (Fig. 1B). No correlation was seen between the number of active inflorescences on a given plant and the number of pollinator visits (N = 63; r = 0.253; P = 0.516) (Fig. 3).
A repeated measures ANOVA revealed that, within individual plants, the number of branches increased significantly over time (N = 30; [F.sub.7,196] = 3.66; P = 0.013). No significant interaction was observed between time and the presence or absence of ants (N = 30; [F.sub.7,196] = 0.91; P = 0.444). The presence of ants, however, significantly affected plant size (N = 30; [F.sub.1,28] = 4.99; P = 0.034). The mean number of branches on plants in the presence of ants (6.84) was higher than when ants were absent (3.12) (Fig. 4).
PLANT REPRODUCTIVE FITNESS
The number of ovules counted in dissected flowers ranged from 25 to 39, and the mean number of ovules per flower was 30 (SD = 2.962). Measures of gross reproductive fitness, such as number of inflorescences (N = 30; df = 29; U = 81; P = 0.187), flowers (N = 30; df = 29; U = 84.5; P = 0.244), mature fruit (N = 30; df = 29; U = 109.5; P = 0.878), and mature seeds (N = 30; df = 29; U = 106; P = 0.739) did not differ significantly between treatments (Fig. 5). Effective fecundity was not significantly different between treatment and control plants (N = 30; df = 29; U = 103; P = 0.627) (Fig. 1C).
EXTRAFLORAL NECTAR PRODUCTION
A repeated measures ANOVA revealed that, within individual plants, the production of EFN decreased significantly over time (N = 30; [F.sub.3,84] = 3.58; P = 0.028). No significant interaction was observed between time and the presence/absence of ants (N = 30; [F.sub.3,84] = 0.401; P = 0.700). The presence of ants had no effect on EFN production (N = 30; [F.sub.7,28]= 0.45; P = 0.509).
Ants have long been known to defend plants through the removal of herbivores, and this phenomenon has been seen on many plant species, including S. chapmanii (Bentley 1977; Rosumek et al. 2009; Heil 2015; Koptur et al. 2015; Jones et al. 2016). The application of Tanglefoot[TM] was effective in excluding ants from treatment plants for the duration of the experiment.
In the present study, we did not observe significant differences in measures of gross reproductive fitness (numbers of inflorescences, flowers, mature fruit, and seeds) between treatments, perhaps due to relatively low sample sizes. Previous studies have, however, shown Increased seed production in S. chapmanii plants with ants present, when compared with plants from which ants were excluded (Jones et al. 2016). Here, we focus greater attention on the effects of ants on Interactions between S. chapmanii and other insects that may affect Its reproductive fitness.
On control plants, ants were regularly seen patrolling flowers and developing fruit. Despite this, no difference was observed in the rate of seed predation between treatments. Although surprising, this result was not wholly unexpected. While several authors have observed Increased EFN production on and around developing fruit, in line with optimal defense theory (Holland et al. 2009; Falcao et al. 2014), few studies have shown ants to reduce pre-dispersal seed predation (but see Inouye & Taylor 1979; Schemske 1980). Lenoir and Pihlgren (2006) observed 10 species of ants attracted to EFNs of the Bush vetch, Vicia sepium L. (Fabaceae). Despite their numbers, ants had no effect on seed predation, which was predominantly mediated by the leaf beetle, Bruchus atomarius L. (Cleoptera: Atellabidae). Ruhren (2003) also observed no effects of ants on the specialist seed predator, Sennius cruentatus Horn (Coleoptera: Chrysomelidae), on Chamaecrista nictitans (L.) Moench (Fabaceae). In this case, the beetles may have evaded detection by living inside developing seed pods. Pod-boring seed predators may pose a particular problem for ant defended plants. In the common vetch, Vicia sativa L. (Fabaceae), seed damage by pod-boring tortricid moths has been shown to be greater in the presence of ants (Koptur & Lawton 1988). It was suggested that ants may even facilitate pod-boring herbivores by patrolling the fruit and deterring predators and parasitoids (Koptur & Lawton 1988).
In the present study, effective fecundity, defined as the proportion of ovules that survived to become mature seeds, did not differ between treatments. These results, along with our seed predation data and insect surveys, indicate that in the case of S. chapmanii, ants do not benefit plant fitness by increasing the survivorship of flowers or developing fruit.
The flowers of Senna species are buzz-pollinated by pollen collecting bees (Marazzi et al. 2015). Only 1 insect, the sweat bee (A pura), was observed to effectively remove pollen from the poricidal anthers of S. chapmanii flowers. Flower visits by this insect were significantly more frequent, and their duration significantly longer, on plants with ants present. This result was surprising, as aggressive ants more often have been seen to deter pollinators (Ness 2006; Assuncao et al. 2014; Ohm & Miller 2014), and pollinators have been observed to recognize the danger posed by ants (Hernandez-Cumplido et al. 2010; Assuncao et al. 2014). However, similar to our findings, another study (Holland et al. 2011) observed increased pollination rates in the presence of ants. Holland et al. (2011) excluded ants from senita cacti in the Sonoran Desert and observed a reduction in pollination rates in the absence of ants.
Although the number and duration of pollinator visits was higher in the presence of ants, pollination efficiency (defined as the proportion of ovules fertilized for each plant) did not differ between treatments. So the question remains, what drives increased pollinator visitation in the presence of ants, and how might this affect plant reproductive fitness? Throughout the course of the study, plant size increased rapidly in the presence of ants, and remained fairly constant in their absence. After 4 mo, plants with ants had significantly more growing stems than plants with ants excluded. These results suggest that by removing herbivores (Koptur et al. 2015) and reducing rates of leaf damage (Jones et al. 2016), ants on S. chapmanii facilitate increased plant growth. It is likely, therefore, that the observed increase in pollinator visits in the presence of ants simply reflected the larger size and increased floral displays of plants with ants. Oliveira (1997) observed higher pollination rates in Caryocar brasiliense A. St. -Hil. (Caryocaraceae) in the presence of ants and drew similar conclusions. Ants reduced herbivore damage to vegetative tissues, resulting in healthier plants that supported larger, more attractive floral displays (Oliveira 1997).
Extrafloral nectar measurements revealed a sharp decline in per leaf sugar production over the course of the study. These measurements were taken between Oct and May, and the same pattern was seen in plants of a similar age during previous field season, in which measurements were taken between Apr and Feb (Jones et al. 2016). These results suggest that the decline in EFN production representsan ontogenetic ratherthan a seasonal or phenological pattern, and that EFN may be most important for plant establishment and early growth in S. chapmanii.
Ants may benefit plant reproductive fitness in a number of ways. For example, by reducing herbivory rates (Janzen 1966; Bruna et al. 2004; Del-Claro et al. 2006) or herbivore numbers (Letourneau & Barbosa 1999), facilitating effective pollination (Oliveira 1997; Holland et al. 2011), protecting flowers or developing fruits (Wackers & Bonifay 2004; Holland et al. 2009), or even providing nutrient subsidies by nesting among plant roots (Wagner 1997; Wagner & Nicklent 2010). Conversely, plants that host ants may incur certain ecological costs. Aggressive ants have been known to deter beneficial insects such a pollinators (Ness 2006; Hernandez-Cumplido et al. 2010; Assuncao et al. 2014), predators (Torres-Hernandez et al. 2000; Nahas et al. 2012; Koptur et al. 2015), and parasitoids (Styrsky & Eubanks 2007; Rosumek et al. 2009). Some defensive ants are also known to cheat their mutualistic partners by removing reproductive structures to promote vegetative growth (Yu & Pierce 1998). In order for plants to benefit from their interactions with ants, the combined effects of these interconnected processes must be weighed in their favor.
The effects of ants on reproductive fitness in S. chapmanii appear inconsistent and are strongly influenced by ecological context (Jones et al. 2016), as is likely the case in many facultative antplant associations. The mechanisms by which ants effect plant reproductive fitness, however, appear relatively simple in this case. The presence of ants on plants, particularly during the months of establishment, contribute to enhanced plant size. The relative effects of ants on rates of pollination, fruit development, and seed predation appear minimal. Any differences in reproductive fitness in the presence of ants likely occur because plants are faster to establish, reach larger sizes, and can allocate more resources to reproductive traits.
Food-for-protection mutualisms between plants and ants have often been shown to enhance plant reproductive fitness (Rosumek et al. 2009). Understanding the intraguild and multitrophic interactions that underline these benefits may allow us to harness ant-plant interactions in agricultural settings where herbivore damage and the overuse of pesticides are worldwide concerns.
We thank 3 field assistants for their help with data collection, H. Gallegos, J. Tardanico, and P. Trainer. The authors also thank S. Zona for his generosity with greenhouse facilities. Help with insect specimen identification came from M. Deyrup and J. Clayborn. Constructive input on the manuscript was provided by J. Theobald and J. Richards. Financial support was provided in the form of 3 research grants from the Lloyd Kelly foundation for tropical botany. Statistical consultation was provided by A. Matamala.
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Ian M. Jones (1,*), Suzanne Koptur (2), and Jorge E. Pena (3)
(1) United States Department of Agriculture (USDA), Agricultural Research Service (ARS), Invasive Plant Research Laboratory, 3225 College Avenue, Fort Lauderdale, FL 33314, USA; E-mail: firstname.lastname@example.org (I. M. J.)
(2) Department of Biological Sciences, Florida International University, 11200 S.W. 8th Street, Miami, FL 33199, USA; E-mail: email@example.com (S. K.)
(3) Tropical Research and Education Center, University of Florida, Homestead FL 33031, USA; E-mail: firstname.lastname@example.org (J. E. P.)
(*) Corresponding author; E-mail: email@example.com (I. M. J.)
Caption: Fig. 1. A. Mean rates of pre-dispersal seed predation on Senna chapmanii plants with (Control) and without (TanglefootTM) ants. Seed predation was calculated for each plant as the number of herbivore damaged seeds divided by the total number of developing seeds (fertilized ovules minus aborted seeds); B. Mean pollinator efficiency on S. chapmanii plants with and without ants. Pollinator efficiency was measured as the proportion of ovules fertilized for each plant; C. Mean effective fecundity of S. chapmanii plants with and without ants. Effective fecundity was calculated for each plant as the number of non-predated mature seeds divided by the total number of ovules. In all 3 cases, comparisons were made between treatments using Mann-Whitney U tests, and results were deemed statistically significant if P values were [less than or equal to]0.05. Error bars represent standard error in all cases. No significant differences were observed between treatments.
Caption: Fig. 2. Mean number (A) and duration (B) of pollinator visits on Senna chapmanii plants with and without ants. In both cases, comparisons were made between treatments using Mann-Whitney U tests, and results were deemed statistically significant if P values were [less than or equal to]0.05. Error bars represent standard error. Asterisks indicate significant differences. In the axis label, no' refers to number.
Caption: Fig. 3. Correlation between the number of active inflorescences on Senna chapmanii plants at the time of observation and the number of pollinator visits. Circles represent the mean number of pollinator visits per observation on plants with different numbers of inflorescences. In the axis label, No' refers to number.
Caption: Fig. 4. Mean size of Senna chapmanii plants in the presence and absence of ants over the course of the 8 mo experiment. Plant size was estimated as the number of growing stems with 10 or more leaves.
Caption: Fig. 5. Reproductive fitness of Senna chapmanii plants with (Control) and without (Tanglefoot[TM]) ants. Bars represent the means of weekly measurements taken over the course of the 8 mo experiment. Error bars represent standard error. In the axis label, "no's." refers to numbers.
Please Note: Illustration(s) are not available due to copyright restrictions.
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|Author:||Jones, Ian M.; Koptur, Suzanne; Pena, Jorge E.|
|Date:||Sep 1, 2017|
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