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. 2018 Feb;113(2):111–118. doi: 10.1590/0074-02760170225

Ecological characterisation and infection of Anophelines (Diptera: Culicidae) of the Atlantic Forest in the southeast of Brazil over a 10 year period: has the behaviour of the autochthonous malaria vector changed?

Julyana Cerqueira Buery 1, Helder Ricas Rezende 2, Licia Natal 3, Leonardo Santana da Silva 1, Regiane Maria Tironi de Menezes 4, Blima Fux 1, Rosely dos Santos Malafronte 3, Aloisio Falqueto 1, Crispim Cerutti Junior 1,+
PMCID: PMC5722266  PMID: 29236924

Abstract

BACKGROUND

In southeastern Brazil, autochthonous cases of malaria can be found near Atlantic Forest fragments. Because the transmission cycle has not been completely clarified, the behaviour of the possible vectors in those regions must be observed. A study concerning the entomological aspects and natural infection of anophelines (Diptera: Culicidae) captured in the municipalities of the mountainous region of Espírito Santo state was performed in 2004 and 2005. Similarly, between 2014 and 2015, 12 monthly collections were performed at the same area of the study mentioned above.

METHODS

Center for Disease Control (CDC) light traps with CO2 were set in open areas, at the edge and inside of the forest (canopy and ground), whereas Shannon traps were set on the edge.

FINDINGS

A total of 1,414 anophelines were collected from 13 species. Anopheles (Kerteszia) cruzii Dyar and Knab remained the most frequently captured species in the CDC traps set in the forest canopy, as well as being the vector with the highest prevalence of Plasmodium vivax/simium infection, according to molecular polymerase chain reaction techniques.

CONCLUSIONS

P. vivax/simium was found only in abdomens of the mosquitoes of the subgenus Nyssorhynchus, weakening the hypothesis that this subgenus also plays a role in malaria transmission in this specific region.

Key words: malária, Plasmodium vivax, Plasmodium simium, Anopheles

While highly prevalent in the Amazon Region, malaria also remains residually in the Atlantic Forest regions of southern and southeastern Brazil. In these regions, the disease is known as bromeliad malaria, since the vectors of the genus Anopheles reproduce in the tanks of Bromeliaceae, plants typical of this biome (Downs & Pittendrigh 1946). The presence of a few autochthonous human cases and asymptomatic infections, the spatial distance between the cases, and the low parasitaemia by microscopy provide evidence in opposition to the traditional transmission chain. It is believed that the cycle of Plasmodium species in the Brazilian Atlantic Forest is maintained by reservoirs of the parasite, in the forest or in the rural population, comprised of both simians and humans, asymptomatic or not; and studies have been conducted to test the validity of these assumptions (Curado et al. 1997, Duarte et al. 2006, Cerutti Jr et al. 2007, Meneguzzi et al. 2009, Rezende et al. 2009). Regarding the vector, in the state of Espírito Santo, Brazil, 26 species of Anopheles have been identified, indicating that this genus is commonly found in the region (Coutinho 1947, Andrade & Brandão 1957, Ferreira 1964, Natal et al. 2007, Sallum et al. 2008, Meneguzzi et al. 2009, Rezende et al. 2009, Silva et al. 2013). The vectors of greatest vectorial capacity and competence belong to the subgenus Kerteszia, mainly Anopheles (Kerteszia) cruzii, in the southern and southeastern Brazilian states (Meneguzzi et al. 2009). However, the species of anophelines involved in the dynamics of malaria transmission outside the Amazon Region vary according to environmental and epidemiological conditions (de Pina-Costa et al. 2014). Autochthonous cases of extra-Amazonian malaria, mostly caused by P. vivax, are found in moderately mountainous regions and are associated with agricultural activities performed by young men near the forest (Cerutti Jr et al. 2007). In addition to that, however, there is one more malaria transmission site in Espírito Santo. The northern region of the state is a frequent scenario of disease outbreaks. These outbreaks come from introducers from the Amazon Region. Records of P. falciparum autochthonous malaria in Espírito Santo are related to these outbreaks. In the cases detected at the site of each outbreak, although they are also called autochthonous cases by epidemiological definition, the disease is brought in from the outside, unlike what is observed in the Atlantic Forest. Therefore, at our present level of knowledge, it is not possible to recognise the occurrence of symptomatic malaria caused by P. falciparum in an Atlantic Forest environment, as it is for cases caused by P. vivax. States such as São Paulo, Santa Catarina and Espírito Santo are covered by dense Atlantic Forest regions (IESB 2007). Among them, Espírito Santo has recorded the largest number of bromeliad-malaria cases in recent years. The biome in question is very humid, with abundant rainfall and vegetation that favours the reproduction of anophelines. In addition, bromeliad-malaria is beginning to be used as a biological marker of human activities within these forests (Gomes et al. 1985, Rezende et al. 2013). Rezende et al. (2009) found anopheline behaviour similar to that expected, based on the literature, in Valsugana Velha, Santa Teresa municipality: a high prevalence of A. (K.) cruzii was reported in a mountainous region of the Atlantic Forest, in an endemic area of the disease in the state of Espírito Santo. However, regarding the hypothesis of a typical transmission model of zoonosis in this scenario, this model would require a stable and constant vectorial behaviour. Such behaviour, therefore, must be repeatedly assessed in order to establish transmission characteristics over the course of years.

MATERIALS AND METHODS

Description of the study site - The study was performed in the rural area of the municipality of Santa Teresa, which is located approximately 78 km from Vitória, in the state of Espírito Santo (ES), Brazil. The permanent trapping station is in Valsugana Velha (19°57′58.4″ S, 40°34′45.2″ W), where cases of residual malaria from Atlantic Forest systems were recorded in the study by Cerutti Jr. et al. (2007) (Fig. 1).

Fig. 1. political map of the municipality of Santa Teresa, Espírito Santo, Brazil, highlighting the rural community where the collections were performed.

Fig. 1

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Source: Instituto Jones dos Santos Neves, 2013.

Collection of anophelines - Hourly collections of anophelines were conducted at a permanent trapping station located in the bromeliad malaria transmission area. These collections were performed one day each month for one year, from June 2014 to May 2015, totalling 12 collections. Two capture methods were used: (i) Center for Disease Control (CDC) light traps with CO2 (Gomes et al. 1985) that were set in open areas (peridomiciliary environment = PD), at the edge of the forest (canopy and ground) and inside the forest (canopy and ground); and (ii) Shannon traps (Bustamante & Pires 1951), set at the edge of the forest.

The five CDC traps were set simultaneously, two of them at 15 m from the ground in the canopy (on the edge and inside the forest), two at one metre from the ground (at the edge and inside the forest), and one at the border between the forest and the area close to dwellings. The collections lasted for 12 h, with the traps placed at night (6:00 PM) and removed in the morning (6:00 AM). For the Shannon traps, the insects were captured during the first 4 h after sunset (6:00 PM to 10:00 PM) each month.

Storage and identification of insects - The specimens were stored in tubes containing isopropanol and later identified using the identification keys proposed by Consoli and Lourenço-de-Oliveira (1994). Identification was performed by a team from the Entomology and Malacology Centre of Espírito Santo (Núcleo de Entomologia e Malacologia do Espírito Santo - NEMES/ES).

Molecular techniques - The DNA for the detection of Plasmodium species was obtained from the thorax, abdomen or entire mosquito of the mosquito groupings in pools (maximum of 10 samples/pool), depending on the subgenus of the specimens. Those of the subgenus Nyssorhynchus were sectioned (separated pools of thoraxes and abdomens), whereas those of the subgenus Kerteszia were processed in whole. The same extraction kit (DNeasy Blood & Tissue Kit, Qiagen, Germany) was used, following the manufacturer's instructions. Each pool included females of the same species, collected in the same type of trap, on the same date. The presence of P. vivax/simium or P. malariae in the pools was detected using the nestedpolymerase chain reaction (PCR) protocol described by Kimura et al. (1997) and modified by Win et al. (2002). The target was the gene encoding the 18S ribosomal subunit. The amplification products were analysed by electrophoresis in 2% agarose gel under ultraviolet light. In positive cases, 100-bp fragments were amplified.

Statistical analysis - To determine the importance and distribution of the various Anopheles species, analyses of diversity, dominance and abundance were performed using Shannon's diversity index (H′) and Simpson's dominance index (D). In the various comparisons, the level of significance was set at 5%. Bivariate Spearman correlation calculations were used to determine the relationship between anopheline capture, temperature and rainfall [data provided by the Capixaba Institute of Research, Technical Assistance and Rural Extension (Instituto Capixaba de Pesquisa, Assistência Técnica e Extensão Rural - INCAPER)], also at a level of 5%.

Ethical standards - During the collection process, no harm was inflicted to the environment. The team members wore long clothing, gloves and hats with head nets to avoid anopheline mosquito bites. Boots were also used to prevent bites by venomous animals. A license to capture arthropod insects was obtained via the SISBIO/Chico Mendes Institute (ICMBio/IBAMA/MMA) under No. 19227-1.

RESULTS

A total of 1,414 specimens were captured, resulting in a set of 13 species. The largest number of specimens was collected in April 2015 (341), and the smallest number of specimens in March 2015 (5). In all collections, there was a predominance of A. (K.) cruzii, totalling 1,044 of the 1,414 mosquitoes captured (Table I). The trap in which most mosquitoes were captured was the CO2-baited CDC trap placed in the canopy, in which A. (K.) cruzii was also predominant (Fig. 3).

TABLE I. Percentage of anopheline species found between June 2014 and May 2015 at the permanent trapping station in Santa Teresa, Espírito Santo, Brazil.

Species Number (%)
Anopheles (Kerteszia) cruzii 1044 73.8
A. (Nyssorhynchus) strodei 103 7.3
A. (N.) triannulatus 84 6.0
A. (N.) evansae 52 3.7
A. (K.) homunculus 39 2.7
A. (N.) galvaoi 29 2.0
A. (N.) albitarsis 17 1.2
A. (N.) parvus 07 0.5
A. (A.) mediopunctatus 05 0.4
A. (N.) rangeli 03 0.2
A. (N.) lanei 01 0.1
TOTAL 1414 100
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Fig. 3. percentage of species captured per trap, from June 2014 to May 2015, at the permanent trapping station in Santa Teresa, Espírito Santo, Brazil.

Fig. 3

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Climate - The months of November 2014, September 2014, and April 2015 showed the highest capture frequencies (Fig. 4). There was no simultaneous capture of all species in the monthly collections, and all species were absent for at least 1 month during the total collection period. A. (K.) cruzii was not captured only in June 2014 and March 2015 (Fig. 4). In fact, those were the only months in which A. (K.) cruzii ceased to be the predominant species and was replaced with A. (Nyssorhynchus) strodei and A. (Nyssorhynchus) triannulatus, respectively.

Fig. 4. species captured each collection month, from June 2014 to May 2015, at the permanent trapping station of Santa Teresa, Espírito Santo, Brazil.

Fig. 4

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A negative trend was observed for the correlation between the number of anophelines of the subgenus Nyssorhynchus and the temperature, although without statistical significance (r = - 0.04, p = 0.89). Additionally, a positive trend was observed for the correlation between the number of anophelines and rainfall (r = 0.17, p = 0.59) but also with no statistical significance. For the subgenus Kerteszia, the correlation between capture frequency and temperature (r = -0.004, p = 0.99) or rainfall (r = -0.13, p = 0.68) revealed negative coefficients but with no statistical significance. The monthly average temperature and the rainfall in Valsugana Velha are shown in Fig. 5.

Fig. 5. temperature and rainfall data in Santa Teresa, Espírito Santo, Brazil, between June 2014 and May 2015.

Fig. 5

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Spatial distribution - A. (N.) strodei and A. (N.) triannulatus were more frequently captured in the Shannon traps, and A. (K.) cruzii was captured more frequently in the CO2-baited CDC traps (Fig. 3) located in the tree canopy. Simpson's dominance index (D) reveals that dominance in the Shannon trap (D1 = 0.227) was greater than the dominance of individuals collected in the CO2-baited CDC trap (D2 = 0.172) (p < 0.02), both at the forest edge.

Based on Shannon's diversity index (H′), the diversity of anophelines collected in the Shannon trap (H′2 = 1.866) was higher compared to that of the anophelines collected in the CDC trap at the forest edge, near the dwellings (H′1 = 1.734) (p = 0.004). A. (N.) strodei was captured in larger numbers at forest edge areas, followed by A. (N.) triannulatus. A. (N.) lanei and A. (N.) rangeli were captured only in the CO2-baited CDC trap located near the dwellings, whereas A. (K.) homunculus was only captured in the CDC traps set in the tree canopy.

Presence of Plasmodium in the anophelines ( Table II ) - Of the total pool of specimens investigated, 13 were positive for P. vivax/simium (Fig. 2). Of these, 10 belonged to the species A. cruzii, and three were abdomens that belonged to specimens of the subgenus Nyssorhynchus. As shown in Table II, most of the mosquitoes with Plasmodium DNA were A. cruzii, captured in CO2-baited CDC traps located in the tree canopy. Fig. 6 shows the monthly distribution of captured mosquitoes in which P. vivax/simium was found. P. malariae infection was not detected.

TABLE II. Species, traps and collection dates for Plasmodium vivax/simium-positive mosquitoes at the permanent trapping station in Santa Teresa, Espírito Santo, Brazil.

Sample Species Trap Date
260a * A. (Nyssorhynchus) lutzii Shannon September 2014
279 A. (Kerteszia) cruzii CDC canopy August 2014
343 A. (K.) cruzii CDC canopy August 2014
479 A. (K.) cruzii CDC canopy October 2014
485 A. (K.) cruzii CDC canopy October 2014
494a * A. (N.) evansae Shannon October 2014
632 A. (K.) cruzii CDC ground November 2014
633 A. (K.) cruzii CDC canopy November 2014
868 A. (K.) cruzii CDC canopy February 2015
1142 A. (K.) cruzii CDC canopy April 2015
1144 A. (K.) cruzii CDC canopy April 2015
1248 A. (K.) cruzii CDC canopy April 2015
1294a * A. (N.) strodei CDC near dwellings May 2015
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*

a: abdomen.

Fig. 2. ethidium bromide-stained agarose gel, photographed using the Alpha Imager software, with 13 samples of pools of Plasmodium vivax/simium-positive anopheline females.

Fig. 2

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Fig. 6. chronological distribution of Plasmodium vivax/simium-infected anopheline females captured in the permanent trapping station in Santa Teresa, Espírito Santo, Brazil.

Fig. 6

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DISCUSSION

Evidence of residual bromeliad malaria in the south and southeast Brazilian Atlantic Forest regions arose after control measures implemented by the government had eliminated transmission in flat areas exploited by humans (Barata 1998, MS 2015). As residual foci remained in the eradication areas, bromeliad malaria, or malaria of the Atlantic Forest systems, began to be studied with more intensity in the 1980s and 1990s (Duarte et al. 2013). With a more consistent understanding of vector ecology and outbreak epidemiology, more evidence has emerged in favour of behaviour consistent with a zoonosis. The zoonosis hypothesis presupposes a concomitant existence of simian malaria. Such an existence has been verified in the past (Duarte et al. 2008), but its prospective evaluation demands extremely complex logistics. Therefore, the evaluation of vector behaviour favourable to enzootic transmission is more feasible and may provide indirect evidence of the presence of the infection among monkeys and of its source of occurrence in human cases. Given the requirement of stable and constant vector behaviour for the maintenance of simian malaria, follow-up studies of the endemic regions are necessary. In addition, according to Marrelli et al. (2007), the entire Atlantic Forest territory that survived deforestation must be carefully monitored due to environmental changes and the possibility of maintaining the infection cycle given the high number of asymptomatic individuals who can act as reservoirs of the parasite in those regions.

In the present study, A. (K.) cruzii still prevailed as the main vector found at the Valsugana Velha trapping station. Between 2004 and 2005 (Rezende et al. 2009), 61.2% of the 2,290 anophelines collected belonged to this species. In 2014 and 2015, 73.8% of the 1,414 anophelines captured were A. (K.) cruzii. Therefore, an increase in the proportion of the main vector of bromeliad malaria was observed in the local fauna. Older studies such as those of Deane (1988), and more recent studies such as those of Duarte et al. (2013), Neves et al. (2013) and Kirchgatter et al. (2014) have previously demonstrated the magnitude of the presence of this species in Atlantic Forest regions with preserved native forest.

The distribution of A. (K.) cruzii when moving from the inside to the edge of the forest has also remained the same over time. As Rezende et al. (2009) described in 2004 and 2005, the anophelines of this species appeared mostly in the tree canopy inside the forest, whereas the numbers decreased drastically in the traps that were set closer to the forest edge and the dwellings. The anopheline fauna was dominated by species such as A. (N.) strodei and A. (N.) triannulatus closer to human-occupied areas. In São Paulo, between 2009 and 2011, this trend was also detected when comparing anthropic and wild areas in the town of Parelheiros. There, 438 A. (K.) cruzii were recorded in a certain anthropic area and 4,832 in the wild area (Duarte et al. 2013).

The absolute predominance of A. (K.) cruzii in the canopy, observed in the present study, indicates a nonsynanthropic behaviour (Forattini et al. 1990) and reinforces its role in the transmission of simian malaria. However, despite being present mostly in the canopy, some specimens were found in the CO2-baited CDC traps set in the ground and in the Shannon traps, which points to the possibility of these vectors descending from their preferential site in the canopy, at which time they could incidentally transmit the parasites to humans. The presence of these specimens reinforces the hypothesis that bromeliad malaria is maintained in the region by means of simian infection. The fact that humans are in the forest and that A. (K.) cruzii comes down from the canopy to feed creates the conditions for Plasmodium specimens originating from the simians in the canopy to infect humans.

The morphometric diagnosis studies of Lorenz et al. (2012) showed a differentiation between A. (K.) cruzii and A. (K.) homunculus not predicted in the study of Rezende et al. (2009). However, only 39 A. (K.) homunculus were captured during the collection period between 2014 and 2015, against 1,045 duly identified A. (K.) cruzii.

One of the limitations of this study was that species identification was made only on a morphological basis. To minimise the possibility of misidentification, we improved the accuracy through evaluation by experienced entomologists and through a double identification performed in cases of doubt.

Unexpectedly, the season during which most mosquitoes were captured was not the summer. Interestingly, the seasons with milder weather had the largest capture rates. For example, the most successful captures occurred in the months of September 2014 and April 2015. This result corroborates the study of Rezende et al. (2009), who suggested the adaptation of anophelines to mild environments. There was also a high number of specimens collected in November 2014. The mean rainfall at that time was the highest of that year (mean of 207.6 mm/month), and the temperature was mild on collection day (ranging from 19.7 to 21.3°C). That month, the “rain” factor may have triggered an increase in the mosquito population.

In this study, 13 pools of mosquitoes were positive for P. vivax/simium. In 2004 and 2005, 10 pools of anophelines infected by the same species of the parasite were obtained (Rezende et al. 2009). However, unlike 10 years ago, the PCR reactions for the 2014 and 2015 collections did not show infection in the thorax of mosquitoes of the subgenus Nyssorhynchus. The infective form should reach the salivary gland of the anopheline for infection to occur. Thus, the separation into thorax and abdomen during the experiments reinforces evidence of the participation of other vector species in the transmission chain. Because Kerteszia is a subgenus of a known vector, there was no separation of the body to perform the experiments, as occurred in mosquitoes of the subgenus Nyssorhynchus, to assess the possibility that these mosquitoes participate in the transmission chain. Since no infection was detected in the Nyssorhynchus specimens thoraxes, unlike 10 years ago, Nyssorhynchus species may have stopped playing the role of secondary vector and A. (K.) cruzii may currently be the only bromeliad malaria vector in this area. The progressive exploitation of the rural and forest environment by the local inhabitants may have led to greater spatial distances between the transmission events and the anthropic environment, where Nyssorhynchus species have greater dominance. In these conditions, given the A. (K.) cruzii dominance, Nyssorhynchus species does not have the opportunity to become infected. However, humans venture into the forest to clean the river springs or to gather firewood and thus acquire the disease. Once they return to their homes, they likely transmit the parasites to the Nyssorhynchus specimens near their dwellings.

Infected A. (K.) cruzii were collected in CO2-baited CDC traps in the tree canopy inside the forest and in one CO2-baited CDC trap located near the ground, at a height of one metre. This fact reinforces the idea that infections can occur in both habitats as a result of the acrodendrophilic behaviour with eventual descent to lower heights, where they can feed on non-usual hosts. This fact also reinforces the possibility of the disease being a zoonosis in regions such as Valsugana Velha, in Santa Teresa, ES.

Regarding the Shannon's dominance index (H′), there was greater dominance in the Shannon trap than in the CO2-baited CDC trap, both at the forest edge.

Regarding Simpson's diversity index (D), the diversity of anophelines collected with the Shannon trap was also higher than that observed in the CO2-baited CDC trap in the same habitat. The placement of the trap near the body of water, where there were Nyssorhynchus species breeding sites, would justify the greater diversity.

These data corroborate a study conducted in the same region and published in 2013 (Rezende et al. 2013), when greater dominance and diversity of anophelines were observed in an anthropic environment with the presence of malaria. These findings support the role of human occupation in the determination of both anopheline distribution and behaviour, since both indices show higher values in collections performed in an environment closer to human dwellings.

The study shows that there was little change in vector behaviour in the region studied. A. (K.) cruzii remains the mosquito with the higher evidence of natural infection in Valsugana Velha, and mosquitoes of the subgenus Nyssorhynchus do not seem to participate in the transmission chain. The acrodendrophilic behaviour of A. (K.) cruzii, particularly those infected, strengthens the hypothesis that the presence of P. vivax/simium in these specimens arises from blood feeding in animals that live in the tree canopy, such as simians.

ACKNOWLEDGEMENTS

To the State Health Department of Espírito Santo and the Entomology and Malacology Centre of Espírito Santo/SESA, for the logistical support and supply of equipment in the field; to Claudiney Biral dos Santos, for technical support; Filomena EC Alencar, Creuza Rachel Vicente, Marcelo Urbano Ferreira, Priscila Thihara Rodrigues and Lais Camoese Salla, for the critical reading of the manuscript; the owners of the Recanto da Preguiça farm, for allowing sampling at that site; and the Capixaba Institute of Research, Technical Assistance, and Rural Extension (INCAPER/ES), for providing the rainfall and temperature data.

Footnotes

Financial support: FAPES, Programa de Pesquisa para o Sistema Único de Saúde do Ministério da Saúde (grant No. 65834119/2014).

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