Tank bromeliads are good models for understanding how climate change may affect biotic associations. We studied the relationships between spiders, the epiphytic tank bromeliad, Aechmea bracteata, and its associated ants in an inundated forest in Quintana Roo, Mexico, during a drought period while, exceptionally, this forest was dry and then during the flooding that followed. We compared spider abundance and diversity between ‘Aechmea-areas’ and ‘control-areas’ of the same surface area. We recorded six spider families: the Dipluridae, Ctenidae, Salticidae, Araneidae, Tetragnathidae and Linyphiidae among which the funnel-web tarantula, Ischnothele caudata, the only Dipluridae noted, was the most abundant. During the drought period, the spiders were more numerous in the Aechmea-areas than in the control-areas, but they were not obligatorily associated with the Aechmea. During the subsequent flooding, the spiders were concentrated in the A. bracteata patches, particularly those sheltering an ant colony. Also, a kind of specificity existed between certain spider taxa and ant species, but varied between the drought period and subsequent flooding. We conclude that climatic events modulate the relationship between A. bracteata patches and their associated fauna. Tank bromeliads, previously considered only for their ecological importance in supplying food and water during drought, may also be considered refuges for spiders during flooding. More generally, tank bromeliads have an important role in preserving non-specialized fauna in inundated forests.
Citation: Hénaut Y, Corbara B, Pélozuelo L, Azémar F, Céréghino R, Herault B, et al. (2014) A Tank Bromeliad Favors Spider Presence in a Neotropical Inundated Forest. PLoS ONE 9(12): e114592. https://doi.org/10.1371/journal.pone.0114592
Editor: Ulrike G. Munderloh, University of Minnesota, United States of America
Received: June 30, 2014; Accepted: November 10, 2014; Published: December 10, 2014
Copyright: © 2014 Hénaut 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: The authors confirm that all data underlying the findings are fully available without restriction. All the data files are available from the database: (http://figshare.com/articles/Data_set_Plos_One_Spiders_bromeliads_and_ants/1209586).
Funding: All the financial support for this study was provided by the French Agence Nationale pour la Recherche (RAINWEBS ANR-12-BSV7-0022-01) and internal fund of El Colegio de la Frontera Sur (ECOSUR). 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.
Confronted with global warming, species may survive if their climate envelopes are wide enough to buffer new environmental conditions or if they are capable of moving to more suitable areas. For instance, in high latitude regions, sedentary animal species respond by the slow, poleward shift of their ranges , . In tropical areas, animal species are mostly affected by major changes in precipitation related to El Niño and La Niña episodes  and can eventually adapt to their new conditions by moving to a different microhabitat (physiological adaptations and microevolution, if any, occur over much larger time scales). Since 1976, there has been an increase in the frequency and intensity of El Niño and La Niña episodes related to global warming . These episodes correspond to sea-surface temperature anomalies across the tropical Pacific Ocean which impact the atmospheric circulation worldwide, causing environmental changes with opposing effects . In the Yucatan Peninsula, this phenomenon will be amplified in the future because this area is one of the most responsive tropical regions to changes in global climate; there, decreases in precipitation during La Niña episodes result in severe droughts .
In this context of climate change and intensification of drought events, inundated forests constitute relevant systems for understanding how species can adapt to recurrent drought by modifying their utilization of the various habitats found in this environment. More specifically, we studied spider distribution in an inundated forest in southern Quintana Roo, Mexico in May 2011 after a La Niña episode while, exceptionally, the ground was dry, and then in January 2012 when the forest was again flooded.
The inundated forests of Quintana Roo are characterized by an abundance of orchid and bromeliad epiphytes, including the large tank bromeliad, Aechmea bracteata. Indeed, tank bromeliads provide habitat, food and water to numerous aquatic and terrestrial organisms (e.g., microbes, algae and various animals such as spiders, crustaceans, insects, mollusks, amphibians, reptiles and mammals) –. Furthermore, they are interesting models for studying biotic interactions because they form spatially discrete and highly replicated micro-ecosystems . For instance, A. bracteata provides ants with a nesting place and, in turn, obtains protection from defoliators and likely nutriments from the ants’ refuse (myrmecotrophy) . On the other hand, spiders, including the Ctenidae, Theraphosidae and Salticidae, can be associated with bromeliads because the plant’s humid micro-climate helps them to avoid desiccation, while providing an adequate reproduction site and a good foraging area with abundant prey –. Also, certain spider species select specific rosette and leaf characteristics –. Note that spiders and certain ant species are generalist predators competing for the same resources and can also prey on one another . Indeed, ants have frequently been observed preying on spiders, including web-weaving spiders –. Whereas the majority of web-weaving spiders discard the ants that fall onto their web, some Nephila learn how to manipulate and capture the ants , . Among the non-web-weaving spiders, some species from the families Ctenidae and Thomisidae occasionally prey on ants , whereas specialization in ant predation has been noted in the Zodariidae and Salticidae –.
We specifically addressed the following questions. (1) Do A. bracteata bromeliads play a role in spider distribution in a context of a marked dry/wet succession in an inundated forest? (2) Do ants associated with A. bracteata impact spider presence?
Materials and Methods
This study was conducted according to relevant national and international guidelines. Permit #FAUT-0241 granted to Dr Yann Hénaut, issued by the Secretaría de Medio Ambiente y Recursos Naturales (SEMARNAT), according to the Norma Oficial Mexicana (NOM-126-ECOL-2000).
This study was conducted in an inundated forest dominated by 10-m-tall Metopium brownei (Anacardiaceae) situated in southern Quintana Roo, Mexico (1.5 km from the Mayan ruins at Kohunlich; 54 km from Chetumal; 18.426725° N; 88.804360° W; 120 meters a.s.l). The mean temperature varies from 25.5 to 26.5°C. The dry season lasts from February to May and the rainy season from June to January. Hurricanes commonly occur in this area between May and December, and particularly in September.
Aechmea bracteata is a large tank bromeliad (leaves ca. 1-m-long; inflorescences up to 1.7-m-long) found from Mexico to northern Colombia, from sea level to 1000 m. a.s.l . Each plant is constituted of a group of shoots at different stages of maturity that develop from a rhizome . As the rhizome grows, each shoot goes through the same stages, from the formation of the bud, which gives rise to a new shoot, up to the development of the inflorescence. Each shoot forms a rosette with numerous reservoirs (phytotelmata) where an abundant aquatic fauna develops. In the heart of the rosette, around the inflorescence, a central watertight cavity delimited by an amphora-shaped leaf is very often occupied by large ant colonies, mostly Neoponera villosa (Ponerinae) (until recently known as Pachycondyla villosa ) and Dolichoderus bispinosus (Dolichoderinae). When the ramet dries out and begins to rot, it becomes a refuge for ground-dwelling animals. Each plant therefore constitutes a complex ecosystem with its associated aquatic and terrestrial fauna .
We monitored 49 A. bracteata in May 2011 at the end of a pronounced drought where the forest floor had been dry for ca. 8 months and in January 2012 after heavy rains flooded the forest floor with 10–40 cm of water (see Fig. 1). Unfortunately, in the interim, heavy winds had caused some of the trees bearing A. bracteata to fall, explaining why the values are lower than 49 in January 2012.
The vertical arrows indicate the collection dates. The horizontal arrows indicate the periods of drought and flooding. The name and category of climatic events are added alongside the corresponding bars.
In May 2011, while monitoring the 49 A. bracteata, we counted the number of shoots interconnected by a rhizome indicative of an individual (see ), measured their size (height and width), the height at which they were located on their host tree and noted what ant species they sheltered. Furthermore, we delimited a circle with a radius of 2 m around the base of each tree bearing an A. bracteata. To these “Aechmea-areas” corresponded “control-areas” of the same surface area situated ∼10 m further with, at their centers, a similar tree (same trunk diameter and inclination) but not bearing an A. bracteata. Due to the homogeneity of this forest, the two kinds of areas present the same ecological characters and are under the same climatic conditions.
During both the dry and the flooded periods, we carefully inspected all the Aechmea- and control-areas (on the ground and on the trees situated at the centers of these areas in May 2011 and on the trees only in January 2012) to look for spider presence. In the Aechmea-areas, we also noted if the spiders were in contact or not with the A. bracteata (i.e., crawling on them or their webs connected to the plant foliage).
The spiders were identified to the genus or species levels whenever possible. Yet, because individuals of the orb-weaving spiders were juveniles, their identification was based on their web architecture (i.e., vertical orb-web for the Araneidae, horizontal orb-webs for the Tetragnathidae and sheet-webs for the Linyphiidae). In May 2011, we did not collect the spiders so as not to disturb their community, whereas we collected voucher specimens for identification in January 2012.
We were basically interested in the differences in the number of spiders between Aechmea- and control-areas during the dry and the flooded periods. Because our experimental design uses only count variables with discrete, positive values, we modeled them with a Poisson distribution, and because the same A. bracteata were sampled twice (dry and flooded periods), we used the sampling units as a random factor in a generalized linear mixed-effects model. We firstly tested the effects of flooding and Aechmea and then the effects of flooding and contact with Aechmea (fixed effects in both cases) on the number of spiders (R v. 2.14.2 software; R Development Core Team ).
The Wilcoxon Matched Pairs test was used to compare spiders that live in direct contact with the A. bracteata foliage vs. orb-weavers and the impact of ants on spider presence.
Impact of Aechmea bracteata presence and flooding on spider distribution
Aechmea presence has a significant positive effect on the number of spiders, the contrary being true for flooding (Table 1A), and Aechmea-areas harbored significantly more spiders than expected by chance during flooding (i.e., the interaction term was significantly positive in Table 1A; see also Fig. 2).This situation was mostly due to a decrease in Ischnothele caudata (Dipluridae), the only funnel-web tarantula noted, which represented 70% of the spiders recorded during the dry period and 42% during flooding. The Ctenidae (banana spiders) were represented by Cupiennius salei, the Salticidae by the genera Thiodina, Lysomanes and Menemerus, the Tetragnathidae by the genus Leucauge, while the Araneidae and Linyphiidae were not identifiable at the genus level.
Points refer to the observed numbers, vertical lines to the model prediction.
Direct association with Aechmea bracteata in the context of a drought and flooding
Flooding has a significantly negative effect on the number of spiders, but we did not find an effect for contact with A. bracteata per se (Table 1B). However, the presence of A. bracteata significantly increased the number of spiders during flooding (spiders in direct contact with the plant), but not during the dry period (i.e., the interaction term was significantly positive in Table 1B; see also Fig. 3). Indeed, during flooding, A. bracteata individuals sheltered spiders regardless of whether they were orb-weaving or not (1.11±0.21 vs. 1.16±0.22; N = 37; Z = 0.02; P = 0.98). In contrast, during the drought, most of the spiders noted in direct contact with the A. bracteata foliage belonged to the Dipluridae, Ctenidae and Salticidae as opposed to the Araneidae, Tetragnathidae and Linyphiidae (i.e., orb-weavers) (1.49±0.3 vs. 0.30±0.08; N = 47; Wilcoxon Matched Pairs test: Z = 3.4; P<0.001).
Spider presence in relationship to ant presence
Between the two sampling periods, the same A. bracteata individuals sheltered the same ant species: Azteca sp. (n = 5) and Dolichoderus bispinosus (n = 12) (both Dolichoderinae), and Neoponera villosa (Ponerinae) (n = 10). In 12 cases, two of these species shared the same A. bracteata, occupying different shoots (Azteca + Neoponera: n = 2; Azteca + Dolichoderus: n = 2; Dolichoderus + Neoponera: n = 8), but we did not record an ant colony in the remaining 10 A. bracteata. Also, Camponotus sp. (Formicinae) and Pseudomyrmex sp. (Pseudomyrmecinae) were each associated once with Azteca sp. and N. villosa, respectively.
During the dry period, we did not note a significant difference in the number of spiders (all species pooled) per A. bracteata whether the ants were present or not (2.80±0.60; N = 35 vs. 1.60±0.56; N = 10; U = 145; P = 0.41), while during flooding we noted significantly more spiders in the presence of ants (2.41±0.35; N = 29 vs. 0.90±0.30; N = 10; U = 69.5; P<0.05).
We further illustrate the distribution patterns of ants and spiders among bromeliads using the SOM, knowing that the number of shoots has only a slight impact on spider presence (Fig. 4). Indeed, ant influence was highlighted for the Dipluridae whose presence was negatively associated with Azteca and positively associated with Neoponera and to a lesser degree with Dolichoderus, regardless of the season. The contrary was true for the Ctenidae in May, but not in January; however, the number of individuals recorded was very low (low values on the lateral shade scales of Fig. 4A). Among the web-weaving spiders, the Araneidae seem positively associated with Azteca, while the Tetragnathidae and Linyphidae were present regardless of the ant species occupying the A. bracteata. The Salticidae were positively associated with Azteca in January 2012 during flooding, but not in May 2011.
Distribution of the A. bracteata individuals on the SOM during the dry (Fig. 4A, May 2011) and the flooding period (Fig. 4B, January 2012) according to their spider and ant assemblages. The numbers of A. bracteata shoots were given a null weight during the ordination process, and therefore act as an explanatory variable. In the large map, A. bracteata individuals that are neighbors within hexagons (or output neurons) are expected to have similar spider-ant assemblages, while those separated by a large distance from each other have different spider-ant assemblages. Clusters A–D (May 2011) and A–E (January 2012) were delineated by applying Ward’s algorithm to the weight vectors of the spider and ant species in the various hexagons. Each small map representing the number of shoots or one taxa can be compared to (or superimposed on) the corresponding large map representing the distribution of A. bracteata. They thus show gradients in the number of shoots (Nshoots), the probability of occurrence of each ant species (first line in the small maps), and the abundance of each spider taxa (second and third lines in the small maps) within the SOM (in shades of grey; dark = high values, light = low values). Codes (e.g., AB9) correspond to individual plants (sampling units).
Climatic conditions and spider abundance, distribution and relationship with Aechmea bracteata
During the dry season, A. bracteata permits spiders to survive a prolonged drought, something noted for other spider taxa –. Moreover, during flooding, the spiders, which can no longer live on the ground, also disappeared from trees devoid of an A. bracteata, even though these trees could have allowed them to escape the flooding. So, almost all of the spiders recorded were associated with A. bracteata which serves as a refuge.
The most abundant spider species noted in this study, the funnel-web tarantula, I. caudata, is a subsocial mygalomorph (Dipluridae) known for providing extensive maternal care and spinning thick curtain webs with a tubular retreat and a sticky sheet-like structure to catch prey . Individuals of this species build a permanent web on the ground, under rocks, at the base of trees or can cover plants; in all cases, a cavity permits them to install their tubular retreat . This was also the case in this study when the forest was dry, although I. caudata individuals were frequent in the A. bracteata foliage. However, during flooding, nearly only A. bracteata offers a suitable architecture for this spider species which can weave its tubular retreat in the base of the long and sturdy leaves.
The absence of spiders on trees other than those bearing A. bracteata during flooding could be the consequence of a ‘cleansing effect’ resulting from the heavy rains and strong winds that affected the spiders which were already installed on these trees as well as those which took refuge on them while the ground was flooded. It appears that the A. bracteata architecture offers a good shelter for spiders during these drastic periods (see also ). In addition, one must keep in mind that spider distribution is related to food location , so that spider association with A. bracteata is likely also related to prey abundance.
The majority of the spiders we observed, particularly the funnel-web tarantulas and the orb-weaving spiders, are known to live on supporting structures and in ecosystems different from those of the present study , –; in other words, they are not tank bromeliad specialists. On the contrary, the Ctenidae, including species of the genus Cupiennius (as noted in this study) and the Salticidae have already been reported as associated with bromeliads, but they may also live on other plants –.
In the inundated forests along the Neotropical coasts affected by frequent climatic events such as hurricanes , large tank bromeliads, including A. bracteata, offer permanent shelter to a wide diversity of organisms. Indeed, they form islands for aquatic and terrestrial fauna, including arboreal ants , , , . We show that, in contrast, A. bracteata acts as a refuge for spiders during flooding as in other climatic conditions they are not associated with bromeliads –; see also .
It is known that, for spiders, ants represent the risk of being killed , , , although some spiders, such as I. caudata, frequently prey on ants . The association of funnel-web tarantulas with particular ant species may be the result of predation by those spiders on the ants. Other spiders, such as the Ctenidae, are generalist predators that may prey on ants , whereas their great velocity, their ability to jump away  and their good vision , allow them to escape ant attacks and to co-exist with ants. Similar traits are known in the Salticidae, which are also good at avoiding ants thanks to their vision and ability to recognize ants . Many orb-weavers do not prey on ants, carefully expulsing the ants that fall onto their web , . Even when their webs are anchored on ant-occupied bromeliads, these spiders can share sites with ants thanks to the isolation provided by those webs . In addition, the web silk of certain species repels ants .
Here we show that ant presence not only does not repel spiders but rather favors their presence and some specificity was even noted between certain ant and spider taxa. Thus, one can hypothesize that, at least for those species well adapted at avoiding ants, some spiders benefit from ant presence as protection from other enemies. Indeed, protection from predation through association with aggressive ants is exemplified when the orb-weaver, Eustala oblonga (Araneidae), inhabits an ant-acacia . Also, Phintella piatensis (Salticidae) lives on the territory of the arboreal weaver ant, Oecophylla smaragdina, despite being occasionally preyed upon. In reality, it uses the ant scent as protection from its main predator, a spitting spider of the genus Scytodes . Finally, myrmecomorphy, or ant-like appearance, permits some salticids to gain protection from other spiders through Batesian mimicry (a palatable spider avoids predation by resembling an unpalatable ant) , .
Therefore, A. bracteata individuals constitute ecological refuges during flooding, and their associated ants globally favor spider presence (see also ).
In conclusion, the nature of the relationship between spiders, A. bracteata and ants depends on climatic events and arthropod traits. Aechmea bracteata not only provides fauna with the habitat and water which allow them to avoid suffering from drought, but also has great importance in the preservation of biodiversity during flooding. Therefore, this tank bromeliad has an important role in preserving arthropod fauna in the inundated forests of Quintana Roo. This role should become more important in the coming years in a context of climate change as El Niño/La Niña events are expected to be more frequent and intense, which in this area will likely correspond to an increase in the intensity of droughts. Like many tank bromeliads, A. bracteata is well adapted to wet/dry extreme events and may mitigate the effects of climate change on the local arthropod fauna.
Conceived and designed the experiments: YH BC AD. Performed the experiments: YH BC AD LP. Analyzed the data: YH AD RC BH. Contributed reagents/materials/analysis tools: YH BC AD FA. Contributed to the writing of the manuscript: YH AD RC BC. Identified the spiders: YH.
- 1. Parmesan C, Yohe G (2003) A globally coherent fingerprint of climate change impacts across natural systems. Nature 421:37–42.
- 2. Root TL, Price J, Hall K, Schneider S, Rosenzweig C, et al. (2003) Fingerprints of global warming on wild animals and plants. Nature 421:57–60.
- 3. Dejean A, Céréghino R, Carpenter JM, Corbara B, Hérault B, et al. (2011) Climate change impact on Neotropical social wasps. PLoS ONE 6:e27004.
- 4. IPCC (2013) Climate change 2013: the physical science basis. Working Group I Contribution to the IPCC Fifth Assessment Report. Cambridge: Cambridge University Press. 1535 p. Available: http://www.ipcc.ch/report/ar5/wg1/. Accessed 12 Nov 2014.
- 5. Philander SGH (1990) El Niño, La Niña and the Southern Oscillation. San Diego: Academic Press. 293 p.
- 6. Nakaegawa T, Kitoh A, Murakami H, Kusunoki K (2014) Annual maximum 5-day rainfall total and maximum number of consecutive dry days over Central America and the Caribbean in the late twenty-first century projected by an atmospheric general circulation model with three different horizontal resolutions. Theor Appl Climatol 116:155–168.
- 7. Dejean A, Olmsted I (1997) Ecological studies on Aechmea bracteata (Swartz) (Bromeliaceae). J Nat Hist 31:1313–1334.
- 8. Frank JH, Lounibos LP (2009) Insects and allies associated with bromeliads: a review. Terrest Arthrop Rev 1:125–153.
- 9. Jabiol J, Corbara B, Dejean A, Céréghino R (2009) Structure of aquatic insect communities in tank bromeliads in a East-Amazonian rainforest in French Guiana. Forest Ecol Manag 257:351–360.
- 10. McCracken SF, Forstner MRJ (2014) Oil road effects on the anuran community of a high canopy tank bromeliad (Aechmea zebrina) in the upper Amazon basin, Ecuador. PLoS ONE 9:e85470.
- 11. Brouard O, Le Jeune A-H, Leroy C, Céréghino R, Roux O, et al. (2011) Are algae relevant to the detritus-based food web in tank bromeliads? PLoS ONE 6:e20129.
- 12. Atwood TB, Hammill E, Greig HS, Kratina P, Shurin JB, et al. (2013) Predator-induced reduction of freshwater carbon dioxide emissions. Nature Geosc 6:191–194.
- 13. Barth FG, Seyfarth EA, Bleckmann H, Schüch W (1988) Spiders of the genus Cupiennius Simon 1891 (Araneae, Ctenidae). I. Range distribution, dwelling plants, and climatic characteristics of the habitats. Oecologia 77:187–193.
- 14. Schuster M, Baurecht D, Mitter E, Schmitt A, Barth FG (1994) Field observations on the population structure of three ctenid spiders (Cupiennius, Araneae, Ctenidae). J Arachnol 22:32–38.
- 15. Romero GQ, Vasconcellos-Neto J (2004) Spatial distribution patterns of jumping spiders associated with terrestrial bromeliads. Biotropica 36:596–601.
- 16. Santos JA, Romero GQ (2004) A new bromeliad-dwelling jumping spider (Araneae, Salticidae) from Brazil. J Arachnol 32:188–190.
- 17. Calaça-Dias S, Domingos-Brescovit A (2004) Microhabitat selection and co-occurrence of Pachistopelma rufonigrum Pocock (Araneae, Theraphosidae) and Nothroctenus fuxico sp. nov. (Araneae, Ctenidae) in tank bromeliads from Serra de Itabaiana, Sergipe, Brazil. Rev Bras Zool 21:789–796.
- 18. de Omena PM, Romero GQ (2008) Fine-scale microhabitat selection in a bromeliad-dwelling jumping spider (Salticidae). Biol J Linn Soc 94:653–662.
- 19. de Omena PM, Romero GQ (2010) Using visual cues of microhabitat traits to find home: the case study of a bromeliad-living jumping spider (Salticidae). Behav Ecol 21:690–695.
- 20. Gonçalves-Souva T, Almeida-Neto M, Romero GQ (2011) Bromeliad architectural complexity and vertical distribution predict spider abundance and richness. Aust Ecol 36:476–484.
- 21. Sanders D, Platner C (2007) Intraguild interactions between spiders and ants and top-down control in a grassland food web. Oecologia 150:611–624.
- 22. Halaj J, Ross DW, Moldenke AR (1997) Negative effects of ant foraging on spiders in Douglas-fir canopies. Oecologia 109:313–322.
- 23. Nelson XJ, Jackson RR, Pollard SD, Edwards GB, Barrion AT (2004) Predation by ants on jumping spiders (Araneae: Salticidae) in the Philippines. N Z J Zool 31:45–56.
- 24. Hénaut Y, Pablo J, Ibarra-Nuñez G, Williams T (2001) Retention capture and consumption of experimental prey by orb-weaving spiders in coffee plantations of Southern México. Entom Exp Appl 98:1–8.
- 25. Hénaut Y, Machkour-M’Rabet S, Lachaud JP (2014) The role of learning in risk-avoidance strategies during spider–ant interactions. Anim Cogn 7:185–195.
- 26. Nentwig W (1986) Non-webbuilding spiders: prey specialists or generalists? Oecologia 69:571–576.
- 27. Allan RA, Elgar MA, Capon RJ (1996) Exploitation of an ant chemical alarm signal by the Zodariid spider Habronestes bradleyi Walckenaer. Proc R Soc London 263:69–73.
- 28. Jackson RR, Pollard SD (1996) Predatory behavior of jumping spiders. Ann Rev Entomol 41:287–308.
- 29. Nelson XJ, Jackson RR, Pollard SD, Edwards GB, Barrion AT (2005) Living with the enemy: jumping spiders that mimic weaver ants. J Arachnol 33:813–819.
- 30. Beutelspacher BCR (1999) Bromeliaceas como ecosistemas. Con especial referencia a Aechmea bracteata (Swartz) Griseb. Mexico: Plaza y Valdes Editores. 123 p.
- 31. Benzing DH (2008) Vascular epiphytes: general biology and related biota. Cambridge: Cambridge University Press. 376 p.
- 32. Schmidt CA, Shattuck SO (2014) The higher classification of the ant subfamily Ponerinae (Hymenoptera: Formicidae), with a review of Ponerine ecology and behavior. Zootaxa 3817:001–242.
- 33. R Development Core Team, 2011. R: A language and environment for statistical computing. Vienna. Available: http://www.R-project.org.
- 34. Kohonen T (2001) Self-Organizing Maps, 3rd edn. Berlin: Springer. 501 p.
- 35. Coyle FA (1995) A Revision of the funnelweb mygalomorph spider subfamily Ischnothelinae (Araneae, Dipluridae). Bull Amer Mus Nat Hist 226:1–133.
- 36. Raizer J, Amaral MEC (2001) Does the structural complexity of aquatic macrophytes explain the diversity of associated spider assemblages? J Arachnol 29:227–237.
- 37. Hardwood JD, Sunderland KD, Symondson WOC (2001) Living where the food is: web location by linyphiid spiders in relation to prey availability in winter wheat. J Appl Ecol 38:88–99.
- 38. Zschokke S, Hénaut Y, Benjamin SP, García-Ballinas JA (2006) Prey-capture strategies in sympatric web-building spiders. Can J Zool 84:964–973.
- 39. Dejean A, Olmsted I, Snelling RR (1995) Tree-epiphyte-ant relationships in the low inundated forest of Sian Ka’an Biosphere Reserve, Quintana Roo, Mexico. Biotropica 27:57–70.
- 40. Adis J (1997) Terrestrial invertebrates: survival strategies, group spectrum, dominance and activity patterns. In:Junk WJ ed. The Central Amazon floodplain. Ecology of a pulsing system. Ecological Studies 126. Berlin: Springer. 299–317.
- 41. Gillespie RG, Reimer N (1993) The effect of alien predatory ants (Hymenoptera: Formicidae) on Hawaiian endemic spiders (Araneae: Tetragnathidae). Pacific Sc 47:21–33.
- 42. Weihmann T, Karner M, Full RJ, Blickhan R (2010) Jumping kinematics in the wandering spider Cupiennius salei. J Comp Physiol A 196:421–438.
- 43. Land MF, Barth FG (1992) The quality of vision in the ctenid spider Cupiennius salei. J Exp Biol 164:227–242.
- 44. Nelson XJ, Jackson RR (2006) Vision-based innate aversion to ants and ant mimics. Behav Ecol 17:676–681.
- 45. Zhang S, Koh TH, Seah WK, Lai YH, Elgar MA, et al. (2012) A novel property of spider silk: chemical defence against ants. Proc R Soc B 279:1824–1830.
- 46. Styrsky JD (2014) An orb-weaver spider exploits an ant–acacia mutualism for enemy-free space. Ecol Evol 4:276–283.
- 47. Nelson XJ, Jackson RR (2014) Timid spider uses odor and visual cues to actively select protected nesting sites near ants. Behav Ecol Sociobiol 68:773–780.
- 48. Durkee CA, Weiss MR, Uma DB (2011) Ant mimicry lessens predation on a North American jumping spider by larger salticid spiders. Environ Entomol 40:1223–1231.
- 49. Huang JN, Cheng RC, Li D, Tso IM (2011) Salticid predation as one potential driving force of ant mimicry in jumping spiders. Proc R Soc B 278:1356–1364.
- 50. Gerlach J, Samways M, Pryke J (2013) Terrestrial invertebrates as bioindicators: an overview of available taxonomic groups. J Insect Conserv 17:831–850.