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Article

Zoonotic Malaria Risk in Serra Do Mar, Atlantic Forest, Brazil

by
Marina E. O. Rangel
1,
Ana Maria R. C. Duarte
2,3,
Tatiane M. P. Oliveira
1,
Luis F. Mucci
3,
Ana Carolina Loss
4,
Jose R. Loaiza
5,
Gabriel Z. Laporta
6,* and
Maria Anice M. Sallum
1
1
Department of Epidemiology, School of Public Health, University of São Paulo, São Paulo 01246-904, SP, Brazil
2
Laboratory of Protozoology, Institute of Tropical Medicine, School of Medicine, University of São Paulo, São Paulo 05403-000, SP, Brazil
3
Institute Pasteur, State Secretary of Health of São Paulo, São Paulo 01311-000, SP, Brazil
4
Graduate Program in Biological Sciences, Federal University of Espírito Santo, Vitória 29075-710, ES, Brazil
5
Institute of Scientific Research and High Technology Services of Panama (INDICASAT AIP), Panamá 0843-01103, Panama
6
Graduate Program in Health Sciences, FMABC University Center, Santo André 09060-870, SP, Brazil
*
Author to whom correspondence should be addressed.
Microorganisms 2023, 11(10), 2465; https://doi.org/10.3390/microorganisms11102465
Submission received: 28 August 2023 / Revised: 22 September 2023 / Accepted: 26 September 2023 / Published: 30 September 2023
(This article belongs to the Special Issue Ecology and Evolution of Forest Malaria)

Abstract

:
Here, the main goal is to assess natural infections of Plasmodium spp. in anophelines in a forest reserve from the same region where we previously found a surprisingly high rate (5.2%) of plasmodia infections (n = 25) in Kerteszia mosquitoes (N = 480) on the slopes of Serra do Mar, Atlantic Forest, Brazil. The mosquito collection sampling was carried out at the Legado das Águas Forest Reserve using CDC light traps and Shannon traps at night (5–10 pm) in 3-day collections in November 2021 and March, April, May, and November 2022. The captured specimens were morphologically identified at the species level and had their genomic DNA extracted in pools of up to 10 mosquitoes/pool. Each pool was tested using 18S qPCR and cytb nested PCR plus sequencing. A total of 5301 mosquitoes, mostly belonging to the genus Kerteszia (99.7%), were sampled and sorted into 773 pools. Eight pools positive for Plasmodium spp. were identified: four for Plasmodium spp., one for P. vivax or P. simium, one for P. malariae or P. brasilianum, and two for the P. falciparum-like parasite. After Sanger sequencing, two results were further confirmed: P. vivax or P. simium and P. malariae or P. brasilianum. The minimum infection rate for Kerteszia mosquitoes was 0.15% (eight positive pools/5285 Kerteszia mosquitoes). The study reveals a lower-than-expected natural infection rate (expected = 5.2% vs. observed = 0.15%). This low rate relates to the absence of Alouatta monkeys as the main simian malaria reservoir in the studied region. Their absence was due to a significant population decline following the reemergence of yellow fever virus outbreaks in the Atlantic Forest from 2016 to 2019. However, this also indicates the existence of alternative reservoirs to infect Kerteszia mosquitoes. The found zoonotic species of Plasmodium, including the P. falciparum-like parasite, may represent a simian malaria risk and thus a challenge for malaria elimination in Brazil.

1. Introduction

Outside the Amazon region, Plasmodium transmission mainly occurs in forest remnants across the Brazilian Atlantic Forest. In November 2012, we found Kerteszia and Nyssorhynchus mosquitoes infected with a forested Plasmodium falciparum-like parasite on the slopes of Serra do Mar, Brazilian Atlantic Forest [1]. These samples were further tested in two other laboratories. An assay amplifying a cytochrome b (cytb) fragment carried out in Brazil further confirmed the P. falciparum-like parasite identified in the mosquitoes Nyssorhynchus strodei and Kerteszia cruzii sampled in Serra do Mar in 2012 [1,2]. A USA-based laboratory, which participates in the WHO testing program to evaluate the performance of labs performing the diagnosis of malaria, further confirmed the P. falciparum-like parasite in Ke. cruzii (sample M267) from Tapiraí County (Serra do Mar) using 18S rRNA gene and apical membrane antigen-1 (AMA-1) gene qPCR assays (Figure S1). The AMA-1 primer and probe set used in the latter assay was specific to P. falciparum; only the African apes Plasmodium reichnowi and Plasmodium gaboni could cross-react, both of which are closely related to P. falciparum (Figure S1). This prompted us to develop a hypothesis on the forested P. falciparum-like parasite in Serra do Mar, which is either an isolated emergence having genetic similarity with the African parasite or the product of an evolutionary event known as the spillover–spillback mechanism [2,3]. This mechanism seems to be subjacent with the high prevalence of Plasmodium simium and Plasmodium brasilianum among platyrrhine (New World) simians in South and Central America [4,5,6]. Both P. simium and P. brasilianum—which are genetically indistinguishable from Plasmodium vivax and Plasmodium malariae—are zoonotic plasmodia that cause simian malaria in humans in Brazil [3,7,8,9,10]. Clinical infections of zoonotic Plasmodium spp. in the Atlantic Forest can be as severe as human malaria [10], particularly if they go undiagnosed.
Zoonotic infections are accidental transmissions of plasmodia to humans from simian reservoirs in the Atlantic Forest [11,12]. Plasmodium brasilianum was experimentally shown to infect human volunteers after a caged colony of Anopheles freeborni had contact with the infected simian reservoir Ateles geoffroyi in Panama [13]. Indigenous people naturally carry P. brasilianum in the Yanomami Indigenous Reserve, Roraima State, Brazil [14]. Plasmodium simium was first found in a reported human infection in São Paulo, Brazil in the 1960s [15]. More recently, it has been discovered that the majority of clinical non-imported malaria cases are of simian origin, particularly due to P. simium in the Atlantic Forest [10]. These plasmodia are transmitted inside the forest by sylvatic anophelines, mainly Kerteszia cruzii [16]. This abundant vector species depends on canopy bromeliads (Bromeliaceae) to develop in the immature stages [11]. Kerteszia females are opportunistic and can seek non-human primates, birds, and other animals in the canopy as well as humans and other mammals at ground level [16]. Mathematical modeling has shown that simian malaria transmission to humans is more likely to occur at forest edges, where vector displacement from the canopy is greater, simian species are present, and biodiversity effects that regulate vector abundance are lower [17].
Both P. simium and P. brasilianum could result from a spillover–spillback process, in which malaria-infected humans introduced Old World lineages of P. vivax and P. malariae into native non-human primates [4,5]. After local speciation, they became zoonotic but remained genetically indistinguishable from their human malaria counterparts [2,4,5,6]. The mitochondrial lineages of P. vivax and P. simium have been found in non-human primates and humans in the Atlantic Forest, but not in the Amazon, which suggests a recent human-to-monkey transfer [18]. This is supported by the low diversity levels of P. simium lineages in New World monkeys compared with P. vivax lineages from humans living in Brazil [18]. New World P. simium and P. vivax PVS47 gamete surface protein sequences cluster together but are non-convergent with those from the Old World, probably due to local vector selection and speciation [4]. Plasmodium brasilianum and P. malariae present identical 18S gene sequences, but they share human and non-human hosts in South America and Africa [6,14,19]. This further demonstrates their lack of genomic distinction but considerably high host-transfer plasticity [6,19]. The evolutionary origins of P. malariae and P. brasilianum remain disputed [20].
The epidemiological importance of Ke. cruzii acting as a malaria vector in Brazil dates back to the 1940s [21]. Clinical cases were attributed to its high vectorial capacity for human malarias [21]. As clinical cases became more sparsely distributed in the 1980s, zoonotic malaria fitted as an alternative hypothesis [11,22]. In 2015–2016, it was suggested that every human vivax malaria case locally acquired in the Atlantic Forest may be due to a P. simium zoonotic infection [10]. More recently, it was shown that New World Alouatta simians (platyrrhine howler monkeys) can contain sufficient P. simium gametocyte density in the blood to infect mosquitoes [23]. In addition, reports showed that 18S and cytb gene sequences of P. falciparum in Kerteszia mosquitoes [1,2] and seroprevalence against P. falciparum circumsporozoite proteins in howler and other New World monkeys [24] posed a further zoonotic malaria risk due to Plasmodium spp. in the Atlantic Forest.
Here, the main goal was to analyze plasmodial natural infection in anophelines in a private and well-preserved forest reserve on the slopes of Serra do Mar in the Brazilian Atlantic Forest from 2021 to 2022. In 2012, we found a surprisingly high infection rate (5.2%) of zoonotic malarias among Kerteszia mosquitoes [1]. As we knew in advance that the reemergence of the yellow fever virus in Brazil from 2016 to 2019 decimated most of the Alouatta populations throughout the Atlantic Forest [25,26], the study hypothesis was that the 2021–2022 zoonotic malaria infection rate in Kerteszia should be zero (0%) as supported by the absence of Alouatta monkeys [25,26] to locally infect mosquitoes [23]. Alternatively, if this zoonotic malaria risk was in any estimate greater than zero, other simian reservoir species might be occurring, or human hosts may sustain human-to-human zoonotic malaria transmission in the studied area.

2. Materials and Methods

2.1. Study Area and Sampling

The Legado das Águas Forest Reserve (Water Legacy – Votorantim Reserve) is the largest private forest reserve in Brazil (31 thousand hectares) and together with other governmental forest reserves comprise the Atlantic Forest Biosphere Reserve (Figure 1). This reserve undertakes programs of ecotourism, forest conservation, wildlife monitoring, native plant nursing, scientific research, training and education, and citizen science (the One Health program). Altogether, this reserve has received >10 awards from different sources recognizing its contribution to the mission of the national conservation of the Atlantic rainforests.
A total of 13 locally acquired malaria cases in humans were officially reported from 2007 to 2022 [27]. These cases were not related to imported malaria; their causal interpretation was zoonotic malaria. In November 2012, we carried out a mosquito collection sampling near the Alecrim Waterfall (Figure 1) and found 22 plasmodium-infected Ke. cruzii out of 207 captured (10.6%) [1]. In December 2018, a researcher from a medical school was leading nocturnal collections of sand flies on the Cambuci Suspended Trail (Figure 1) and acquired malaria. This case was officially reported as P. vivax in the state of São Paulo [27]. In January 2019, we captured and tested 1536 Ke. cruzii from the Alecrim Waterfall and Cambuci Suspended Trail sites (Figure 1). These samples were tested in the previously mentioned USA-based laboratory, but all the tests were negative for Plasmodium spp. (Table S1). In March 2022, a visitor who was participating in ecotourist activities on the December Waterfall Trail (Figure 1) was diagnosed with malaria. This case was officially reported as P. vivax in the state of São Paulo [27].
In the present work, we undertook a comprehensive sampling to further test mosquito infectivity for the presence of Plasmodium spp. in three sites in the Legado das Águas Forest Reserve (Figure 1). The December Waterfall Trail is a 3 km forested trail along with natural pools, rivers, and a 15 m high waterfall. The Cambuci Suspended Trail is a 2 km forested trail over a suspended wooden structure on a steep slope. The Tapir Creek Village is a 100-year-old local community composed of small houses surrounded by a forest and inhabited by 15–20 native residents. Mosquito sampling was carried out in 3-day collections (day 1, Cambuci Suspended Trail; day 2, December Waterfall Trail; and day 3, Tapir Creek Village) at 5–10 pm with 3 Shannon traps/day and 3 canopy CDC light traps/day in 5 periods (November 2021 and March, April, May, and November 2022). The collection period of August–September 2021 was a pilot study when we tested collection methods (Shannon and CDC traps), sampled mosquito fauna from the Cambuci Suspended Trail, and visited other sites which were not considered herein.
Mosquito species were determined based on female adult morphology using standard taxonomic keys [28] based on the nomenclature found in [29]. After species identifications, female specimens were separated into pools in microtubes that were labeled with information from field work as collection site, collection method, collection time, collection day, and so on. Storage was provided to these samples in −20 °C freezers at the University of São Paulo.

2.2. DNA Extraction

Species-identified females were separated into pools of up to 10 specimens/pool in 1.5 mL tubes and stored at −20 °C until DNA extraction. The only exception was during the third collection period (March) because we knew in advance that a case of malaria had been identified from a visitor who was in the studied region during Carnival (26–28 February and 1 March). We decided to individually test mosquitoes sampled in March to increase the chances of Plasmodium spp. detection and sequencing.
The DNA extraction from pools of whole mosquitoes was implemented using a salting-out method [1]. Details regarding this method can be found elsewhere [1]. This approach was carried out at the School of Public Health of the University of São Paulo.
The extracted DNA was stored (−20 °C) until the real-time qPCR of 18S and conventional PCR of cytb plus Sanger sequencing were accomplished. These approaches were undertaken at the Institute of Tropical Medicine of the University of São Paulo.

2.3. Real-Time qPCR Assay

The extracted DNA was first cleaned with RNase enzyme treatment and then tested in real-time with 18S qPCR amplifying a fragment of 157–165 bp [30]. We used a Mix TaqMan Universal (Thermofisher Scientific, Waltham, MA, USA) and genus- and species-specific primers and probes for Plasmodium spp., P. vivax or P. simium, P. malariae or P. brasilianum, and P. falciparum [31]. In each testing, we had 3 μL of DNA (0.3–60 ng/UL), a primer concentration of 0.15 μM and a probe of 0.05 μM, followed by qPCR conditions: 50 °C for 2 min and 95 °C for 10 min plus 50 amplification cycles (95 °C for 15 s and 60 °C for 1 min). Positive controls were P. vivax, P. falciparum, or P. malariae DNA. Negative control was ultrapure water.

2.4. Nested PCR plus Sequencing

Positive samples in the real-time qPCR samples were further analyzed with a nested PCR assay amplifying a ∼402 bp cytb fragment [32,33]. The first reaction was carried out with a DreamTaq PCR Master Mix (Thermofisher Scientific™, Waltham, MA, USA). We used 5 µL of DNA and 1 µL of each primer (Pf_F3700 and Pf_R4615), resulting in a 915 bp fragment [32,33]. For the second reaction, we used a DreamTaq PCR Master Mix (Thermofisher Scientific™, Waltham, MA, USA) with the 4 µL PCR product from the first reaction and 1 µL for each primer (Pf_F3700 and Pf_R4615), resulting in a ∼402 bp fragment [32]. Conditions for both assays were as follows: 1 cycle of denaturation at 94 °C for 5 min, 30 cycles of denaturation at 94 °C for 15 s, and annealing at 55 °C (the primers’ first pair) or 52 °C (the primers’ second pair) for 15 s with a final extension for 2–5 min at 72 °C. PCR products were observed in agarose gel (Sigma-Aldrich, Saint Louis, MO, USA) with a concentration of 3.0% in 1x TBE buffer (0.09 M Tris-borate, 0.002 M EDTA). A 50 bp molecular weight marker was used and the gel was visualized under ultraviolet light. Fragments having the expected sizes (∼402 bp) were forwarded to a Sanger sequencing company (Genomic Engenharia Molecular, São Paulo, SP, Brazil) [2].

2.5. Phylogenetic Analyses

The cytb sequences generated herein were compared with databases available using the BLAST tool (Basic Local Alignment Search Tool; https://blast.ncbi.nlm.nih.gov, accessed on 29 September 2023) on GenBank (https://www.ncbi.nlm.nih.gov/genbank/, accessed on 29 September 2023). These cytb sequences were aligned on the Geneious 6.1 program (Biomatters, Auckland, New Zealand) along with 16 other Plasmodium sequences available from GenBank, including Plasmodium gallinaceum and Plasmodium relictum as outgroups (~363 bp). Phylogenetic reconstruction with maximum likelihood and bootstrapping in the RAxML program on the CIPRES platform (https://www.phylo.org/portal2, accessed on 29 September 2023) was implemented. GTR+G was the molecular evolution model assumed.

2.6. Data Analysis

The minimum infection rate (MIR) was estimated as follows: MIR = x n × 100, where x is the number of positive pools and n is the total number of mosquitoes tested. This approach has been used previously [34]. The main assumption was that a positive pool had at least one Plasmodium-infected mosquito. For the collections in the third period (March), any positive result meant a natural infection in a single mosquito.

3. Results

3.1. Sampled and Tested Specimens

A total of 5301 anophelines were captured from the selected sampling sites (Figure 1). A total of 80 h of sampling efforts (3 days/site × 5 h × 5 periods = 75 h + 5 h in the pilot study/one site) resulted in an average of 66 anophelines captured per hour. The majority were Ke. cruzii (n = 5133; 97%) or Kerteszia mosquitoes (n = 5285; 99.7%) and a few belonged to other species (An. lutzii, An. medialis, and An. fluminensis). Shannon traps were the most efficient (5226 captured anophelines), while CDC light traps captured 75 anophelines (Table 1). We sampled 108 mosquitoes at the Cambuci Suspended Trail site from August to September 2021, which was a pilot study collection. From November 2021 on, we collected samples at all three collection sites. The number of mosquitoes sampled varied as follows: 2746 in November 2021, 184 in March, 1209 in April, 162 in May, and 892 in November 2022.

3.2. Real-Time qPCR Assay

Out of the 773 pools tested, real-time qPCR resulted in eight positive pools (1%) in Kerteszia females (Table 1). In March, we individually tested all mosquitoes because we knew a human malaria case was identified from a visitor who had been hiking on the December Waterfall Trail one week before our field collections from March 8th to 10th. One sample (D_3210; one Ke. cruzii specimen) was 18S-positive for P. vivax or P. simium, showing a cycle threshold of (ct) = 40. This malaria-positive mosquito female was collected in a Shannon trap at 19–20 h (Table 1). In April, five pools were positive (Table 1). One of them was 18S-positive for P. falciparum, also known as the forested P. falciparum-like parasite (ct = 40). This was obtained from a pool (S_3723) with two Ke. cruzii females captured in Shannon traps at 20–21 h at the Cambuci Suspended Trail site (Table 1). Another one was 18S-positive for P. malariae or P. brasilianum (ct = 47) from a pool (RA_4518) with three Ke. cruzii females captured in Shannon traps at 20–21 h at the Tapir Creek Village site (Table 1). In November 2022, we had one 18S-positive sample for P. falciparum (also known as the forested P. falciparum-like parasite; ct = 47) in a pool (D_4972) of two Ke. cruzii females captured in Shannon traps at 17–18 h at the December Waterfall Trail site (Table 1). The remaining four were 18S-positive for plasmodium-genus only in pools with 10 Ke. cruzii female specimens (RA_4366 ct = 35, RA_4397 ct = 31, and RA_4457 ct = 45) in April and (RA_5166 ct = 44) in November 2022 at the Tapir Creek Village site (Table 1).

3.3. Nested PCR plus Sequencing and Phylogenetic Analyses

Two 18S-qPCR-positive pools were further confirmed with nested PCR plus sequencing (Table 1). The P. vivax or P. simium (GenBank ID OQ830680; Table 1) nucleotide sequences herein obtained were 98.1% similar to the P. vivax mitogenome from human samples in Brazil [18] (Figure 2) and elsewhere in Papua New Guinea and Panama. The P. malariae or P. brasilianum (GenBank ID OQ830681; Table 1) nucleotide sequences herein obtained were 99% similar to the P. malariae mitogenome in feces of Pan troglodytes (GenBank ID MF693452) and Gorilla (GenBank ID MF693444 and MF693446) and from a human sample (GenBank ID MF693442) in Cameroon, Central Africa [35]. The sample also showed 99% similarity with P. brasilianum collected from callitrichid monkeys (Saguinus fuscicollis and Saguinus imperator) in Madre de Dios, Southeastern Peru (GenBank ID MF693425) [36] (Figure 2).

3.4. Data Analysis

The minimum infection rates in Kerteszia females are shown in Table 2. These are global estimates. If we considered only the sampled mosquitoes in the day when one was found positive, the estimates would be much higher. For instance, we collected a total of 57 Ke. cruzii females in a one-day collection in March at the December Waterfall Trail site when a P. simium-infected female was identified. For this day and site, the infection rate was 1.75% (1/57) or 17× higher than the global estimate of 0.1% (Table 2). During this month, a human malaria case was reported from an ecotourist who engaged in forest activities at this site.

4. Discussion

The zoonotic malaria risk estimated as the minimum infection rate in Kerteszia females with Plasmodium spp. ranged from 0.1 to 0.2% in the Legado das Águas Forest Reserve from 2021 to 2022. This means that the zoonotic malaria risk for visitors or staff engaging in forest activities is as low as one–two plasmodium-infected persons per 1000 human-seeking Kerteszia females. This risk is notably lower than that obtained 10 years ago (5–10%) [1]. On one hand, this outcome was in line with the study’s hypothesis, i.e., with the decline of howler monkeys as the main reservoir in the studied area, the zoonotic malaria risk dropped to low levels [25]. On the other hand, an alternative simian host to infect Ke. cruzii with P. simium, P. brasilianum, and the P. falciparum-like parasite was a puzzling outcome and needs further comments, as seen below.
Before proceeding to explain this alternative hypothesis, it is important to highlight the difference between global estimates vs. day/site estimates when interpreting our outcomes. We identified an anopheline infection rate 17× higher than the global estimate (1.75 vs. 0.1%) on 9th March 2022 at the December Waterfall Trail site. This collection occurred one week after a visitor participated in activities at this site and contracted malaria. This case, officially reported as P. vivax, was diagnosed by blood smear slides in a reference center for malaria in São Paulo [27]. Here, we obtained an 18S fragment sequence 98% identical to P. vivax or P. simium [18] at the same site and period from a Kerteszia female. In other words, alternative reservoirs as evidenced below might be able to sustain highly dynamic transmission and support a strong force of infection of simian parasites to humans, conditioned to time and space.
Atlantic Forest howler monkeys (Alouatta guariba clamitans) are the main reservoir for simian malaria [7,23,37]. However, their populations steeply declined after yellow fever virus outbreaks from 2016 to 2017 [25,38]. The Legado das Águas Forest Reserve has 20–30 forest rangers who walk 10–15 km on a daily basis to prevent trespassing from wildlife hunters or palm tree smugglers. While doing this, they make important observations on currently present wildlife in this reserve. These rangers confirmed the absence of howler monkey sightings between 2018 and 2022. This suggests that other simian species can harbor Plasmodium spp. and infect Kerteszia in the absence of howler monkeys. In agreement with this view is another study undertaken on the slopes of Serra do Mar in Espírito Santo State where anopheline infection rates were unaffected by yellow fever outbreaks and local Alouatta population decline [39]. We hypothesize that one or two of the remaining simian species in the Legado das Águas Forest Reserve can play a role as alternative reservoirs. Southern Muriqui (Brachyteles arachnoides) and capuchin monkeys (Sapajus) are frequently seen by rangers in forested areas from this reserve and both have been previously found to be infected with P. simium and P. brasilianum [40,41,42]. During this research, we trained forest rangers to obtain feces samples from these simians during their daily monitoring (Figure 3). These simian fecal samples (n = 12) were tested and one of them from a Southern Muriqui was positive (ct = 45) for plasmodium-genus only (Figure 3).
The main limitation faced by this study was lower levels of specificity for tests carried out with non-human samples (mosquitoes) conditioned to complexities of Plasmodium evolutionary lineages in the Atlantic Forest.

5. Conclusions

Naturally plasmodium-infected Kerteszia cruzii were found in Serra do Mar, Atlantic Forest at ground level and in the absence of their main reservoir (Alouatta monkeys), which suggests the role of Southern Muriqui (Brachyteles arachnoides) as alternative reservoirs.
We found potential agents of zoonotic simian malaria, also known as P. simium and the P. falciparum-like parasite, on the December Waterfall Trail, P. brasilianum and four unknown Plasmodium species in the Tapir Creek Village, and P. falciparum-like on the Cambuci Suspended Trail.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/microorganisms11102465/s1. Figure S1: Outcomes from laboratory testing of samples of Ke. cruzii for P. falciparum at University of Florida, Gainesville FL, USA, December 2017. These samples went all positive in the work by Laporta et al. 2015 [1]. Sample n. M267 went positive in both assays and its cytb sequence has been shown into a phylogenetic analysis [2] and is deposited in GenBank under accession number MT779800 and URL = https://www.ncbi.nlm.nih.gov/nuccore/MT779800, accessed on 29 September 2023. Table S1: Specimens of Ke. cruzii captured in January 2019 in the Legado das Águas Forest Reserve and tested at the University of Florida, March 2019.

Author Contributions

Conceptualization, A.M.R.C.D., G.Z.L. and M.A.M.S.; formal analysis, T.M.P.O., A.C.L., J.R.L. and G.Z.L.; funding acquisition, A.M.R.C.D., G.Z.L. and M.A.M.S.; investigation, M.E.O.R., A.M.R.C.D., L.F.M., J.R.L. and G.Z.L.; methodology, A.M.R.C.D., T.M.P.O., L.F.M., A.C.L., G.Z.L. and M.A.M.S.; resources, G.Z.L. and M.A.M.S.; writing—original draft, M.E.O.R. and G.Z.L.; writing—review and editing, A.M.R.C.D., T.M.P.O., L.F.M., A.C.L., J.R.L., G.Z.L. and M.A.M.S. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Votorantim Reserve (technical cooperation agreement CW2357975). ACL was supported by the FAPES grant n. 667/2022. GZL was supported by the São Paulo Research Foundation (FAPESP grant n. 2021/06669-6). AMRCD was supported by LIM-49/IMT/FMUSP/USP and Instituto Pasteur. MEOR had a CAPES scholarship (Finance Code 001).

Institutional Review Board Statement

The field study protocol was approved by the Brazilian Ministry of Environment through authorization number SISBIO 82376 for the mosquito in situ specimens and SISBIO 59859 for the simian feces. The details on the genetic access of the Plasmodium spp. DNA from these samples was fully informed to the Brazilian Ministry of Environment (SISGEN register n. A577CCC).

Data Availability Statement

Data are contained within the article.

Acknowledgments

We would like to thank (1) Antônio “The Ranger” Waldomiro de Oliveira, (2) João “The Mister” Carlos Nascimento de Oliveira, (3) Luiz Milton “The Incredible” Bonafé, (4) Sergio “The Upbeat” Benettão, and (5) Carlos Alberto “The Guardian” Furtunato for their all-important help in the field work of this project. We would like to thank our friends (Valdirene, Valter, and Elisa) from Tapir Creek Village who received us as if we were family. We would like to thank our partners (David Canassa, Daniela Gerdenits, Gabriel Gade, and Bianca Matinata) and all the team from Legado das Águas Forest Reserve for their remarkable interest in and support of our scientific endeavor. We would like to thank David Feder, Ricardo Souto, and Celia Guarnieri from NEPAS for the timely administrative support provided to this project.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. Study area and sampling sites. In 2012, we found a surprisingly high Plasmodium spp. infectivity rate among Kerteszia mosquitoes at the Alecrim Waterfall site. In the present work, we tested the infectivity of sampled mosquitoes at three sites in the Legado das Águas Forest Reserve: (1) December Waterfall Trail, (2) Cambuci Suspended Trail, and (3) Tapir Creek Village.
Figure 1. Study area and sampling sites. In 2012, we found a surprisingly high Plasmodium spp. infectivity rate among Kerteszia mosquitoes at the Alecrim Waterfall site. In the present work, we tested the infectivity of sampled mosquitoes at three sites in the Legado das Águas Forest Reserve: (1) December Waterfall Trail, (2) Cambuci Suspended Trail, and (3) Tapir Creek Village.
Microorganisms 11 02465 g001
Figure 2. Maximum-likelihood phylogenetic tree of Plasmodium species including the two sequences obtained from Ke. cruzii naturally infected in the Legado das Águas Forest Reserve, São Paulo, Brazil (in bold). The values in the branches are bootstraps. Blue (GenBank ID OQ830681) and green (GenBank ID OQ830680) colors are the samples obtained herein.
Figure 2. Maximum-likelihood phylogenetic tree of Plasmodium species including the two sequences obtained from Ke. cruzii naturally infected in the Legado das Águas Forest Reserve, São Paulo, Brazil (in bold). The values in the branches are bootstraps. Blue (GenBank ID OQ830681) and green (GenBank ID OQ830680) colors are the samples obtained herein.
Microorganisms 11 02465 g002
Figure 3. Locations with exact geographic coordinates of simian fecal samples obtained from forest rangers for this project. One fecal sample from a Southern Muriqui tested positive with 18S qPCR for Plasmodium spp. (ct = 45).
Figure 3. Locations with exact geographic coordinates of simian fecal samples obtained from forest rangers for this project. One fecal sample from a Southern Muriqui tested positive with 18S qPCR for Plasmodium spp. (ct = 45).
Microorganisms 11 02465 g003
Table 1. Anopheline females captured at Legado das Águas Forest Reserve, 2021–2022.
Table 1. Anopheline females captured at Legado das Águas Forest Reserve, 2021–2022.
Sampling SiteAnophelines (n)Pool Positive for Plasmodium spp. with 18S qPCR 1
PlasmodiumP. vivaxP. falciparumP. malariae
Cambuci Suspended TrailKe. cruzii (853)
Kerteszia spp. (2)
An. lutzii (3)
An. medialis (1)
-
-
-
-
-
-
-
-
1 (April 22)
-
-
-
-
-
-
-
December Waterfall TrailKe. cruzii (1928)
Kerteszia spp. (114)
-
-
1 (March 22) 2
-
1 (November 22)
-
-
-
Tapir Creek VillageKe. cruzii (2352)
Kerteszia spp. (36)
An. lutzii (3)
An. medialis (5)
An. fluminensis (4)
3 (April 22)
1 (November 22)
-
-
-
-
-
-
-
-
-
-
-
-
-
1 (April 22) 3
-
-
-
-
1 Pool containing 2–10 specimens, except for collections in March when mosquitoes were individually tested. 2 P. vivax or P. simium sequenced with 18S qPCR and cytb 402 bp (GenBank ID OQ830680). 3 P. malariae or P. brasilianum sequenced with 18S qPCR and cytb 402 bp (GenBank ID OQ830681).
Table 2. Minimum infection rate in Kerteszia females to estimate zoonotic malaria risk per selected sampling site in the Legado das Águas Forest Reserve, 2021–2022.
Table 2. Minimum infection rate in Kerteszia females to estimate zoonotic malaria risk per selected sampling site in the Legado das Águas Forest Reserve, 2021–2022.
Sampling SitePlasmodiumP. malariaeP. vivaxP. falciparum
Cambuci Suspended Trail--- 1 855 = 0.1%
December Waterfall Trail-- 2 2042 = 0.1%
Tapir Creek Village 5 2388 = 0.2%--
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Rangel, M.E.O.; Duarte, A.M.R.C.; Oliveira, T.M.P.; Mucci, L.F.; Loss, A.C.; Loaiza, J.R.; Laporta, G.Z.; Sallum, M.A.M. Zoonotic Malaria Risk in Serra Do Mar, Atlantic Forest, Brazil. Microorganisms 2023, 11, 2465. https://doi.org/10.3390/microorganisms11102465

AMA Style

Rangel MEO, Duarte AMRC, Oliveira TMP, Mucci LF, Loss AC, Loaiza JR, Laporta GZ, Sallum MAM. Zoonotic Malaria Risk in Serra Do Mar, Atlantic Forest, Brazil. Microorganisms. 2023; 11(10):2465. https://doi.org/10.3390/microorganisms11102465

Chicago/Turabian Style

Rangel, Marina E. O., Ana Maria R. C. Duarte, Tatiane M. P. Oliveira, Luis F. Mucci, Ana Carolina Loss, Jose R. Loaiza, Gabriel Z. Laporta, and Maria Anice M. Sallum. 2023. "Zoonotic Malaria Risk in Serra Do Mar, Atlantic Forest, Brazil" Microorganisms 11, no. 10: 2465. https://doi.org/10.3390/microorganisms11102465

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