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Chironomid larvae inhabiting bromeliad phytotelmata in a fragment of the Atlantic Rainforest in Rio de Janeiro State

Larvas de Chironomidae (Insecta, Diptera) em fitotelmata de Bromeliaceae em um fragmento de Mata Atlântica no Estado do Rio de Janeiro

Abstracts

A study of chironomids (Diptera, Chironomidae) occurring in phytotelmata of Bromeliaceae was carried out in a fragment of the Atlantic Rain Forest in an area of the city of Magé, Pau Grande, one of the metropolitan areas of Rio de Janeiro City, during a period of 13 months between September 2006 and September 2007. Eight samplings were performed at intervals of 1 ½ months and the content of the phytotelmata of the bromeliad species Neoregelia concentrica (Vellozo) L.B. Smith, 1934 and Aechmea nudicaulis (Linnaeus) Grisebach, 1864, were examined. A taxonomical inventory and evaluation of the numerical abundance of Chironomidae larvae were performed in 50 specimens of the bromeliads, being 13 individuals of N. concentrica and 37 of A. nudicaulis. Three taxa of Chironomidae belonging to three distinct subfamilies were recorded: Polypedilum sp., Orthocladiinae genus A and Monopelopia sp. A total of 293 individuals of Chironomidae, were recorded, being 9 Polypedilum sp., 233 Orthocladiinae genus A, and 51 Monopelopia sp., the latter representing the first record of Monopelopia in phytotelmata in Rio de Janeiro State. Considering all samples, a mean density of 3.32 ± 2.62 chironomid larvae per phytotelmata was recorded. There was a positive relationship between the chironomid abundance and both precipitation and the volume of water in the phytotelmata. Apparently there is no preference by the chironomids regarding the colonistion of the bromeliad species.

invertebrates; bromeliad fauna; Chironomidae; Atlantic Forest


Um estudo dos Chironomidae presentes em fitotelmata de duas espécies de bromélias com ocorrência em um fragmento de Mata Atlântica de uma área do município de Magé, Pau Grande, uma das áreas metropolitanas do Estado do Rio de Janeiro, por um período de 13 meses, entre setembro de 2006 e setembro de 2007. Foram realizadas 8 coletas a intervalos de aproximadamente 1 ½ mês e analisados o conteúdo dos fitotelmata das espécies Neoregelia concentrica (Vellozo) L.B. Smith, 1934 e Aechmea nudicaulis (Linnaeus) Grisebach, 1864. Realizou-se o estudo taxonômico e a avaliação da abundância das larvas de Chironomidae em 50 exemplares de bromélias, sendo 13 exemplares de N. concentrica e 37 de A. nudicaulis. Três taxons de Chironomidae pertencentes a três subfamílias distintas foram registradas: Polypedilum sp., Orthocladiinae gênero A e Monopelopia sp. No total foram coletados 293 espécimes de Chironomidae, sendo nove indivíduos de Polypedilum sp., 233 de Orthocladiinae gen. A e 51 de Monopelopia sp., este último, o primeiro registro de Monopelopia em fitotelmata para o Estado do Rio de Janeiro. Considerando-se todas as amostragens realizadas, obteve-se um valor médio de 3,32 ± 2,62 de larvas de Chironomidae por fitotelmata. A abundância dos Chironomidae nos fitotelmata das bromélias variou de acordo com a precipitação e volume de água encontrado nas bromélias, não havendo preferência por parte dos Chironomidae estudados quanto ao tipo de bromélia para colonização.

invertebrados; fauna bromelícola; Chironomidae; Floresta Atlântica


ECOLOGY

Chironomid larvae inhabiting bromeliad phytotelmata in a fragment of the Atlantic Rainforest in Rio de Janeiro State

Larvas de Chironomidae (Insecta, Diptera) em fitotelmata de Bromeliaceae em um fragmento de Mata Atlântica no Estado do Rio de Janeiro

Sodré, VM.I, III,* * e-mail: viniciusmoraessodre@hotmail.com ; Rocha, O.II; Messias, MC.III

IPrograma de Pós-Graduação em Ecologia e Recursos Naturais, Universidade Federal de São Carlos - UFSCar, Rodovia Washington Luís, Km 235, SP-310, CEP 13565-905, São Carlos, SP, Brazil

IIDepartamento de Ecologia e Biologia Evolutiva, Universidade Federal de São Carlos - UFSCar,Rodovia Washington Luís, Km 235, SP-310, CEP 13565-905, São Carlos, SP, Brazil

IIIMuseu Nacional, Departamento de Entomologia, Quinta da Boa Vista, Universidade Federal do Rio de Janeiro - UFRJ, Bairro Imperial de São Cristóvão, CEP 20940-040, Rio de Janeiro, RJ, Brazil

ABSTRACT

A study of chironomids (Diptera, Chironomidae) occurring in phytotelmata of Bromeliaceae was carried out in a fragment of the Atlantic Rain Forest in an area of the city of Magé, Pau Grande, one of the metropolitan areas of Rio de Janeiro City, during a period of 13 months between September 2006 and September 2007. Eight samplings were performed at intervals of 1 ½ months and the content of the phytotelmata of the bromeliad species Neoregelia concentrica (Vellozo) L.B. Smith, 1934 and Aechmea nudicaulis (Linnaeus) Grisebach, 1864, were examined. A taxonomical inventory and evaluation of the numerical abundance of Chironomidae larvae were performed in 50 specimens of the bromeliads, being 13 individuals of N. concentrica and 37 of A. nudicaulis. Three taxa of Chironomidae belonging to three distinct subfamilies were recorded: Polypedilum sp., Orthocladiinae genus A and Monopelopia sp. A total of 293 individuals of Chironomidae, were recorded, being 9 Polypedilum sp., 233 Orthocladiinae genus A, and 51 Monopelopia sp., the latter representing the first record of Monopelopia in phytotelmata in Rio de Janeiro State. Considering all samples, a mean density of 3.32 ± 2.62 chironomid larvae per phytotelmata was recorded. There was a positive relationship between the chironomid abundance and both precipitation and the volume of water in the phytotelmata. Apparently there is no preference by the chironomids regarding the colonistion of the bromeliad species.

Keywords: invertebrates, bromeliad fauna, Chironomidae, Atlantic Forest.

RESUMO

Um estudo dos Chironomidae presentes em fitotelmata de duas espécies de bromélias com ocorrência em um fragmento de Mata Atlântica de uma área do município de Magé, Pau Grande, uma das áreas metropolitanas do Estado do Rio de Janeiro, por um período de 13 meses, entre setembro de 2006 e setembro de 2007. Foram realizadas 8 coletas a intervalos de aproximadamente 1 ½ mês e analisados o conteúdo dos fitotelmata das espécies Neoregelia concentrica (Vellozo) L.B. Smith, 1934 e Aechmea nudicaulis (Linnaeus) Grisebach, 1864. Realizou-se o estudo taxonômico e a avaliação da abundância das larvas de Chironomidae em 50 exemplares de bromélias, sendo 13 exemplares de N. concentrica e 37 de A. nudicaulis. Três taxons de Chironomidae pertencentes a três subfamílias distintas foram registradas: Polypedilum sp., Orthocladiinae gênero A e Monopelopia sp. No total foram coletados 293 espécimes de Chironomidae, sendo nove indivíduos de Polypedilum sp., 233 de Orthocladiinae gen. A e 51 de Monopelopia sp., este último, o primeiro registro de Monopelopia em fitotelmata para o Estado do Rio de Janeiro. Considerando-se todas as amostragens realizadas, obteve-se um valor médio de 3,32 ± 2,62 de larvas de Chironomidae por fitotelmata. A abundância dos Chironomidae nos fitotelmata das bromélias variou de acordo com a precipitação e volume de água encontrado nas bromélias, não havendo preferência por parte dos Chironomidae estudados quanto ao tipo de bromélia para colonização.

Palavras chave: invertebrados, fauna bromelícola, Chironomidae, Floresta Atlântica.

1. Introduction

Plants of the family Bromeliaceae, known as bromeliads, are especially adapted to develop phytotelmata, small bodies of water held in central structures formed by the characteristic arrangement of overlapping leaves in hollow rosettes (Fish, 1983).

Phytotelmata can be seen as aquatic microcosms since, despite the very small volume of rainwater collected in them, micro-communities have been found there which, relative to the size of the habitat have a very diverse range of taxa, which survive and interact as small ecosystems. Records exist of organisms of the following groups, simultaneously inhabiting the phytotelmata of a single bromeliad: Protozoa, Nematoda, Oligochaeta, copepoda, Cladocera, Ostracoda, Tardigrada, Insecta, Arachnida and Amphibia (Greeney, 2001; Kitching, 2000; Laessle, 1961; Picado, 1913). Around 470 species of aquatic animals have been recorded so far in these bromeliad tanks.

Such communities have been under study in several regions of the globe and the feature that has intrigued many researchers is the simultaneous occurrence of organisms of several trophic levels, in spite of the very limited space and low flux of energy (Kitching, 2000). Another aspect, very relevant to society at large, is the fact that phytotelmata shelter immature stages of mosquitoes such as Aedes aegypti Linnaeus, 1762 (Forattini et al., 1998; Cunha et al., 2002; Derraik, 2005), vector of dengue. On the other hand, phytotelmata communities are important as small repositories or refuges of biodiversity, particularly in habitats undergoing great changes (Armbruster et al., 2002; Noss, 1990), and also take part in forest maintenance by redistributing nutrients to the soil, as epiphytic bromeliads and their communities process nutrients before falling to the ground from the canopy.

Frank et al. (2004) warns the investigators that wish to work in the Neotropical region that they will encounter severe taxonomic problems. The effort to collect the specimens is small compared with the effort required to identify the specimens reliably to the species level. Four approaches have been suggested in attempts to unravel the mysteries of bromeliad fauna: brief reports of new discoveries, in-depth studies (behavioural or ecological or taxonomic) of a selected taxa, whole fauna inventories, and broad-scale hypothesis tests.

The immature stages of the non-biting midges (Diptera, Chironomidae) are commonly found in bromeliad water. Records of 12 species have been published: Antillocladius antecalvus Saether, 1981, Mesosmittia patrihortae Saether, 1985, Metriocnemus abdominoflavatus Picado, 1913, Ablabesmyia costaricensis Picado, 1913, Ablabesmyia ignobilis (Johannsen) Johannsen, 1932, Monopelopia caragata Mendes, Marcondes and Pinho, 2003, Monopelopia mikeschwartzi Epler, 1998, Monopelopia tillandsia Beck and Beck, 1966, Chirocladius pedipalpus , Picado 1913, Stenochironomus atlanticus Pinho and Mendes, 2005, Tanytarsus bromelicola Cranston, 2007, Tanytarsus confusa (Malloch), Miller, 1971 (Marcondes and Pinho, 2005; Cranston and Judd, 1987; Epler and Janetzky, 1998; Cranston, 2007; Pinho et al., 2005; Mendes et al. 2003).

In this study, phytotelmata, in a fragment of the Atlantic Rainforest in the until now unstudied Pau grande area of Magé district, were screened for the presence of Chironomidae larvae. The aim was to create an inventory of these dipterans in bromeliad water, as a contribution to the existing taxonomic information on the phytotelmata biota in the Neotropical region, with a view to preserving such communities.

2. Material and Methods

2.1. Study area

The town of Magé belongs to the metropolitan region of the State of Rio de Janeiro and is about 55 km from its capital city. The study area was a fragment of forest in the district of Pau Grande (22° 34' 48" S and 43° 09' 94" W), located at the edge of the conurbation of Greater Rio de Janeiro. This fragment is directly connected with some environmentally protected sites in the region, as well as with the Serra dos Órgãos National Park. Such remaining fragments of the Atlantic Rainforest form an ecological corridor that extends across almost the entire length of the state (Figure 1). The collection site is easily reached, but protected by an agreement between the local government and a drinks factory that uses the clean water from a reservoir nearby, formed by damming the River Piabetá. The study area is around 5000 m² of forest centred on this reservoir.


2.2. Sampling

Eight collections were carried out in the period form September 2006 to September 2007 at intervals of 1.5 months on average: September, October, December, February, April, June, July and September. Climatological data (temperature and rainfall) for this period were obtained from the Instituto Nacional de Meteorologia (INMET) automatic weather station in Xerém, RJ, Brazil.

An inventory was made of the phytotelmata found in 50 bromeliad specimens belonging to two species: 13 specimens of Neoregelia concentrica (Veloso) Smith and 37 of Aechmea nudicaulis (Linnaeus) Grisebach.

The Chironomidae samples were taken, on site, by aspiration of the water and organisms from the central tank of the bromeliad into a 60 mL syringe, through an attached silicone tube of 5.0 mm bore. The volume and pH of the water in the phytotelmata were measured. The collected fauna was fixed on site in 70% ethanol, labelled and taken to the laboratory for subsequent analysis.

Analysis of variance (ANOVA) was used to determine whether there were significant differences in water volume or pH between the phytotelmata of the two plant species.

In the laboratory, the material was sorted under a stereomicroscope and specimens of Chironomidae separated. These larvae were mounted in slides, as described by Schlee (1966), for later taxonomic identification with an optical microscope, with the aid of specialist keys such as those of Trivinho-Strixino (1995) and Epler (2001). The morphological terms adopted were those proposed by Saether (1980).

Selected examples of all Chironomidae material have been deposited in the Entomological Collection of the National Museum at the Federal University of Rio de Janeiro (UFRJ) in Rio, Brazil.

3. Results

Data on the mean air temperature and monthly rainfall in the period from September 2006 to September 2007 are shown in Figure 2. The lowest rainfall was recorded in October 2006 (0.2 mm) and the highest in June 2007 (283 mm). The mean temperature of the air varied from 20.6 °C in July 2007 to 27.4 °C in March 2007.


The data on the phytotelmata, sampled in the wet and dry periods (number of samples, volume, pH, numbers of larvae) in the bromeliads A. nudicaulis and N. concentrica, between September 2006 and September 2007, are displayed in Table 1. In the dry period, no significant difference was observed between the mean volumes of the sampled phytotelmata in the two species, while in the wet period there was a significant difference between these volumes (p = 0.001). On average, N. concentrica held 23.14 mL of water per phytotelmata and A. nudicaulis 15.03 mL.

The pH of the water in the phytotelmata varied between 5.0 and 7.5 among samples, with an average of 6.18 ± 0.61, but there was no difference between the samples from the two plants. The pH rose a little in the dry period, becoming slightly more neutral, but the difference between the two periods was not significant.

The Chironomidae data were assessed jointly for all the bromeliads sampled, irrespective of the plant species. Both the total number of Chironomidae larvae and the number of samples containing them were higher in the rainy period, in both of the bromeliads.

In all the phytotelmata sampled, three morphotypes of Chironomidae, belonging to three different subfamilies, were recorded: Polypedilum sp. with 9 specimens (Chironominae), Orthocladiinae gen. A, with 233 specimens (Orthocladiinae) and Monopelopia sp. with 51 specimens (Tanypodinae). Overall, the average number of Chironomidae per phytotelmata was 3.32 ± 2.62.

The variation in time of the number of Chironomidae larvae and the volume of water in the phytotelmata are displayed in Figure 3, together, and a clear correlation exists between the two sets of data, except for one collection, in April (fifth collection).


The relative abundance of the three Chironomidae taxa, calculated from their respective frequency in the phytotelmata samples taken at each collection, is shown in Figure 4. The organisms belonging to Orthocladiinae gen. A clearly dominated every collection, except the fourth. Hence, Orthocladiinae genus A can be considered a constant taxon (80%) in this habitat, while Monopelopia sp. (17%) and Polypedilum sp. (3%) are accidental taxa (Dajoz, 1973) (Figure 5).



The time profile of the absolute abundance of each taxon in phytotelmata of N. concentrica is shown in Figure 6, while the numbers in A. nudicaulis are presented in Figure 7. The variations in abundance of all taxa are quite similar in each bromeliad.



4. Discussion

The Atlantic Rainforest constitutes one of the richest sets of ecosystems on the planet as far as biological diversity is concerned. Most of the ecological studies on the invertebrates found in phytotelmata in this forest focus on the presence of the Culicidae, given the great importance to human health of some culicid species. The autoecology of Chironomidae in phytotelmata has rarely been studied and, in general, larvae of this family have been identified just at family level or recorded as belonging wide-range genera, such as Pentaneura (Cranston, 2007). Nevertheless, phytotelmata represent an important habitat for the survival of certain chironomid species, some of which may be as yet unrecorded.

This study reinforces the considerations of Frank et al., (2004) about the severe taxonomic problems in the Neotropical region and contributes with some of the approaches suggested.

The accurate taxonomic identification of the immature Chironomidae is only possible when the other stages are involved. However, although it was not possible to make such associations (attempts to rear the Chironomidae in the laboratory did not obtain the expected results), extensive literature searches in a library specialised in this group and conversations with other researchers, enabled us to classify the genera cited in this paper with taxonomic reliability.

Regarding the taxa recorded in this study, Monopelopia sp. and Polypedilum sp. have previously been recorded in phytotelmata. Thus, M. mikeschwartzi Epler,1998; M. tillandsia Beck and Beck, 1966 and M. caraguata Mendes et al., 2003 were recorded in Jamaica, US (Florida) and Brazil (Santa Catarina), respectively (Mendes et al., 2003), while Polypedilum cf.tritum was found by Epler and Janetzky (1998) in bromeliads in Jamaica and P. parthenogeneticum Donato and Paggi, 2008 was described recently in Argentina (Donato and Paggi, 2008).

The richness of the fauna in phytotelmata may be controlled by factors associated with the microhabitat in which the bromeliad grows (Araújo et.al., 2007). The plants examined in this study were well shaded, being situated beneath leafy trees. According to Lopez et al. (1998), in phytotelmata of bromeliads in restinga, the degree of exposure to the sun and not the amount of flooding of the substrate is the factor determining the taxonomic richness of the fauna. Those authors report that the species regularly inhabiting phytotelmata can successfully locate and colonise bromeliads, even in places with water bodies that hold much greater volumes of water than the plant tanks.

Accidental colonisation of the sampled phytotelmata with Polypedilum sp., recorded here, might have been due to the proximity of the nearby reservoir in which specimens of this genus have been collected (Sodré and Rocha, 2007).

This paper tried to study as deep as possible the ecological and taxonomical patterns of the chironomid's phytotelmata community inhabiting a fragment of Atlantic Rainforest in Rio de Janeiro state.

5. Conclusions

The abundance of Chironomidae in the phytotelmata of these bromeliads varies with monthly rainfall and the volume of water trapped in the plant. The chironomid larvae under study showed no preference for colonising either type of bromeliad.

Organisms belonging to the genus Monopelopia are apparently adapted to the phytotelmata habitat, corroborating previous accounts in the literature. This paper reports the first record of the genus Monopelopia in phytotelmata in the state of Rio de Janeiro.

The bromeliad phytotelmata found in the fragment of the Atlantic Rainforest studied represent an important habitat for conservation of the chironomid species recorded and make a contribution to the conservation of the biodiversity.

Acknowledgement - Thanks to Drª Sonia Lopes Fraga for her kindness and support throughout the development of this study. We also thank CAPES for the financial support through the provided scholarship.

Received November 11, 2009

Accepted October 28, 2009

Distributed August 31, 2010

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  • Publication Dates

    • Publication in this collection
      16 Aug 2010
    • Date of issue
      Aug 2010

    History

    • Received
      11 Nov 2009
    • Accepted
      28 Oct 2009
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