Predators affect plant fitness when they forage on them and reduce the action of herbivores. Our study evaluates the complementary effects of spiders and ants that visit the extrafloral nectaries of Eriotheca gracilipes (Malvaceae) on the production of fruits and viable seeds of these savanna trees. Four experimental groups were established: control group – with free access of spiders and ants; exclusion group – spiders and ants excluded; ant group – absence of spiders; and spider group – absence of ants. The presence of ants reduced the spider richness; however, the presence of spiders did not affect the ant richness. A significantly higher number of fruits per buds were found in the presence of spiders alone or spiders and ants together (control group) compared with the absence of both predators (exclusion group). The number of seeds per fruits and seed viability were higher in the control group. This is the first study showing that spiders and ants may exert a positive and complementary effect on the reproductive value of an extrafloral nectaried plant. Mostly the impact of ants and/or spiders on herbivores is considered, whereas our study reinforces the importance of evaluating the effect of multiple predators simultaneously, exploring how the interactions among predators with distinct skills may affect the herbivores and the plants on which they forage.
Citation: Stefani V, Pires TL, Torezan-Silingardi HM, Del-Claro K (2015) Beneficial Effects of Ants and Spiders on the Reproductive Value of Eriotheca gracilipes (Malvaceae) in a Tropical Savanna. PLoS ONE 10(7): e0131843. https://doi.org/10.1371/journal.pone.0131843
Editor: Daniel Ballhorn, Portland State University, UNITED STATES
Received: January 12, 2015; Accepted: June 6, 2015; Published: July 13, 2015
Copyright: © 2015 Stefani et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited
Data Availability: All relevant data are available within the paper.
Funding: The authors (HMTS and KDC) had financial support of the Conselho Nacional de Desenvolvimento Científico e Tecnológico; CNPq – Grant numbers 473055/2012; 72046/2011; 301248/2009. VS thanks the Coordenação de Aperfeiçoamento de Pessoal de Nível Superior – Plano Nacional de Pós-Doutorado, CAPES-PNPD, number 2556/2011). The authors ensure that the funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
In terrestrial communities, multitrophic interactions comprise a minimum of three trophic levels that interact among each other: plants, herbivores and their natural enemies [1, 2]. The top-down forces exerted by invertebrate predators on herbivores and their cascading effect on plants are very important for the structuring of terrestrial communities [3, 4, 5]. Among major invertebrate predators, ants exert a strong impact on the density and spatial distribution of leaf and floral herbivores, which is reflected in the reproductive capacity of the plants [6, 7, 8]. This important effect has only recently also been attributed to spiders [9, 10, 11].
Studies of ant-plant-herbivore interactions have reported that the host plant may benefit from these relationships, depending on the behavior of the ant species associated with it and on the intensity and quality of the herbivore attack [12, 13]. For example, the action of ants against the main floral herbivore of the Brazilian savanna plant Qualea multiflora, the beetle Macrodactylus pumilio Burm. (Scarabaeidae), led to a 40% increase in this plant’s fruit production . Nascimento and Del-Claro  performed experimental manipulations under natural conditions and observed that the presence of ants that visit the extrafloral nectaries of Chamaecrista debilis (Fabaceae) increased its fruit production by more than 50% in relation to plants from which ants were excluded. The constant presence of ants in the vegetation is due mainly to the existence of different renewable sources of liquid food in the foliage, such as extrafloral nectaries , which effectively nourish the ants and allow for better ant colony development . Therefore, ants, herbivores and plants establish interaction networks that influence the structure of communities in tropical environments [18, 19]. These networks may be sustained over time as a function of the sequential flowering and budding of the host plants . The phenological synchronization between ants, herbivores and their host plants may determines the quantity and quality of food resources, including extrafloral nectar, directly impacting populations and communities [18, 20].
Studies of trophic interactions involving spiders and their impacts on the vegetation have increased considerably in the last few years. This is expected, considering that spiders are present in almost all terrestrial environments and occur in higher abundance in vegetation-rich areas . Regarded as excellent predators, spiders also use plants as foraging substrates, exploring differences in the plant architecture and in prey capture strategies, and may be categorized into different guilds [22, 23]. Furthermore, spiders commonly prey on insect herbivores, which can result in a great decrease in herbivory rates, benefiting the host plants [11, 24]. Ruhren and Handel  found that the presence of Salticidae spiders on Chamaecrista nictitans (Caesalpiniaceae) resulted in a higher number of fruits and seeds produced in comparison to plants without spiders. In contrast, the spider Peucetia viridans (Oxyopidae) preys on pollinators and seed herbivores of Haplopappus venetus (Asteraceae), generating ambiguous effects for the host plant. The negative effect was the low number of fertilized eggs reducing the number of seeds produced, the positive effect was the low number of seeds injured by herbivores . Nahas and co-workers  showed that, for a multitrophic system that involves the presence of ants and spiders simultaneously, these predators may have a significant complementary effect on the reduction of leaf area loss and the reduction of herbivore presence on the plants.
Tropical savannas, such as the Brazilian Cerrado, are rich in examples of plants visited simultaneously by spiders and ants; however, several aspects of these interactions are still poorly studied. The Cerrado is an ecosystem rich in plants with extrafloral nectaries and is the second largest Brazilian biome, although it is highly endangered by agricultural expansion and urban growth in the interior of the country . Plants with extrafloral nectaries or with herbivorous trophobionts in the Cerrado are commonly visited by ants that effectively reduce their leaf area loss [27, 28]. More recently, it has been shown that spiders of several families (e.g., Anyphaenidae, Salticidae, Araneidae, Theridiidae, Thomisidae, and Oxyopidae) are common in Cerrado plants  and may visit extrafloral nectaries and attack herbivores . Understanding the interactions that structure natural communities in the Cerrado is important because the simultaneous interaction of several species provides a connection among the studies of the natural history of these species, allowing studies of the community and of ecosystem patterns and processes [30, 31, 32].
The hypothesis of the present study was that ants and spiders increase the reproductive value of plants with extrafloral nectaries in the Cerrado and that they may have an isolated or a complementary effect. Eriotheca gracilipes (Malvaceae) trees, a species with extrafloral nectaries on its leaf blades that is abundant in Cerrado areas, was used as a model. To test our hypothesis, we addressed four main questions: (a) Is the species richness of spiders or ants affected by the co-occurrence of these predators on host plants? (b) What are the main guilds of spiders and ants species that occur on these extrafloral nectaried plants? (c) Do ants and/or spiders exert a positive impact on plant reproduction? (d) Are the outcomes of these predator-plant relationships dependent on the co-occurrence of ants and spiders in the same host plants, or it does not matter?
Materials and Methods
Field observations and experiments were performed from April to September 2012 in a Private Reserve of Natural Heritage (Reserva Particular do Patrimônio Natural–RPPN) (18°58’00” S and 48°17’30” W) belonging to the Itororó Hunting and Fishing Club of Uberlândia, located in the municipality of Uberlândia, in the state of Minas Gerais, Brazil. The Biology Institute of Universidade Federal de Uberlândia has a memorandum of understanding with CCPIU (Itororó Hunting and Fishing Club of Uberlândia), an agreement between Mr. Nilson Dias, head of CCPIU, and Dr. Kleber Del Claro, director of Biology Institute that enables ecological studies in the area. The field studies did not involve endangered or protected species. The climate of the region presents a dry season from May to September and a rainy season from October to April. The mean annual temperature is 22°C, and the total rainfall is 1500 mm per year. The predominant vegetation in the area is cerrado sensu stricto (see  for a better characterization of the area).
Eriotheca gracilipes (Malvaceae) is a tree species that may reach up to 15 m in height in Cerrado areas and occurs more commonly in Cerrado areas in the southeast of Brazil [34, 35]. This species flowers from May to August; the flowers are receptive for two or three days and are self-incompatible and thus dependent on large bees (Anthophoridae) for pollination . This species possesses extrafloral nectaries at the base of the petiole, in the veins at the abaxial region of the blade of young leaves  and at the base of the corolla of the flowers, extending their activity until the formation of the fruit.
In April 2012, 60 E. gracilipes individuals were selected at a similar phenological state, at a height of between 1 and 2.5 meters, and were distant at least five meters from one another. These individuals were randomly divided into four groups of 15 individuals. After the random draw that separated the individuals, each group received a name and treatment. The control group was not manipulated. The remaining groups were subjected to the following experimental manipulations: exclusion group–removal of both spiders and ants from the plants; ant group–removal of spiders from the plants; and spider group–removal of ants from the plants.
Ants were excluded (exclusion group and spider group) manually, and after the removal, we covered the trunks with a 5 cm large adhesive paper strap and applied a layer of sticky resin over it (Tanglefoot) on the trunk of the plant 30 cm from the soil. This resin acts as a physical barrier preventing ant access to the plants. The branches of plants in the vicinity and any other structures from the environment that could act as a passage for ants were cut.
Spiders were excluded (exclusion group and ant group) by manual removal of all individuals every three days. This time interval was established during the pre-experimental phase (before the reproductive period of the plants), when spiders were removed from five host plants and their reestablishment was inspected for a period of five days, following the method of . The recolonization during the experiment was low, and the mean number of spiders in the plants was lower during the following five days than on the first day of the experiment (Fig 1).
Recolonization by spiders (mean ± standard error) removed from Eriotheca gracilipes plants (N = 5) over a period of five days in a removal experiment.
The individuals trees were inspected (12 days per month, once each three days), marked and monitored from the appearance of floral buds (May) until the formation of fruit (September). The number of seeds per fruit was counted, and the viability of all seeds in each experimental group was evaluated. The spider guilds, ant species, flower bud herbivores, flower herbivores and fruit herbivores were also recorded for each host plant. The spiders were divided into four guilds, according to [38, 39]: trappers (e.g., Araneidae, Theridiidae), jumpers (e.g., Salticidae and Oxyopidae), ambushers (e.g., Ctenidae, Thomisidae), and pursuers (e.g., Anyphaenidae).
Seed viability test
We checked whether the absence and/or presence of spiders and ants influence the quantity and quality of seeds, performing a viability test. As the seeds of E. gracilipes are considered recalcitrant was used the tetrazolium test. This test is based on the alteration of enzyme activities and has been shown to be a good choice because of the speed in the determination of the viability and vigor of the seeds [40, 41, 42]. The tetrazolium test distinguishes between viable and dead tissues of the embryo on the basis of their relative respiration rate in the hydrated state . In short, dehydrogenase enzymes react with substrates and release hydrogen ions to the oxidized, colorless, tetrazolium salt solution, which is changed into the red. This makes it possible to distinguish live parts, colored red, those dead ones [40, 41, 42].
When the E. gracilipes fruits began to crack, they were collected, counted and left to dry for 24 hours until they were completely open. The fruits were tagged according to manipulation of the host plant and the seeds were then counted and later immersed for staining in a solution of approximately 0.5% 2,3,5-triphenyltetrazolium chloride for 24 hours in the dark at 35°C. After this period, the seeds were analyzed individually by opening them longitudinally with a surgical blade, observing the external and internal faces between the cotyledons, and verifying the appearance of light carmine red coloration (indicating the viability of the seed) or white coloration (indicating the inviability of the seed) (see [40, 41, 42]).
The assumptions of the parametric test were tested using Levene’s test for equality of variances and Lilliefors’ test for normality. In those cases where data did not satisfy the assumptions of a normal distribution (p < 0.05) and transformations were unable to achieve data normality, non-parametric statistical tests were used. Student’s t-test was used to compare the ant richness in the presence and absence of spiders, as well as the spider richness in the presence and absence of ants. To determine the effect of ants and spiders (together or separately) on plant productivity (numbers of fruits formed per floral buds produced; seeds per fruits; and viable seeds) in each experimental group was used the Kruskal-Wallis test with a post-hoc Dunn (Q) test.
The abundance of the families of herbivores present and their proportions during the different stages of the reproductive development of E. gracilipes (flower buds, flowers and fruits) were quantified in each experimental group. To know whether presence or absence of ants and spiders (together or separately) affected herbivores abundance during the plant reproductive period, the number of herbivores in each experimental group was quantified in buds, flowers and fruits, since the formation of first buds until the time of seeds viability tests. We also used Kruskal-Wallis test with post-hoc Dunn (Q) test to compare the groups.
Were observed nine species of ants patrolling the host plant E. gracilipes (Fig 2A). The ant richness did not vary significantly between plants with spiders and plants without spiders (t = -0.198, df = 28, p = 0.84; Fig 2B). Some species, however, were found in higher proportion in plants without spiders (Ectatomma edentatum, Cephalotes pusillus, Camponotus sp., Camponotus crassus and Brachymyrmex sp.) (Fig 2A).
(a) Proportion of different ant species in plants with (control group) and without spiders (ant group), b) Ants richness in plants with (control group) and without spiders (ant group); richness refers to the number of species per tree.
A total of 17 morphospecies (from seven different families) of spiders was found in the E. gracilipes plants. The guild with the highest number of species represented was jumpers (Salticidae N = 6; Oxyopidae, N = 2), followed by trappers (Araneidae, N = 3; Theridiidae, N = 2), ambushers (Ctenidae, N = 1; Thomisidae, N = 2), and pursuers (Anyphaenidae, N = 1). The proportions of spiders belonging to the guilds jumpers, pursuers and ambushers were higher in plants without ants, whereas only the guild trappers showed a higher proportion in plants with ants (Fig 3A). The spider richness was significantly higher in plants without ants (t = -5.06, P = 0.001, df = 28; Fig 3B).
(a) Spiders richness and the proportion of different spider guilds in plants with (control group) and without ants (spider group); (b) spider richness in plants with (control group) and without ants (spider group), richness refers to the number of species per tree. ** indicate significant different—Student's t-test.
The fruit set formed per floral buds produced was different among groups (H = 11.17; p = 0.011). Trees occupied only by spiders presented higher fruit production, followed by control, ant and exclusion groups, respectively (Fig 4A; Table 1). The production of seeds per fruits was also different among groups (H = 7.41; p = 0.059). However, the paired analysis showed a significant difference only between control and exclusion groups (Fig 4B; Table 1). Also the number of viable seeds was different among groups (H = 8.96; p = 0.03, Fig 4C), and again the most significant difference was between exclusion and control groups (Fig 4C; Table 1).
Number of fruits per buds produced (a), number of seed per fruits produced (b) and number of viable seeds (c) in the group ‘Control’—with both predators, ‘Exclusion’–without predators, ‘Ant’–with spiders removed, and ‘Spiders’–with ants removed. Means + 1SE are presented. Different letters over bars point to statistical significant difference (Kruskal-Wallis test, with post-hoc Dunn test; see Table 1).
We found a higher abundance of herbivores in the exclusion and spider groups for all the reproductive phases of E. gracilipes. In the exclusion group, the most abundant families of herbivores in the flower buds were Proscopiidae, Acrididae and Gryllidae; whereas Gryllidae and Chrysomelidae were most abundant in the flowers. Curculionidae were the most abundant in the fruits. The ant and control groups showed a lower abundance of herbivores. In the fruiting phase, the lowest abundance of herbivores was in control group (Table 2). The total number of herbivores was significant different among groups (H = 14.11; p = 0.0028). However, the paired analysis (Table 2) showed significant differences only between the groups: control and exclusion (Q = 21; p<0.05); ants and exclusion (Q = 18.57;p<0.05); and spiders and exclusion (Q = 8.96;p<0.05).
The hypothesis that spiders and ants exert a positive and complementary effect on the reproduction of E. gracilipes was confirmed. The beneficial and complementary effects occurred mainly when both spiders and ants were present, leading to an increase in the number of fruits per buds, seeds per fruits and, particularly, in the vitality of the seeds. Therefore, the complementarity of the ecological services provided by different predators, which possess different abilities and cognitive and predatory capacities, may result in a direct benefit to the adaptive value of the host plant. A similar pattern has been reported for wasps that visit extrafloral nectaries (e.g. [8, 43, 44]). The importance of these complementary effects was also confirmed by the significant reduction in the number of herbivores in plants visited by both, ants and spiders. However, the results of these interactions may still be ambiguous, as shown by Nahas and co-workers , who did not find a significant positive impact when ants and spiders acted together or separately in the reproduction of Q. multiflora (Vochysiaceae); rather, showed a complement impact of spiders and ants on herbivory of the vegetative structures of the plant. Conversely, Ruhren and Handel  reported that, in the Chamaecrista nictitans (Fabaceae) shrub, spiders of the family Salticidae chose plants with active extrafloral nectaries to house them. These authors also observed these spiders feeding on nectar. In our study more fruits where formed in plants visited by ants and spiders simultaneously. However, plants visited only by spiders also produced more fruits than plants visited only by ants. Assunção and co-workers  showed that in ants may repel pollinators and reduce fruit formation in plants of Brazilian savanna.
The role of generalist predators, such as spiders and ants, using the same foraging substrate, may result in competition for prey, and these predators may attack one another. We observed that the spider richness in the absence of ants was significantly higher, whereas the ant richness in the absence of spiders did not vary significantly. This difference in our results may be attributed to the composition of distinct species of both ants and spiders and, consequently, to the different types of interactions among them. Nahas and co-workers  found that the ant abundance and richness were similar in the presence and absence of spiders; however, the spider abundance and richness were lower, although not significantly, in plants visited by ants. Sanders and co-workers  reported a 90% decrease in the density of ants in the presence of web-building spiders, a 50% decrease in the density of herbivores in the presence of web-building spiders or hunter spiders, and a 60% decrease when both groups of spiders were present. Hunter spiders (jumpers, ambushers and pursuers) were found in higher proportions in plants without ants. This result must be associated with the behavior of these spiders, which move constantly through the vegetation, using it directly for foraging and also for shelter and reproduction. Such movement increases their encounters with ants. Opposite, web-building spiders (trappers), which were found in a higher proportion in plants with ants, are usually inaccessible to ants.
Predators affect herbivores directly, due predation, or indirectly, reducing access to food sources for example . Distinct predators represent different hunting strategies, and in the system studied the diversity of both ants and spiders in E. gracilipes trees was great. Thus, their action simultaneously and separately, can be one of the main explanations for the reduction of the number of herbivores, which resulted in high values for the viability of the E. gracilipes seeds. Rosa  observed that the leaf area consumed on Hirtella myrmecophila (Chrysobalanaceae) was consistently larger in the leaves on which Dipoena bryantae (Araneae) spiders were present. This suggests that the presence of the spider negatively affects the behavior of the ant Allomerus octoarticulatus (Myrmicinae), reducing its efficiency in defending the plant. Another study of the Amazonian myrmecophyte species Maieta poeppigii (Melastomataceae) demonstrated that after an herbivory event, the number of ants present in the leaves increases in response to the presence of herbivores and volatile compounds that are released from the damaged leaf . Similarly, spiders can sense volatile compounds and are attracted to the leaves with a higher concentration of ants. In fact, some studies have demonstrated that the release of volatile compounds induced by the consumption of leaves attracts predators of herbivores [50, 51]. According to Nelson and Jackson , juveniles of the spider Evarcha culicivora (Salticidae), which feed on nectar, are attracted by the release of phytochemical compounds of the host plant Lantana camara (Verbenaceae), such as β-caryophyllene and α-humulene, highlighting strategies promoted by host plants to attract potential predators of its herbivores. In the adult phase, E. culicivora does not feed on nectar but rather on insects, also using the plant as a mating site.
The result of the joint action of spiders and ants, however, varies according to their synergistic and antagonistic frequencies . In our study, the proportion of the reduction in the number of herbivores was more significant when ants and spiders were present together, reflecting positively on the plant’s reproduction. Therefore, spiders and ants are active at the third trophic level and may indirectly affect the reproductive value (number of seeds and their viability) and, consequently, the fitness of the plants they visit.
Conceived and designed the experiments: VS HMTS KDC. Performed the experiments: VS TLP. Analyzed the data: VS HMTS KDC. Contributed reagents/materials/analysis tools: VS HMTS KDC. Wrote the paper: VS HMTS KDC.
- 1. Price PW, Bouton CE, Gross P, Mcpheron BA, Thompson JN, Weis AE (1980) Interactions among three trophic levels: influence of plants on interactions between insect herbivores and natural enemies. Annu Rev Ecol Syst 11: 41–65.
- 2. Halaj J, Wise DH (2001) Terrestrial trophic cascades: how much do they trickle? Am Nat 157: 262–281. DOI: 0003-0147/2001/15703-0002$03.00 pmid:18707289
- 3. Sanders D, Nickel H, Ghutzner T, Platner C (2008) Habitat structure mediates top-down effects of spiders and ants on herbivore. Basic Appl Ecol 9: 152–160.
- 4. Price PW, Denno RF, Eubanks MD, Finke DE, Kaplan I (2011) Insect ecology: behavior, populations and communities. Cambridge University Press, Cambridge. 801 p.
- 5. Terborgh J, Estes JA (2010) Trophic Cascades: Predators, Prey, and the Changing Dynamics of Nature. Island Press, Washington. 488 p.
- 6. Thomas CD (1989) Predator–herbivore interactions and the escape of isolated plants from phytophagous insects. Oikos 55: 291–298
- 7. Rosumek FB, Silveira FAO, Neves FS, Barbosa NPU, Diniz L, Oki Y, et al. (2009) Ants on plants: a meta-analysis of the role of ants as plant biotic defenses. Oecologia 160:537–549. pmid:19271242
- 8. Alves-Silva E, Del-Claro K (2013) Effect of post-fire resprouting on leaf fluctuating asymmetry, extrafloral nectar quality, and ant–plant–herbivore interactions. Naturwissenschaften 100: 525–532.
- 9. Romero GQ, Vasconcellos-Neto J (2004) Beneficial effects of flower-dwelling predators on their host plant. Ecology 85:446–457. http://dx.doi.org/10.1890/02-0327
- 10. Gonçalves-Souza T, Omena PM, Souza JC, Romero GQ (2008) Trait mediated effects on flowers: artificial spiders deceive pollinators and decrease plant fitness. Ecology 89: 2407–2413. DOI: org/10.1890/07-1881.1 pmid:18831161
- 11. Nahas L, Gonzaga MO, Del-Claro K (2012) Emergent impacts of ant and spider interactions: herbivory reduction in a tropical savanna tree. Biotropica 44: 498–505.
- 12. Heil M, Mckey D (2003) Protective ant–plant interactions as model systems in ecological and evolutionary research. Annu Rev Ecol Evol Syst 34: 425–453.
- 13. Del-Claro K, Guillermo-Ferreira R, Zardini H, Almeida EM, Torezan-Silingardi HM (2013) Ants Visiting the Post-Floral Secretions of Pericarpial Nectaries in Palicourea rigida (Rubiaceae) Provide Protection Against Leaf Herbivores But Not Against Seed Parasites. Sociobiology 60: 217–221.
- 14. Del-Claro K, Berto V, Réu W (1996) Effect of herbivore deterrence by ants on the fruit set of an extrafloral nectary plant, Qualea multiflora (Vochysiaceae). J Trop Ecol 12: 887–892. http://dx.doi.org/10.1017/S0266467400010142
- 15. Nascimento EA, Del-Claro K (2010) Ant visitation to extrafloral nectaries decreases herbivory and increases fruit set in Chamaecrista debilis (Fabaceae) in a Neotropical savanna. Flora 205: 754–756.
- 16. Davidson DW, Cook SC, Snelling RR, Chua TH (2003) Explaining the abundance of ants in lowland tropical rainforest canopies. Science 300: 969–972. pmid:12738862
- 17. Byk J, Del-Claro K (2011) Ant–plant interaction in the Neotropical savanna: Direct beneficial effects of extrafloral nectar on ant colony fitness. Popul Ecol 53:327–332.
- 18. Lange D, Datillo W, Del-Claro K (2013) Influence of extraforal nectary phenology on ant–plant mutualistic networks in a neotropical savanna. Ecol Entomol 38: 463–469.
- 19. Dáttilo W, Fagundes R, Gurka CAQ, Silva MSA, Vieira MCL, et al. (2014) Individual-Based Ant-Plant Networks: Diurnal-Nocturnal Structure and Species-Area Relationship. Plos One 9(6): e99838. pmid:24918750
- 20. Vilela AA, Torezan-Silingardi HM, Del-Claro K (2014) Conditional outcomes in ant-plant-herbivore interactions influenced by sequential ﬂowering. Flora 209: 359–366.
- 21. Foelix RF (2010) Biology of spiders. Oxford University Press, Oxford. 428 p.
- 22. Souza ALT, Módena ES (2004) Distribution of spiders on different types of inflorescences in the Brazilian Pantanal. J Arachnology 32: 345–348. http://dx.doi.org/10.1636/M02-38
- 23. Diniz S, Tizo-Pedroso E, Lange D, Vilela AA, Stefani V, et al. (2012) Might heterostyly underlie occurrence on inflorescence? A case study of Palicourea rigida (Rubiaceae) a common shrub from brazilian cerrado. Psyche. https://doi.org/10.1155/2012/791395
- 24. Romero GQ, Vasconcellos-Neto J (2007) Interações bióticas entre plantas, herbívoros e aranhas. In: Gonzaga MO, Santos AJ, Japyassú HF, editors. Ecologia e comportamento de aranhas. Interciência, Rio de Janeiro, Brazil. pp. 277–300.
- 25. Louda SM (1982) Inflorescence spiders: a cost/benefit analysis for the host plant, Haplopappus venetus Blake (Asteraceae). Oecologia 55: 185–191.
- 26. Oliveira PS, Marquis RJ (2002) The cerrados of Brazil: ecology and natural history of a neotropical savanna. Columbia University Press, New York. 398 p.
- 27. Stefani V, Del-Claro (2005) The outcomes of na Ant-Treehopper association on Solanum Lycocarpum St. Hill: Increased Membracid fecundity and reduced damage by chewing herbivores. Neot Entom 34: 881–887.
- 28. Del-Claro K, Torezan-Silingardi HM (2009) Insect-plant Interactions: New Pathways to a better comprehension of ecological communities in neotropical savannas. Neot Entom 38: 159–164.
- 29. Souza ALT, Martins RP (2005) Foliage density of branches and distribution of plant-dwelling spiders. Biotropica 37: 416–420.
- 30. Thompson JN (1997) Conserving interaction biodiversity. In: Pickett STA, Ostfeld RS, Shachak M, Likens GE, editors. The ecological basis of conservation: Heterogeneity, ecosystems, and biodiversity, Chapman and Hall, New York. pp. 285–293.
- 31. Thompson JN (2005) The geographic mosaic of coevolution. University of Chicago Press, Chicago. 428 p.
- 32. Bronstein JL (2009) The evolution of facilitation and mutualism. J Ecol 97: 1160–1170.
- 33. Ferreira CA, Torezan-Silingardi HM (2013) Effects of floral herbivory on reproductive success in species of the genus Banisteriopsis (Malpighiaceae) in the Brazilian cerrado. Sociobiology 60: 323–328.
- 34. Silberbauer-Gottsberger I, Etten G (1987) A hectare of Cerrado. I. General aspects of the trees and thick-stemmed shrubs. Phyton (Austria) 27: 55–91
- 35. Durigan G, Nishikawa DLL, Rocha E, Silveira ER, Pulitano FM, Regalado LB, et al. (2002) Caracterização de dois estratos da vegetação em uma área de cerrado no município de Brotas, SP, Brasil. Acta Bot Bras 16: 251–262
- 36. Oliveria PE, Gibbs PE, Barbosa AA, Talavera S (1992) Constrasting breeding systems in two Eriotheca (Bombacaceae) species of the Brazilian cerrados. Plan Syst Evol 179: 207–219.
- 37. Machado SR, Morellato LPC, Sajo MG, Oliveira PS (2008) Morphological patterns of extrafloral nectaries in woody plant species of the brazilian cerrado. Plant Biol 10: 660–673. pmid:18761504
- 38. Heikkinen MW, Macmahon JA (2004) Assemblages of spiders on models of semi-arid shrubs. J Arachnol 32: 313–323. http://dx.doi.org/10.1636/M02-1
- 39. Höfer H, Brescovit AD (2001) Species and guild structure of a Neotropical spider assemblage (Araneae) from Reserva Ducke, Amazonas, Brazil. Andrias 15: 99–119.
- 40. Delouche JC, Still TW, Raspet M, Lienhard M (1976) O teste de tetrazólio para viabilidade da semente. Brasília: AGIPLAN, Brazil. 103 p.
- 41. França Neto JB, Pereira LAG, Costa NP, Krzyzanowski FC, Henning AA (1988) Metodologia do teste de tetrazólio em sementes de soja. Londrina: EMBRAPA-CNPSo, Brazil. 60 p.
- 42. Costa NP, Marcos Filho J (1994) O emprego do teste de tetrazólio na avaliação da qualidade da semente de soja. Informativo ABRATES 4: 53–62.
- 43. Torres-Hernández L, Rico-Gray V, Castillo-Guevara C, Vergara JÁ (2000) Effect of nectar-foraging ants and wasps on the reproductive fitness of Turnera ulmiflora (Turneraceae) in a costal sand dune in Mexico. Acta Zoologica Mexicana 81: 13–21
- 44. Torezan-Silingardi HM (2011) Predatory behavior of Pachodynerus brevithorax (Hymenoptera: Vespidae, Eumeninae) on endophytic herbivore beetles in the Brazilian tropical savanna. Sociobiology 57: 181–189
- 45. Ruhren S, Handel SN (1999) Jumping spiders (Salticidae) enhance the seed production of a plant with extrafloral nectaries. Oecologia 119:227–230.
- 46. Assunção MA, Torezan-Silingardi HM, Del-Claro K (2014) Do ant visitors to extrafloral nectaries of plants repel pollinators and cause an indirect cost of mutualism? Flora 209: 244–249.
- 47. Sanders D, Schaefer M, Platner C, Griffiths GJK (2011) Intraguild interactions among generalist predator functional groups drive impact on herbivore and decomposer prey. Oikos 120:418–426.
- 48. Rosa C (2008) Um estranho no ninho: efeito indireto da presença da aranha mirmecófaga Dipoena bryantae (Aranae: Theridiidae) no aumento da herbivoria em Hirtella myrmecophila (Chrysobalanaceae). In: Machado G, Camargo JLC, editors. Livro do curso de campo Ecologia da Floresta Amazônica PDBFF/INPA, Manaus.
- 49. Christianini AV, Machado G (2004) Induced biotic responses to herbivory and associated cues in the Amazonian ant-plant Maieta Poepigii. Entomol Exp Appl 112: 81–88.
- 50. Dicke M, Sabelis MW, Takabayashi J, Bruin J, Posthumus MA (1990) Plant strategies of manipulating predator-prey interactions through allelochemicals: prospects for application in pest control. J Chem Ecol 16: 3091–3118. pmid:24263298
- 51. Turlings TCJ, Tumlinson JH, Lewis WJ (1990) Exploitation of herbivore-induced plant odors by host-seeking parasitic wasps. Science 250: 1251–1253. pmid:17829213
- 52. Nelson JX, Jackson RR (2013) Hunger-driven response by a nectar-eating jumping spider to specific phytochemicals. Chemoecology, 23: 149–153.
- 53. Schmitz OJ (2007) Predator diversity and trophic interactions. Ecology 88: 2415–2426. http://dx.doi.org/10.1890/06-0937.1 pmid:18027743