Services on Demand
- Cited by SciELO
- Access statistics
- Cited by Google
- Similars in SciELO
- Similars in Google
Print version ISSN 1519-566X
Neotrop. entomol. vol.40 no.6 Londrina Nov./Dec. 2011
ECOLOGY, BEHAVIOR AND BIONOMICS
MG FerreiraI, II; OC de PinhoII; JBP BalestieriII; O FaccendaIII
ILab de Palinologia, Instituto Nacional de Pesquisas da Amazônia, Manaus, AM, Brasil
IIFac de Ciências Biológicas e Ambientais, Univ Federal da Grande Dourados, Dourados, MS, Brasil
IIIUniv Estadual de Mato Grosso do Sul, Dourados, MS, Brasil
This is a study of the population fluctuation of euglossine species, as well as their preferences for scent baits (cineole, eugenol, vanillin and methyl salicylate) in two forest strata (canopy and understory) at the Reserva Florestal do Azulão, a forest fragment located in the municipality of Dourados, MS, Brazil (22°12'S, 54°55'W). We collected a total of 529 males from four genera and eight species. Diversity and equitability for both strata (understory: H' = 1.195 and J' = 0.6139; canopy: H' = 1.193 and J' = 0.6131) did not show a significant difference and a high similarity index was found (P = 87.5%). On the other hand, abundance was substantially higher in the canopy (n = 358) than in the understory (n = 171). From the scents used, eugenol attracted a larger number of individuals (n = 225), but cineole and vanillin attracted a higher number of species.
Keywords: Diversity, equitability, floral reward, richness, seasonality
The euglossine tribe forms a very distinct group within Apidae, comprising five genera (Euglossa, Eufriesea, Eulaema, Aglae, and Exaerete) with approximately 200 described species (Roubik & Hanson 2004, Ramirez et al 2010). It is broadly distributed throughout the tropical America, occurring from central Argentina to southern United States (Michenner 2007). Its greatest richness and abundance, however, are found in tropical rainforests (Cameron 2004, Roubik 2004).
One of this group's main characteristics is the males' practice of collecting aromatic substances, which are floral rewards produced in Orchidaceae, Araceae, Gesneriaceae, Solanaceae, Euphorbiaceae, Amaryllidaceae, and Theaceae osmophores (Sazima et al 1993, Melo 1995, Carvalho & Machado 2002, Braga & Garófalo 2003). In face of this characteristic, the use of odor baits has allowed rapid surveys and ecological studies of the group in different Neotropical areas.
In Brazil, systemized studies on euglossine have been concentrated predominantly in tropical forests. However, due to these insects' great importance as indicators of environmental quality, there is a pressing need for further taxonomic work and the determination of species that occur outside the humid forests region. Otherwise, the use of these bees as indicators of environmental quality will become rather restricted in areas in which data for this group are unavailable (Peruquetti et al 1999, Sofia & Suzuki 2004).
There are few studies focusing the fauna and behavior of these bees in open and fragmented areas in Brazil such as the cerrado biome, in the State of Mato Grosso do Sul (Rebelo & Silva 1999, Nemésio & Faria Jr 2004, Alvarenga at al 2007). The Brazilian cerrado is characterized by the presence of several forest fragments, and one of the structural factors that greatly influences the maintenance of diversity in these fragments is its spatial heterogeneity (Hart & Horwitz 1991). This heterogeneity is usually associated to the occurrence of a greater number of microhabitats, therefore allowing the coexistence of a greater number of species (Gonçalves & Lozada 2005). Thus, a new emphasis has been given to studies on the vertical distribution of the physical-chemical and biotic characteristics of these forests (Davies et al 1997). In that sense, despite the numerous studies on euglossine bees in Brazil, in the cerrado region its fauna is poorly known (Nemésio & Silveira 2007), and little has been done on the vertical stratification of this group (Oliveira & Campos 1996, Otero & Sallenave 2003, Martins & Souza 2005).
This study is aimed at identifying the fauna and the fluctuations in the population of euglossine males, while also evaluating their preferences for scented baits and their possible vertical stratification in a forest fragment in the cerrado of Mato Grosso do Sul.
Material and Methods
The present study was undertaken in a 43 ha remnant area of cerrado scrubland in Mato Grosso do Sul, denominated "Reserva Florestal da Fazenda Coqueiro". The remnant is located at 430 m.a.s.l, in the municipality of Dourados (22°12' S, 54°55' W). The area is characterized by its relative isolation from other fragments, which are covered by pastures or plantations. It is also under constant threat, imposed either by real estate speculation, which has been taking over land bordering neighboring areas, or by the timber extraction industry.
The region is represented by continental tropical climate, with two well-defined seasons: rainy summer and dry winter. The average summer temperature is 26.4ºC, while the winter one is 19.8ºC, and the annual average is 23.7ºC (EMBRAPA/CPAO 2008).
The collection of euglossine males was conducted from April 2004 to March 2005 in two strata of a cerrado fragment: understory and canopy. In the understory, the traps were placed at a height of up to 2 m, and at least 5 m apart. Traps in the canopy were installed at heights of 10-15 m, and also 5 m apart from each other. The captured individuals were fixed in 70% ethanol and stored for later identification.
Fifty-two collections were conducted on a weekly basis. Modified scent traps manufactured with 2-liter PET bottles (Fig 1) had an increased internal area and a reduced number of entrances in order to avoid the escape of captured individuals. In addition, bottles were used with stoppers and wicks to prolong the attractiveness of the scents used. A total of eight traps were distributed throughout the forest, with four traps per stratus. The maintenance (insect removal and replacement of scents) of the traps was performed once a week. The following scents were used: cineole, eugenol, methyl salicylate, and vanillin.
The weekly averages of climatic data, relative humidity, and temperature, were supplied by the meteorological station of the Universidade Federal da Grande Dourados (Dourados, MS).
Analyses of the bee species captured in the traps were based on the indexes of frequency, constancy, abundance and dominance (Silveira Neto et al 1976). Once the percentage of constancy was obtained, species were grouped into the following categories: constant (w) when present in more than 50% of the collections; accessories (y) when present in 25-50% of the collections; and accidental (z) when present in less than 25% of the collections.
For the estimation of abundance, the limits established by the confidence interval (CI) at 5% and 1% of probability were evaluated, and the following classes were determined: rare (r), when the number of individuals from a given species was less than the lower limit of the CI at 1% of probability; disperse (d), if the number of individuals was between the lower limits of the CI at 1% and 5% of probability; common (c), when the number of individuals was maintained between the limits of 5% and 95%; abundant (a), if the number of individuals was between the limits of 95% and 99%; and very abundant (ma), when the number of individuals was greater than 99% of probability. Regarding dominance, a species was considered dominant when it presented relative frequency superior to 1/S, where S is the total number of species in each environment. In order to compare the average number of individuals among the environments, the non-parametric U-test by Mann-Whitney was applied.
The diversity in the environments was calculated by using the Shannon-Wiener Index (Poole 1974), and differences were checked using the t test (P < 0.05). Based on the diversity index, the evenness (J') of Pielou (1977) was also calculated, where J' = H'/H'Max; H'Max = ln(S); and S = number of species, its value ranging from 0 to 1, where 1 corresponds to the situation in which all species are equally abundant.
The similarity between strata was obtained using the Renkonen index (Wolda 1981), given by P = ∑ minimum (p1i, p2i), where, p1i is the percentage of species in stratum 1, and p2i is the percentage of species in stratum 2. The percentage can range from 0 (no shared species) to 100 (completely shared).
The Past statistical program, 1.37 Hammer version et al (2001), was used to calculate diversity (H' and J'). The remaining tests were performed with the Spss program for Windows, version 12.0 (Spss Inc. 2005).
Fauna and stratification
A total of 529 euglossine males, belonging to eight species of Euglossa, Eufriesea, Eulaema, and Exaerete were captured. Euglossa was the most abundant genus totalizing 59.7% of all the individuals collected, and it was represented by four species: Euglossa cordata (L.), with six individuals (1.1%) showing discreet occurrences in June, July, September, December, and January; Euglossa pleosticta Dressler, with 25 individuals (4.7%) showing greater occurrence in April, and discrete presence in May, September, October, December, January, February, and March; Euglossa fimbriata Rebêlo & Moure, with only one individual (0.2%) captured in December; and Euglossa stellfeldi Moure, with 284 individuals (53.7%) collected throughout the whole sampling period (Fig 2).
Eufriesea was represented by 154 individuals (29.1%) that belonged all to the Eufriesea violacea (Blanchard) species, most frequent from November to January. The 38 collected specimens (7.2%) of Eulaema nigrita Lepeletier, on the other hand, were distributed throughout April, May, September, November, December, January, and February. The least abundant genus of Exaerete, on its turn, was represented by 20 (3.8%) specimens of Exaerete smaragdina Guérin collected mostly in November, February and March, and by a single specimen (0.2%) of Exaerete dentata L., captured in December. Altogether, E. stellfeldi, E. violacea and E. nigrita represented 90% of all specimens captured (Fig 2).
Besides being highly frequent during the sampling period, E. stellfeldi was also observed in the two studied strata. While 88 specimens of E. stellfeldi were found in the understory, 196 individuals were collected from the canopy. This species was therefore classified as very abundant (ma) and dominant (s), although it was constant (w) only in the canopy stratum (Table 1). Euglossa stellfeldi was also less affected by climatic conditions, showing little variation in its frequency throughout the collection period. Other species such as E. nigrita and E. violacea on their turn, showed greater abundance in April and in the period between November and December, respectively (Fig 2).
No difference in species diversity was observed between the understory (H' = 1.195) and the canopy (H' = 1.193). The evenness of the understory (J' = 0.6139) and canopy (J' = 0.6131) allowed us to conclude that the two strata were similar regarding uniformity in the collection of bees (Table 1). The Renkonen similarity-index was high (P = 8.75%), showing that six of the eight species found in this study were shared by the two strata. However, a higher abundance of specimens was found in the canopy (n = 358) as compared to the understory (n = 171). Euglossa stellfeldi, E. violacea and E. nigrita were considerably more abundant in the canopy than in the understory (Table 1).
Cineole and vanillin (H' = 1.05) attracted a larger number of species than eugenol (H' = 0.38) and methyl salicylate (H' = 0.60) (Table 2). However, eugenol-scented traps were by far the most attractive ones, collecting an average of 2.4 bees/trap. They were followed by cineol and vanillin, which collected 1.3 bees/trap each. The least attractive trap was the one scented with methyl salicylate (0.1 bee/trap) (Table 4). Bee attractiveness to scented traps was also species dependent. While nearly 80% of the E. stellfeldi specimens were attracted to eugenol-scented traps, most individuals of E. smaragdina were attracted to methyl salicylate-scented traps. Cineole and vanillin-scented traps were most attractive to E. violacea. Cineole-scented traps were also attractive to E. stellfeldi and E. nigrita, whereas those with vanillin were attractive to E. pleosticta and E. nigrita (Table 3).
Although the diversity and similarity indexes found in the two studied strata did not differ, the abundance of specimens was substantially greater in the upper stratum, which is contrary to what had been previously reported (Oliveira & Campos 1996, Otero & Sallenave 2003, Martins & Souza 2005).
Several hypotheses have been presented to explain the possible causes of the euglossine stratification. In one of these hypotheses, Otero & Sallenave (2003) suggested that lower wind velocity, and consequently the slower dispersion of odor baits in the undergrowth, would difficult bait detection by bees and, therefore, explain the higher abundance in the canopy. For Ramalho (2004), the bees' vertical stratification could be related to the seasonality of resources and body size of the species. Or, perhaps, as suggested in this study, the activities of the euglossine may be related to the climatic oscillations during the year, which would act in the different strata. By doing so, these variations would create micro-habitats where, for some species, there would be greater occurrence of individuals. In that sense, the hypothesis proposed by Tonhasca et al (2002a), which states that within the same habitat, priority micro-habitats with greater abundance and richness of euglossine can exist, is here supported.
Considering the seasonal extremes, we highlight E. stellfeldi as the species found with the least variation during the collection period. Eufriesea violacea, on the other hand, had considerable peaks of occurrence in the rainy period, revealing a more seasonal behavior than the other studied species (Fig 2). These findings corroborate studies conducted in other locations that also indicated an accentuated seasonality for this species (Peruquetti & Campos 1997, Sofia & Suzuki 2004).
Eufriesea violacea was considered endemic to the Atlantic rain forest (Nemésio & Silveira 2007), being well represented mainly in the Southern and Southeastern Brazil (Wittmann et al 1987, Peruquetti & Campos 1997, Rebêlo & Garófalo 1991, Sofia & Suzuki 2004). Although the presence of this species had also been recorded by Kimsey (1982) in Central Brazil, more exactly in the Mato Grosso State region, doubts were left about its occurrence in the cerrado of Mato Grosso do Sul. These doubts were cleared in this study, where E. violacea was well represented. Furthermore, despite being described as sensitive to fragmentation (Giangarelli et al 2009), E. violacea abundance was greater than would be expected for the size of the studied fragment.
Isolation and fragmentation are always followed by physical modifications that are responsible for large reductions in plant and animal communities. In this sense, the occurrence and maintenance of diverse species can be directly or indirectly affected by the resulting micro-climatic modifications (Morato & Campos 2000). Some studies have sought to enlighten the possible impacts caused by deforestation and fragmentation of forests on the euglossine communities (Tonhasca et al 2003, Brosi 2009). Bee abundance has shown to be affected mainly by the size of the fragment and surrounding area, whereas species richness has been mainly related to the surrounding area. Although our data indicate that the decrease in abundance and species richness is related to the size of the fragment and to the degree of disturbance, we have to acknowledge that these data may have been influenced in part by the sampling method. Although the entomological nets have been shown to be more efficient than baited traps in bees sampling (Nemésio & Morato 2004, 2006), a recent report demonstrated differently (Storck-Tonon et al 2009).
Baited traps were selected as a sampling tool in this study due to the difficulties in collecting bees with entomological nets in the forest canopy. In addition, the chosen method was partly justified by the higher abundance of individuals registered in the canopy, which demonstrated that working only with the entomological net would have increased the risk of underestimating the abundance of euglossine in this fragment. Furthermore, the modifications undertaken in the traps guaranteed that the essences remained attractive for longer periods of time, which perhaps allowed the only representative of the rare E. dentata to be collected in baited traps (Silva & Rebelo 1999, Storck-Tonon et al 2009).
The indication that the euglossine abundance would depend on the scent used is not conclusive, since scents different to those used here are shown to be the most attractive in similar studies (Morato et al 1992, Rebelo & Garófalo 1997, Storck-Tonon et al 2009). Thus, the preference for a particular scent appears to be related to the existing local flora (availability and floral diversity) or even to the climate of the region where the study is undertaken. In that sense, the higher the number of essences used as baits in the traps, the higher would be the number of individuals and species collected (Oliveira & Campos 1995, 1996, Oliveira 1999).
The abundance of euglossine, unlike its richness, was significantly greater in the canopy, which provides evidence of their stratification when it comes to the number of specimens. Such fact may be related to the climatic oscillations during the year, which are capable of influencing the climate within the fragment in distinct ways by creating microclimates that may affect the activities of the different euglossine species in the forest strata.
Despite the low values in abundance and richness, our data highlighted the accentuated seasonality and the marked presence of E. violacea in the region of Mato Grosso do Sul, in addition to the record of E. dentata, a rare euglossine. Furthermore, the reduced number of species and specimens collected may be related to the size and degree of disturbance of the studied fragment, despite the methods used for collection. Nevertheless, eugenol was by far the most attractive essence, attracting the greatest number of specimens, while cineole and vanillin attracted the greatest number of species. Methyl salicylate was the least attractive essence, collecting one single representative of E. dentata. Therefore, the use of a greater number of essences is required in studies of diversity of euglossine bees.
Dr. André Nemésio of the Laboratory of Bee Ecology and Systematics (Depto. de Zoologia ICB, Universidade Federal de Minas Gerais), for the identification of specimens of Euglossa.
Alvarenga PEF, Freitas RF, Sugusto SC (2007) Diversidade de Euglossini (Hymenoptera: Apidae) em áreas de cerrado do Triângulo Mineiro, MG. Biosci J 23: 30-37. [ Links ]
Braga AK, Garófalo CA (2003) Coleta de fragrâncias por machos de Euglossa townsendi Cockerell (Hymenoptera, Apidae, Euglossini) em flores de Crinum procerum Carey (Amaryllidaceae), p.201-207. In Melo GAR, Alves-dos-Santos I (eds) Apoidea Neotropica: homenagem aos 90 anos de Jesus Santiago Moure. Criciúma, Ed. UNESC, XVI+320p. [ Links ]
Brosi BJ (2009) The effects of forest fragmentation on euglossine bee communities (Hymenoptera: Apidae: Euglossini). Biol Conserv 142: 414-423. [ Links ]
Cameron SA (2004) Phylogeny and biology of neotropical orchid bees (Euglossini). Annu Rev Entomol 49: 377-404. [ Links ]
Carvalho R, Machado IC (2002) Pollination of Catasetum macrocarpum (Orchidaceae) by Eulaema bombiformis (Euglossini). Lindleyana 17: 85-90. [ Links ]
Davis AJ, Huijbregts J, Kirk-Spriggs AH, kriken J, Sutton SL (1997) The ecology and behavior of arboreal dung beetles in Borneo, p.417-432. In Stork NE, Adis J, Didham RK (eds) Canopy arthropods. London, Chapman & Hall, 567p. [ Links ]
Giangarelli DC, Freiria GA, Colatreli OP, Suzuki KM, Sofia SH (2009) Eufriesea violacea (Blanchard) (Hymenoptera: Apidae): an orchid bee apparently sensitive to size reduction in forest patches. Neotrop Entomol 38: 610-615. [ Links ]
Gonçalves TT, Louzada JNC (2005) Estratificação vertical de coleópteros carpófilos (Insecta: Coleoptera) em fragmentos florestais do Sul do estado de Minas Gerais, Brasil. Ecol Austral 15: 101-110. [ Links ]
Hammer O, Harper AT, Rian PD (2001) Past: palaeonthological statistics software package for education and data analysis. Version. 1.37. Disponível em: http://palaeo-electronica.org/2001_1/past/issue1_01.htm (accessed on 12 November 2008). [ Links ]
Hart DD, Horwitz RJ (1991) Habitat diversity and species-area relationship: alternative models and tests. Chapter 3, p.47-68. In Bell SS, McCoy ED, Mushinsky HR (eds) Habitat structure. The physical arrangement of objects in Space. London, Chapman and Hall, 567p. [ Links ]
Kimsey LS (1982) Systematics of bees of the genus Eufriesea (Hymenoptera, Apidae). Univ Calif Publ Entomol 95: 1-125. [ Links ]
Martins CF, Souza AKP (2005) Estratificação vertical de abelhas Euglossina (Hymenoptera, Apidae) em uma área de Mata Atlântica, Paraíba, Brasil. Rev Bras Zool 22: 913-918. [ Links ]
Melo GAR (1995) Fragrance gathering by Euglossa males in flowers of Ternstroemia dentate (Theaceae) (Hymenoptera: Apidae: Euglossinae). Entomol Gen 19: 281-283. [ Links ]
Michener CD (2007) The bees of the world. Baltimore, John Hopkins University Press, 953p. [ Links ]
Morato EF, Campos LAO (2000) Efeitos da fragmentação florestal sobre vespas e abelhas solitárias em uma área da Amazônia Central. Rev Bras Zool 17: 429-444. [ Links ]
Morato EF, Campos LAO, Moure JS (1992) Abelhas Euglossini (Hymenoptera, Apidae), coletados na Amazônia Central. Revta Bras Entomol 36: 767-771. [ Links ]
Nemésio A, Faria Jr LRR (2004) First assessment of orchid bee fauna (Hymenoptera: Apidae: Apini: Euglossina) of Parque Estadual do Rio Preto, a cerrado area in southeastern Brazil. Lundiana 5: 113-117. [ Links ]
Nemésio A, Morato EF (2004) Euglossina (Hymenoptera: Apidae) of the Humaitá Reserve, Acre state, Brazilian Amazon, with comments on bait trap efficiency. Rev Tecnol Amb 10: 71-80. [ Links ]
Nemésio A, Morato EF (2006) The orchid-bee fauna (Hymenoptera: Apidae) of Acre state (northwestern Brazil) and a re-evaluation of euglossine bait-trapping. Lundiana 7: 59-64 [ Links ]
Nemésio A, Silveira FA (2007) Diversity and distribution of orchid bees (Hymenoptera: Apidae) with a revised checklist of species. Neotrop Entomol 36: 874-888. [ Links ]
Oliveira ML (1999) Sazonalidade e horário de atividade de abelhas Euglossinae (Hymenoptera, Apidae), em floresta de terra firme na Amazônia Central. Rev Bras Zool 16: 83-90. [ Links ]
Oliveira ML, Campos LAO (1995) Abundância, riqueza e diversidade de abelhas euglossinae (Hymenoptera:Apidae) em florestas continuas de terra firme na Amazônia Central, Brasil. Rev Bras Zool 12: 547-556. [ Links ]
Oliveira ML, Campos LAO (1996) Preferência por extratos florais e por substâncias odoríferas em abelhas Euglossinae. Rev Bras Zool 13: 1075-1085. [ Links ]
Otero JT, Sallenave A (2003) Vertical stratification of euglossine bees (Hymenoptera: Apidae) in an Amazonian Forest. Pan-Pac Entomol 79: 151-154. [ Links ]
Peruquetti RC, Campos LAO (1997) Aspectos da biologia de Euplusia violacea (Blanchard) (Hymenoptera:Apidae:Euglossini). Rev Bras Zool 14: 91-97. [ Links ]
Peruquetti RC, Campos LAO, Coelho CDP, Abantes CVM, Lisboa LCO (1999) Abelhas Euglossini (Apidae) de áreas de mata atlântica: abundância, riqueza e aspectos biológicos. Rev Bras Zool 16: 101-118. [ Links ]
Pielou EC (1977) Ecological diversity. New York, John Wiley & Sons, 165p. [ Links ]
Poole RW (1974) An introduction to quantitative ecology. New York, McGraw-Hill, 532p. [ Links ]
Ramalho M (2004) Stingless bees and mass flowering trees in the canopy of Atlantic Forest: a tight relationship. Acta Bot Bras 18: 37-47. [ Links ]
Ramírez SR, Roubik DW, Skov C, Pierce NE (2010) Phylogeny, diversification patterns and historical biogeography of euglossine orchid bees (Hymenoptera: Apidae). The Linnean Society of London. Biol J Linn Soc 100: 552-572. [ Links ]
Rebêlo JMM, Garófalo CA (1991) Diversidade e sazonalidade de machos de Euglossina (Hymenoptera, Apidae) e preferências por iscas-odores em um fragmento de floresta no sudeste do Brasil. Rev Bras Zool 787-799. [ Links ]
Rebêlo JMM, Garófalo CA (1997) Comunidade de machos de Euglossini (Hymenoptera: Apidae) em matas semidecíduas do nordeste do estado de São Paulo. An. Soc Entomol Brasil 26: 243-255. [ Links ]
Rebêlo JMM, Silva FS (1999) Distribuição de abelhas Euglossini (Hymenoptera: Apidae) no estado do Maranhão Brasil. An Soc Entomol Brasil 28: 389-401. [ Links ]
Roubik DW (2004) Long-term studies of solitary bees: what the orchid bees are telling us, p.97-103. In Freitas BM, Pereira JOP (eds) Solitary bees: conservation, rearing and management for pollination. Fortaleza, Imprensa Universitária, 285p. [ Links ]
Roubik DW, Hanson PE (2004) Abejas de orquídeas de la America tropical - Biología y guía de campo. Costa Rica, Editorial INBio, 370p. [ Links ]
Sazima M, Vogel S, Cocucci A, Hausner G (1993) The perfume flowers of Cyphomandra (Solanaceae): pollination by Euglossine bees, bellows mechanism, osmophores, and volatiles. Plant Syst Evol 187: 51-88. [ Links ]
Silveira Neto S, Nakano O, Barbin D, Villa Nova NA (1976) Manual de ecologia dos insetos. Piracicaba, Ed. Agronômica Ceres, 419p. [ Links ]
Sofia SH, Suzuki MS (2004) Comunidades de machos de abelhas Euglossina (Hymenoptera: Apidae) em fragmentos florestais no Sul do Brasil. Neotrop Entomol 33: 693-702. [ Links ]
Storck-Tonon D, Morato EF, Oliveira ML (2009) Fauna de Euglossina (Hymenoptera: Apidae) da Amazônia Sul-Ocidental, Acre, Brasil. Acta Amazon 39: 693-706. [ Links ]
Tonhasca JA, Albuquerque GS, Blackmer JL (2003) Dispersal of euglossine bees between fragments of the Brazilian Atlantic Forest. J Trop Ecol 19: 99-102. [ Links ]
Tonhasca JA, Blackmer JL, Albuquerque GS (2002a) within-habitat heterogeineity of Euglossine bees population: reevaluation of the evidence. London, J Tropic Ecol 18: 929-933. [ Links ]
Wittmann D, Radtke R, Hoffmann M, Blochtein B (1987) Seasonality and seasonal changes in preferences for chemicals baits of male Eufriesea violacea in Rio Grande do Sul, southern Brazil, p.730-731. In Eder J, Rembold H (eds) Chemistry and biology of social insects. Munique, Verlag J. Peperny, 757p. [ Links ]
Wolda H (1981) Similarity indices, sample sizes and diversity. Oecologia 50: 296-302. [ Links ]
Marcos G Ferreira
Lab de Palinologia
Instituto Nacional de Pesquisas da Amazônia
Av. André Araujo, 2936, CP 498, Aleixo
69060-001, Manaus, AM, Brasil
Received 10 February 2011 and accepted 30 July 2011
Edited by Fernando B Noll - UNESP