Anopheles sundaicus s.l. is an important malaria vector primarily found in coastal landscapes of western and central Indonesia. The species complex has a wide geographical distribution in South and Southeast Asia and exhibits ecological and behavioural variability over its range. Studies on understanding the distribution of different members in the complex and their bionomics related to malaria transmission might be important guiding more effective vector intervention strategies. Female An. sundaicus s.l. were collected from seven provinces, 12 locations in Indonesia representing Sumatra: North Sumatra, Bangka-Belitung, South Lampung, and Bengkulu; in Java: West Java; and the Lesser Sunda Islands: West Nusa Tenggara and East Nusa Tenggara provinces. Sequencing of ribosomal DNA ITS2 gene fragments and two mitochondrial DNA gene markers, COI and cytb, enabled molecular identification of morphologically indistinguishable members of the complex. Findings allowed inference on the distribution of the An. sundaicus s.l. present in Indonesia and further illustrate the phylogenetic relationships of An. epiroticus within the complex. A total of 370 An. sundaicus s.l specimens were analysed for the ITS2 fragment. The ITS2 sequence alignment revealed two consistent species-specific point mutations, a T>C transition at base 479 and a G>T transversion at base 538 that differentiated five haplotypes: TG, CG, TT, CT, and TY. The TG haplotype matched published An. epiroticus–indicative sequences from Thailand, Vietnam and peninsular Malaysia. The previously described insertion event (base 603) was observed in all identified specimens. Analysis of the COI and cytb genes revealed no consistent nucleotide variations that could definitively distinguish An. epiroticus from other members in the Sundaicus Complex. The findings indicate and support the existence of An. epiroticus in North Sumatra and Bangka-Belitung archipelago. Further studies are recommended to determine the full distributional extent of the Sundaicus complex in Indonesia and investigate the role of these species in malaria transmission.
In Indonesia, more than 80 species of Anopheles have been documented, of which approximately 24 species are regarded as malaria vectors. Many of these mosquitoes are members of species complexes, being morphologically indistinguishable from other member sibling species. The Anopheles sundaicus complex (s.l.) has a wide geographical distribution in South and Southeast Asia, and exhibits ecological and behavioural variability over its range. Anopheles sundaicus s.l. is an important malaria vector present primarily in coastal areas of western and central Indonesia. Cytologic, isozyme, and molecular methods have been used to distinguish members of the complex in Indonesia, with several species being reported in different localities. This study aims to explore the distribution of the An. sundaicus complex in Indonesia using molecular methods. Female Anopheles sundaicus s.l. were collected from 12 localities within seven provinces in western to south-central Indonesia. The findings indicate the presence of An. epiroticus in North Sumatra and Bangka-Belitung archipelago off the eastern coast of central Sumatra. Further studies are required to determine the full distributional extent of the An. sundaicus complex in Indonesia and investigate the role of each species in malaria transmission.
Citation: Syafruddin D, Lestari YE, Permana DH, Asih PBS, St. Laurent B, Zubaidah S, et al. (2020) Anopheles sundaicus complex and the presence of Anopheles epiroticus in Indonesia. PLoS Negl Trop Dis 14(7): e0008385. https://doi.org/10.1371/journal.pntd.0008385
Editor: Audrey Lenhart, Centers for Disease Control and Prevention, UNITED STATES
Received: January 10, 2020; Accepted: May 12, 2020; Published: July 2, 2020
Copyright: © 2020 Syafruddin et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Data Availability: All relevant data are within the manuscript.
Funding: This study was supported by the Government of Indonesia, the Sumba SPIRIT Study and the Bill and Melinda Gates Foundation under Grant No. 45114. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
The genus Anopheles contains over 480 formally described species worldwide  with more awaiting description. Though over 100 Anopheles species have the capacity to transmit human malaria parasites, only a handful of species are currently regarded as ‘primary’ vector species, some of which are members of species complexes [2–4]. In Indonesia, more than 80 species of Anopheles are known present, with approximately 24 confirmed as malaria vectors . Many of these mosquitoes are members of sibling species complexes, genetically closely related taxa morphologically indistinguishable from one another. Behavioural differences between members of a species complex may dramatically influence their respective capacity to transmit pathogens [6–7]. For example, the Anopheles farauti complex present in Papua New Guinea has at least three members as important malaria vectors, while four others are either secondary or non-vectors . Possible behavioural and biological differences between species that contribute to pathogen transmission may determine whether their specific identification is useful for enhancing malaria control programs.
Anopheles (Cellia) sundaicus (Rodenwaldt) is an important malaria vector throughout its range in Indonesia . This species has a wide distribution throughout Indonesia (Sumatra to the Maluku islands), the only major exclusion is the western half of New Guinea Island. It is present primarily in coastal zone habitats and more limited in interior areas and foothills [9–11]. Anopheles sundaicus is typically anthropophilic; however, host preference and biting behaviour may vary by location and host availability . Immature stages of An. sundaicus are typically associated with coastal, sunlit, brackish water habitats, and often with floating algal mats . Salinity of coastal habitats typically ranges between 1.2 to 1.8% (seawater is ~3.5%). For inland areas at higher elevations (up to 1000 m), freshwater habitats are used [11–15].
The An. sundaicus complex is in the subgenus Cellia, Pyretophorus Series . Members in the complex can be easily identified morphologically, whereas definitive Species identifications are based on cytogenetic (ovarian polytene chromosomes), specific enzymatic (isozymes) presence, and molecular (DNA) markers. The initial discovery of sibling species involved three cytological forms from populations in Thailand, Sumatra and Java, provisionally designated cytotypes (forms) A, B and C  and supported by isozyme evidence . Cytotype D was later identified in the Andaman and Nicobar Islands (Indian Ocean) [18, 19]. Form A is the most widespread of the three cytotypes, occurring primarily along coastal, brackish water ecologies in Thailand and Indonesia (Sumatra and Java). The molecular method uses DNA markers—the nuclear ribosomal DNA (rDNA) Internal Transcribed Spacer-2 (ITS2), and the mitochondrial DNA (mtDNA) Cytochrome Oxidase I (COI) and Cytochrome b (Cytb) genes. Four members of the An. sundaicus complex have been identified molecularly: An. sundaicus s.s., An. epiroticus Linton & Harbach, An. sundaicus species D, and An. sundaicus species E .
The use of chromosome and DNA to identify sibling species has resulted in discrepant conclusions between the two methods. Cytologic evidence indicates that Form A (= An. epiroticus) should be present in Sumatra and Java [16, 17, 21]. However, this is contradictory with more current findings based on DNA evidence indicating that An. epiroticus appears confined to mainland Southeast Asia and not present in Indonesia or eastern Malaysia (Borneo) [20, 22, 23]. Form B has been found in sympatry with Form A at inland freshwater sites near Purworejo (south-central Java), and South Tapanuli (northern Sumatra). Form C appears confined to a coastal locality in the Asahan area in north-eastern Sumatra and also sympatric with forms A and B [16, 17].
Anopheles sundaicus s.s.  from Sarawak (Malaysian Borneo)  and An. epiroticus from mainland Southeast Asia  are allopatric. Because sibling species are isomorphic, lacking sufficient morphological characters for definitive species determination, DNA markers using fixed differences in the rDNA ITS2 fragment and the mtDNA COI gene are used to separate the two species. Allopatric An. sundaicus species D (Indian Ocean) is based on chromosomal forms and ITS2 sequences [18, 19]. Until very recently, An. sundaicus species E in Indonesia (e.g., Sumatra, Java and Sumba islands) was considered allopatric with the other Sundaicus Complex members with separation based on COI sequences using a multiplex allele-specific polymerase chain reaction [20, 22, 25–27]. So far, the relationships of cytotypes B and C to other members in the complex remain unclear [22, 25].
The present study explores the distribution, phylogenetic relationships, and population structure of the An. sundaicus complex in Indonesia. Morphological characters were compared with clades identified from DNA markers—genes encoding mtDNA COI and cytochrome-b (cytb), and the rDNA ITS2 region. The COI sub-unit gene has been widely used in anopheline systematics and population structure studies , while the ITS2 region shows low co-evolutionary intra-specific and high inter-specific variation , and serves a valuable marker for the molecular characterization of anopheline species [29, 30].
This study was approved by the Ethics Committee of Research in Health, Medical Faculty of Hasanuddin University, Makassar, Indonesia (No.0868/H126.96.36.199.31/PP36-KOMETIK/2011) and endorsed by the Eijkman Institute Research Ethics Committee, Jakarta, Indonesia (No. 51; 29 December, 2011). Both committees include a certified veterinarian to oversee and ensure the well-being of animals (animal-baited trapping) used in this study.
Female Anopheles mosquitoes were collected as part of independent studies on malaria and mosquito bionomics in Indonesia between 2007 and 2015. Geo-coordinates of collection locations are provided in Table 1. Mosquitoes were collected using human-landing catches (HLC), animal-baited traps, and larval collections, from seven provinces: North Sumatra, Bangka-Belitung islands, South Lampung, Enggano Island (Bengkulu), West Java, West Nusa Tenggara, and East Nusa Tenggara (Fig 1), representing 12 specific locations (Table 1).
The seven collection areas (provinces), comprising 12 collection sites for An. sundaicus s.l. in Indonesia (1) North Sumatra, (2) Bangka-Belitung, (3) Bengkulu (Enggano Is.), (4) South Lampung, (5) West Java, (6) West Nusa Tenggara, and (7) East Nusa Tenggara. The dashed lines are biogeographical transition zones the separate Asia and Australasia. The transitional zone between the Wallace’s and Weber’s lines is termed ‘Wallacea’. Plants and animals related to Asian species are found to the north-west. Australasian species are found mainly to the south-east, with a small inter-mix of Asian species as seen with An. sundaicus. This species complex is not found east of Weber’s or Lydekker’s lines. Map from Natural Earth. https://www.naturalearthdata.com/.
Human landing catch
At the beginning of a study in each site, local people were asked their willingness to participate in HLCs. After obtaining informed consent, healthy adult male and female volunteers, were trained to collect mosquitoes that landed on their exposed legs using a mouth aspirator and place them in holding cups. Each collection night, HLCs were conducted both indoors and outdoors from 18.00–06.00 h with a 10-minute rest period every hour. The number of collection nights varied by study. After study participation, HLC volunteers were contacted for one month for tracking and treating any possible mosquito-borne infections the result of their participation.
Animal-baited tent trap
Animal-baited tent traps utilized local livestock. Traps were located near livestock stables with either a cow or a goat leashed loosely to a stake in the center of the tent enclosure. Evening-active mosquitoes found resting on the inner surface of the tenting material were collected using a mouth aspirator once each hour, from 18.00 to 06.00.
Female mosquitoes were initially identified using morphological keys by field staff [31, 32], and preserved individually in 1.5 ml snap-cap plastic tubes over silica gel separated with a cotton plug preventing direct contact between desiccant and specimen . Those identified as An. sundaicus were separated, and preserved for later detailed morphological species confirmation and molecular analysis.
DNA was extracted from individual adult mosquitoes using Chelex-100 (BioRad Laboratories, Hercules, CA, USA) with slight modifications to the protocol . Briefly, mosquitoes were ground with clean Teflon pestles in 50 μl blocking buffer (BB), containing 5.0 g Casein; 0.01 g/L Phenol Red; 900 ml phosphate buffered saline (PBS), pH 7.4; 100 ml of 0.1 N NaOH; with additional IGEPAL (5 μl IGEPAL: 1 ml BB). Afterwards, the pestles were rinsed with additional 200 μl of blocking buffer. Mosquito DNA from the homogenate was extracted using the Chelex-100 ion exchanger. The 50 μl homogenate was added to 50 μl 20% Chelex-100 in distilled water (pH ≥ 10.5). The DNA was extracted by boiling at 100°C for 10 min. The DNA was either used immediately for polymerase chain reaction (PCR) or stored at -20ºC for later analysis.
PCR amplification and DNA sequencing
Amplification of the COI, cytb, and ITS2 genomic regions was performed using each respective set of gene primers [20, 25, 28]. The PCR products were purified using clean-up systems (PROMEGA Corporation, Madison, WI, USA) and Exonuclease I—shrimp alkaline phosphatase (USB, Affymetrix, Cleveland, OH, USA). The purified amplicons were sequenced using an ABI Prism Dye BigDye Terminator Cycle Sequencing Ready Kit (Applied Biosystem, Foster City, CA, USA) in a fluorescent DNA capillary electrophoresis sequencer (ABI 3130×l) at the Eijkman Institute (Jakarta, Indonesia), and repeated at the University of Notre Dame (Indiana, USA).
Phylogenetic analyses were performed by aligning DNA sequences using ClustalW, an alignment editor (Biological Sequence Alignment Editor, BioEdit, ver 7.0.9 Ibis Biosciences, Carlsbad, CA, USA), BLAST (GenBank, NCBI), and manual examination. Multiple alignments were made using Molecular Evolutionary Genetics Analysis (MEGA) Software Version 6.0. Phylogenetic trees were constructed using 1000 bootstrap re-sampling repetitions. Evolutionary distances were computed using the Maximum Composite Likelihood method and are in the units of the number of base substitutions per site. The percentage of replicate trees and associated taxa that clustered together in the bootstrap test was also calculated . The analysis utilized 17 ITS2 and 20 COI nucleotide sequences. All ambiguous positions were removed from each sequence pair resulting in 344 positions in the final dataset. Evolutionary analyses used MEGA6 [35, 36]. The An. subpictus ITS2 (GenBank accession number KX622063), and COI (GenBank accession number KJ461780) gene sequences were used as outgroups in the molecular analyses.
Approximately 90% of the initially field-identified An. sundaicus s.l. specimens were confirmed as An. sundaicus s.l. using follow-up expert morphological examination and molecular-based methods. DNA sequences were generated from 370 An. sundaicus specimens collected from northern Sumatra to Sumba Island located in East Nusa Tenggara Province, geographically spanning most of the known range of this species complex in Indonesia (Fig 1). Target sequences included the ITS2 (n = 370), partial COI (n = 107), and ctyb (n = 107) genes.
PCR and sequencing ITS2 fragments
All 370 An. sundaicus specimens successfully yielded a 586 base pair (bp) ITS2 amplicon. The rDNA sequence electropherogram was manually examined for sequencing artefacts using ClustalW. Alignment demonstrated that ITS2 sequences were highly conserved, with two consistent nucleotide substitutions; a T>C transition at nucleotide (nt) base 479 and a G>T transversion at nt 538. The insertion event at nt 603 was found in all specimens examined (Fig 2). The 17 ITS2 sequences representing each study site are deposited in GenBank accession numbers JN675907- JN675923.
(GenBank Acc. No. GQ284822, AF369550, GQ284826) and An. epiroticus (GenBank Acc. No. AF469855). Geographic origins of specimens indicated as RB-17 = Lampung, BRB-127 = North Sumatra, RB-14 = Lampung, SM1-108 = Sumba, East Nusa Tenggara, and E-01: Enggano, Bengkulu.
ITS2 fragment sequence analysis
Sequence alignment revealed a 99.46–99.48% sequence similarity between ITS2 amplicons (n = 152) and the published voucher sequence of An. epiroticus (GenBank accession number AF469855). Other ITS2 sequences (n = 218) matched either An. sundaicus sequences from Sarawak, Malaysia (GenBank accession numbers GQ284826, AF369550) or Sumatra, Indonesia (GQ284822). As reported by Dusfour et al. [20, 22], this dataset also revealed that An. epiroticus ITS2 sequences (BRB-127) and An. sundaicus differed at several variable sites; a T>C transition at nt 479 and a G>T transversion at nt 538 (Table 1). Variations in An. sundaicus sequences in this study did not overlap with the variations seen in previous studies or those mentioned above. For example, a sample from western Sumba (SM1-103) possessed a G>T transversion at nt 538 but lacked a base transition at nt 479 (Fig 2). Conversely, the specimens from Enggano Island possessed a T to C transition at nt 479 but lacked a base transversion at nt 538.
Analysis of ITS2 sequences identified polymorphic sites at nt 479 and 538, (Table 1). Based on nucleotides at positions 479 and 538, the An. sundaicus s.l. specimens possessed four haplotypes: TG, CG, TT, CT. In nine DNA samples from the Bangka-Belitung archipelago, a heteroduplex ITS2 at nt 479 as Y (C/T) and nt 538 as K (T/G/) was detected (Fig 3). Anopheles epiroticus appears to exclusively possess the TG haplotypes at these sites [13, 20], and specimens (n = 152) from North Sumatra (Barbaran and Sebajior villages) and Bangka-Belitung each had this distinct haplotype. These mosquitoes, hence, are considered to be An. epiroticus. The CG and CT haplotypes predominated in all sampled sites, whereas the TT haplotype was only observed on Bangka-Belitung.
COI gene fragment analysis
The COI gene fragment (522 bp) was amplified from 107 specimens of An. sundaicus s.l. Sequence alignment revealed 97 variable sites, of which 32 were parsimony informative. Analysis of nucleotide substitutions revealed no consistent nucleotide position useful to distinguish An. epiroticus from the other three sibling species. The nucleotide substitution at base 294 where the A to G substitution was present in An. epiroticus and An. sundaicus with the lone exception of a single specimen from Bangka-Belitung having the G nucleotide at base 294 (Table 2). No COI positions that could be linked to the observed ITS2 sequence differences. Insertion and deletion events were not observed in the sequence alignment analysis.
Cyt-b gene fragment analysis
A 485 bp cytb gene fragment was amplified from An. sundaicus s.l. specimens. Alignment of these sequences revealed 128 variable sites, of which 60 were parsimony informative. Alignment of the sequences with published sequences from An. sundaicus s.s. (GenBank accession numbers AY243796, AY256956, AY299095, AY299098, AY299103) and An. epiroticus (GenBank accession numbers AY253160, AY256954, JN675907-JN675923) revealed five species-indicative nucleotide variations at bases 12, 267, 297, 469 and 474. However, no variation was unique to a specific species and thus not useful to distinguish between An. epiroticus and other species complex members (Table 2). With the exception of mosquitoes from western Sumba Island, specimens from all sampled sites were the same haplotype.
All ITS2 and COI sequences obtained from specimens collected from 12 locations were separately aligned with GenBank entries for An. epiroticus and An. sundaicus s.s. from Thailand and Malaysia. After removing all ambiguous positions, the sequence datasets used for the final phylogenetic tree reconstruction included ITS2 (n = 17) with sequence length 586 bp and COI (n = 20) sequence length 522 bp. The resulting tree with sample names and corresponding GenBank accession numbers is provided (Fig 4). Despite the low bootstrap values for both ITS2 and COI sequences, analysis revealed significantly different clade formation for An. epiroticus and An. sundaicus (Fig 4A and 4B respectively). Evolutionary history was inferred using the Neighbor-Joining method . Based on ITS2, specimens from North Sumatra (SUT-11) and Bangka Belitung (BB-46 and BB-5) clustered together with An. epiroticus. Specimens from West Java, Lampung and other specimens from Bangka Belitung (BB-3) clustered with An. sundaicus s.s. from Lundu, Sarawak, Malaysia. The vast majority of specimens from Sumba formed a different cluster with specimens from Bengkulu and the remaining specimens from Lampung, North Sumatra, Java and West Nusa Tenggara provinces. Anopheles epiroticus may have recently diverged from the An. sundaicus complex as evidenced by the ITS2 branching (Fig 4A). Based on the COI gene, most specimens clustered with An. sundaicus except for several specimens from Bangka Belitung (BB-2, BB-6 and BB-8) that were closer to An. epiroticus. Specimens from North Sumatra clustered with An. sundaicus from Lampung, West Java and West Nusa Tenggara.
Phylogenetic tree of An. sundaicus s.l. based on the rDNA ITS2 fragment (Panel A) and concatameric mtDNA COI (Panel B). The percentage of replicate trees in which the associated taxa clustered together in the bootstrap test is shown next to the branches. The optimal tree with the sum of branch length = 0.01841176 is depicted. The tree is drawn to scale, with branch lengths in the same units as those of the evolutionary distances used to infer species relationships. Some specimens from North Sumatra (Barbaran and Sebajior) and Bangka-Belitung cluster with An. epiroticus from Malaysia, Vietnam, and Thailand. Site codes: SUT = North Sumatra; SUM = Sumba, East Nusa Tenggara; BB = Bangka Belitung Archipelago; LA = Lampung; JAW = West Java; NTB = West Nusa Tenggara; and BK = Bengkulu.
Analysis of ITS2 sequences (n = 370) in An. sundaicus s.l. specimens revealed two previously documented consistent inter-specific variations; a T>C transition at nt 479 and a G>T transversion at nt 538 that distinguish An. epiroticus from the other members of the Sundaicus Complex. Furthermore, these results corroborate the findings of Linton et al.  showing these two nucleotides are suitable to distinguish An. epiroticus from An. sundaicus. Linton et al.  also reported the absence of a base insertion at ITS2 nt 603 in specimens formerly identified as An. sundaicus in Vietnam and Thailand. However, this base insertion was found in all specimens from Indonesia, indicating the possibility this mutation event occurred either independent of genetic divergence between An. sundaicus and An. epiroticus, or due to periodic recurrent gene flow between landmasses .
This study provides the first definitive evidence for the presence and geographical extent of An. epiroticus in Indonesia, contrary to previous studies that suggested the species exists exclusively in mainland Southeast Asia . Using verified methods , An. epiroticus was documented on the island of Sumatra and the Bangka-Belitung archipelago, islands set in the Java Sea between Sumatra and Kalimantan (Borneo) near the Karimata Strait. These findings also indicate An. epiroticus occurs in sympatry with other sibling lineages. These observations do not dispute the inferred allopatric speciation of members of the complex on separate Asian landmasses, possibly attributed to repeated geological occurrences of cyclical island and refugium creation. The theory that periodic sea-level changes caused by repeated glaciation events may have created secondary isolation barriers (i.e., vicariance) and genetic bottleneck events during the Pleistocene epoch (2.6 million– 11,700 mya) has been advanced as a biogeographical hypothesis of population history and gene flow in this region . This hypothesis of ecological and allopatric speciation has been challenged based on analyses that indicates species divergence often appears no greater between than within landmasses, thus providing sufficient and recurrent gene flow during recent geologic periods of Earth .
The ITS2 nucleotide substitutions used as markers for distinguishing An. epiroticus from the other members of the An. sundaicus complex include five haplotypes: TG, CG, TT, CT, and CY. The TG haplotype is associated specifically with An. epiroticus. At this stage, it is not clear whether the CG, TT, CT, and TY haplotypes correspond with specific forms of An. sundaicus identified in Indonesia, i.e., cytotypes B and C, An. sundaicus s.s., and An. sundaicus E. Interestingly, evidence of heteroduplexes indicate that natural hybridization (introgression) is possible between these sympatric sibling species. However, this evidence does not refute the validity of An. epiroticus as a distinct taxon as reproductive isolation may breakdown occasionally between sibling species, as seen in other species complexes such as An. gambiae s.l. where ITS2 sequence-based species differences are maintained and COI differences are virtually non-existent [38, 39].
Analysis of COI and cytb genes from 97 An. sundaicus s.l. revealed no consistent species-specific nucleotides useful as molecular markers to distinguish An. epiroticus from other members of the complex. These findings are not in agreement with Linton et al. (2005)  that indicate the A to G transition at base 294 COI and nucleotide variations at 12, 267, 297, 469 and 474 cytb are useful markers for An. epiroticus. The use of mtDNA to characterize various organisms, including mosquitoes, is well established [20, 21, 40]. The unique attributes of mtDNA include maternal inheritance, absence of recombination during reproduction (as a single inheritable unit), relatively rapid rates of mutations (evolutionary change), and small size, which makes it a useful marker for examining closely related taxa [41, 42]. However, in this study, variations at nt 27, 122 and 294 of COI and at nt 12 of cytb could not distinguish An. epiroticus and the other sibling members. In comparison to the rDNA ITS2 fragment, the mtDNA COI and cytb genes showed greater variation. This evidence supports the assertion that mtDNA has higher mutation rates than nuclear DNA . Therefore, the COI and cytb genes may be suitable for distinguishing intra-specific (polytypic) variation within populations.
Of the four cytotypes identified, cytotype A and B are the predominant forms geographically and found in sympatry in various areas of Southeast Asia [20, 21]. Therefore, cross-species gene flow between closely related members of the An. sundaicus complex is possible and supported by finding naturally occurring heteroduplex ITS2 nucleotides in this study. The heteroduplex (TY haplotype) in nine (~6%) of 151 specimens from Bangka-Belitung indicates that natural introgression can occur between populations of An. sundaicus haplotypes TT and TC. Naturally occurring hybridization between sibling species, together with other inherent confounders e.g., heteroplasmy, possibility of bi-parental inheritance of mitochondria, and mtDNA introgression , may complicate the use of mtDNA-based markers in this complex.
We acknowledge some inherent limitations to the study and analysis. Besides a low number of samples from some localities, having had an opportunity to explore additional molecular markers or approaches would have possibly enhanced the study and conclusions further. However, this was not possible with the material at hand, as this investigation relied solely on specimens collected over many years from different entomological collections and study designs.
The An. sundaicus complex includes morphologically indistinguishable and epidemiologically important vectors of malaria along coastal areas of South and Southeast Asia [12, 45]. Fortunately, molecular analysis provides a relatively rapid and inexpensive method for accurately identifying many species. This complex includes two formally named species and four forms based on either cytogenetics or rDNA/mtDNA evidence [14–16, 20, 22, 25]. Currently, the complex consists of four cytotypic forms designated A, B, C, and D [16, 19]. Anopheles sundaicus species A, present in mainland Southeast Asia was formally named An. epiroticus, based on DNA sequence differentiation of the entire nuclear ITS2 region and a portion of both mitochondrial COI and ctyb genes . The use of ITS2 sequences alone may not be robust enough to distinguish between members of the complex, as this gene is highly conserved resulting in a very low bootstrap value upon phylogenetic analyses. Nucleotide differences within the ITS2 gene among the members of the An. sundaicus complex ranged from 99.4–99.8%—merely 1–3 nt differences. Phylogenetic analysis using ITS2 resulted in three clusters—An. epiroticus, An. sundaicus s.s., and the Bengkulu-Sumba cluster. The single or double nucleotide difference seen, combined with sympatric specimens and evidence of possible natural hybridization, results in an unconvincing case to base speciation on this marker alone at these sites. Additional DNA markers with more informative sequences may help clarify these observations. In areas where members of the Sundaicus Complex occur in sympatry, it may be important to accurately distinguish between each species based on possible differing behavioural and biological characteristics influencing capacity to transmit malaria for vector control purposes [2, 46].
Though the major role of An. sundaicus s.l. in malaria transmission in western Indonesia has long been characterized [10–12], due to its recent discovery, the specific role of An. epiroticus has not been elucidated. More recently, An. sundaicus E has been confirmed having a major role in malaria transmission along the south-west coastal region of Sumba island . Anopheles epiroticus is a regarded as mostly an incidental or secondary vector in Cambodia, Myanmar, Thailand and Vietnam [48, 49]. The extent to which a vector may contribute to malaria transmission can be site-specific and is likely influenced by prevailing environmental and epidemiological variables such as habitat suitability, seasonality, abundance, blood feeding behaviour (host selection, time of feeding), and vector competence (sporozoite infections) [48, 50]. Compared with other Indonesian vector species, there are limited studies in areas with An. epiroticus (previously identified as An. sundaicus) that describe the bionomics and suitable methods of control [51, 52]. Currently, little is known about the specific role of An. epiroticus in the transmission of malaria in Sumatra and Bangka-Belitung. Anopheles epiroticus was not investigated to establish malaria vector status in this study. However, it is possible that mosquitoes morphologically identified earlier as An. sundaicus s.l. that exhibited relatively high human-biting rates [53, 54] and found infected with malaria sporozoites  may actually be An. epiroticus.
This study examined the sequence variation of rDNA ITS2 gene fragments and mtDNA COI and cytb genes of mosquitoes of the An. sundaicus complex in Indonesia. Previously published species-specific ITS2 nucleotide variations were detected that distinguished An. epiroticus from other members of the complex. Further studies on the distribution of members of An. sundaicus s.l. in Indonesia and their potential site-specific roles in malaria transmission requires further investigation. Species-specific identification of members in this complex has practical and possibly operationally relevant significance for targeting vector management programs in the country.
The authors are grateful for the support of the Eijkman Institute for Molecular Biology (EIMB) Jakarta, the National Institute of Health Research and Development, Ministry of Health Jakarta, the Malaria Transmission Consortium (MTC) Indonesia, CDC-Environmental Health, Department of Health, Jakarta, and the Sumba SPIRIT Team, Southwest Sumba District, East Nusa Tenggara Province. We thank Nia Rahmawati and Anggie PN Hidayati for their assistance in the laboratory and EIMB technical staff during mosquito sampling. This study is part of a MS thesis (YEL) at the University of Indonesia.
- 1. Harbach RE. Mosquito Taxonomic Inventory. Available from: http://www.mosquito-taxonomic-inventory.info. Accessed 15 May 2019
- 2. Morgan KP, Somboon , Walton C. Understanding Anopheles diversity in Southeast Asia and its applications for malaria control. In: Manguin S. (ed.). Anopheles Mosquitoes—New Insights into Malaria Vectors. InTech Open Access. Publisher, Rijeka, Croatia. 2013. p. 327–355. http://doi.org/10.5772/55709
- 3. Sinka ME, Bangs MJ, Manguin S, Rubio-Palis Y, Chareonviriyaphap T, Coetzee M, et al. A global map of dominant malaria vectors. Parasit Vectors 2012;5:69. pmid:22475528
- 4. Sinka ME, Bangs MJ, Chareonviriyaphap T, Manguin S, Elyazar IRF, Patil AP, et al. The dominant Anopheles vectors of human malaria in the Asia-Pacific region: occurrence data, distribution maps and bionomic précis. Parasit Vectors 2011;4:89. pmid:21612587
- 5. Indonesia Ministry of Health. Malaria Epidemiology of Indonesia. Data and Health information Window Bulletin. 2011; 1
- 6. Linton YM, Smith L, Koliopoulos G, Zounos AK, Samanidou-Voyadjoglou A, Harbach RE. The Anopheles (Anopheles) maculipennis complex (Diptera: Culicidae) in Greece. J Nat Hist. 2007; 41:2683–2699. pmid:27444437
- 7. White BJ, Collins FH, Besansky NJ. Evolution of Anopheles gambiae in relation to humans and malaria. Syst Rev Ecol Evol. 2011; 42:111–132.
- 8. Cooper RD, Waterson DG, Frances SP, Beebe NW, Pluess B, Sweeney AW. Malaria vectors of Papua New Guinea. Int J Parasitol. 2009;39:1495–1501. pmid:19505467
- 9. O’Connor CT, Sopa T. A checklist of the mosquitoes of Indonesia. A special publication of the U.S. Naval Medical Research Unit No. 2, Jakarta, Indonesia. NAMRU-SP-45. 1981;1–26
- 10. Soemarlan, Gandahusada S. The fight against malaria in Indonesia: a historical review and future outlook. National Institute of Health Research and Development, Ministry of Health, Republic of Indonesia. 1990;1–63
- 11. Elyazar IRF, Sinka ME, Gething PW, Tarmisi SN, Surya A, Kusriastuti R, et al. The distribution and bionomics of Anopheles malaria vector mosquitoes in Indonesia. Rollinson D. (ed.). Adv Parasitol. 2013; 83:173–266. pmid:23876873
- 12. Takken W, Snellen WB, Verhave JP, Knols BGJ, Atmosoedjono S. Environmental measures for malaria in Indonesia–a historical review on species sanitation. Wageningen Agricultural University Papers 90.7. Veenman Drukkers, Wageningen. 1990;1–167. Available from: https://edepot.wur.nl/282643
- 13. Baimai V, Kijchalao U, Rattanarithikul R. Metaphase karyotypes of Anopheles of Thailand and Southeast Asia: V. The Myzomyia Series, subgenus Cellia (Diptera: Culicidae). J. Am Mosq Contr Assoc. 1996;12:97–105
- 14. Linton YM, Harbach RE, Chang MS, Anthony TG, Matusop A. Morphological and molecular identity of Anopheles (Cellia) sundaicus (Diptera: Culicidae), the nominotypical member of a malaria vector species complex in Southeast Asia. Syst Entomol. 2001;26: 357–366. https://doi.org/10.1046/j.1365-3113.2001.00153.x
- 15. Dusfour I, Harbach RE, Manguin S. Bionomics and systematics of the Oriental Anopheles sundaicus complex in relation to malaria transmission and vector control. Am J Trop Med Hyg. 2004;71:518–524. pmid:15516652
- 16. Sukowati S, Baimai V. A standard cytogenetic map for Anopheles sundaicus (Diptera: Culicidae) and evidence for chromosomal differentiation in populations from Thailand and Indonesia. Genome 1996; 39:165–173. pmid:18469885
- 17. Sukowati S, Baimai V, Harun S, Dasuki Y, Andris H, Efriwati M. Isozyme evidence for three sibling species in the Anopheles sundaicus complex from Indonesia. Med Vet Entomol. 1999;13: 408–414. pmid:10608230
- 18. Nanda N, Das MK, Wattal S, Adak T, Subbarao SK. Cytogenetic characterization of Anopheles sundaicus (Diptera: Culicidae) population from Car Nicobar Island, India. Ann. Entomol. Soc. Am. 2004; 97:171–176. https://doi.org/10.1603/00138746(2004)097[0171:CCOASD]2.0.CO;2m
- 19. Alam MT, Das DK, Ansari MA, Sharma YD. Molecular identification of Anopheles (Cellia) sundaicus from the Andaman and Nicobar islands of India. Acta Tropica, 2006; 97:10–18. pmid:16125659
- 20. Dusfour I, Blondeau J, Harbach RE, Vythilingham I, Baimai V, Trung HD, et al. Polymerase chain reaction identification of three members of the Anopheles sundaicus (Diptera: Culicidae) complex, malaria vectors in Southeast Asia. J Med Entomol. 2007; 44:723–731. https://doi.org/10.1603/0022-2585(2007)44[723:pcriot]2.0.co;2 pmid:17915501
- 21. Linton YM, Dusfour I, Howard TM, Ruiz LF, Duc Manh N, Ho Dinh T, Sochanta T, Coosemans M, Harbach RE. Anopheles (Cellia) epiroticus (Diptera: Culicidae), a new malaria vector species in the Southeast Asian Sundaicus Complex. Bull. Entomol. Res. 2005; 95:329–339. pmid:16048681
- 22. Dusfour I, Linton LM, Cohuet A, Harbach RE, Baimai V, Trung HD, et al. Molecular evidence of speciation between island and continental populations of Anopheles (Cellia) sundaicus (Diptera: Culicidae), a principal malaria vector taxon in Southeast Asia. J Med Entomol. 2004;41:287–295. pmid:15185927
- 23. Zarowiecki M, Linton YM, Post RJ, Bangs MJ, Htun PT, Hlaing T, et al. Repeated land mass reformation limits diversification in the widespread littoral zone mosquito Anopheles sundaicus sensu lato in the Indo-Oriental Region. Mol Ecol. 2014; 23:2573–2589. pmid:24750501
- 24. Rodenwaldt, E. Entomologische notities. III. Genees. Tijdsch. v. Nederlandsch-Indië 1925;65:173–201
- 25. Dusfour I, Michaux JR, Harbach RE, Manguin S. Speciation and phylogeography of the Southeast Asian Anopheles sundaicus complex. Infect. Genet Evol 2007;7:484–493. pmid:17350896
- 26. Syafruddin D, Bangs MJ, Sidik D, Elyazar I, Asih PBS, Chan K, et al. Impact of the spatial repellent on malaria incidence in two villages in Sumba, Indonesia. Am J Trop Med Hyg 2014;91(6): 1079–1087. pmid:25311699
- 27. St. Laurent B, Sukowati S, Burton TA, Bretz D, Zio M, Firman S, et al. Comparative evaluation of anopheline sampling methods in three localities in Indonesia. Malar J. 2018;17:13. pmid:29310656
- 28. Collins FH, Paskewitz SM. A review of the use of ribosomal DNA (rDNA) to differentiate among cryptic Anopheles species. Insect Mole Biol. 1996;5:1–9. pmid:8630529
- 29. Cornel AJ, Porter CH, Collins FH. Polymerase chain reaction species diagnostic assay for Anopheles quadrimaculatus cryptic species (Diptera: Culicidae) based on ribosomal DNA ITS2 sequences. J Med Entomol. 1996;33:109–116. pmid:8906913
- 30. Walton C, Handley JM, Kuvangkadilok C, Collins FH, Harbach RE, Baimai V, et al. Identification of five species of the Anopheles dirus complex from Thailand, using allele-specific polymerase chain reaction. Med Veter Entomol. 1999;13:24–32. pmid:10194746
- 31. Reid JA. Anophelines of Malaya and Borneo. Government of Malaysia. Studies Institute Med. Res. Malaysia. 1968;31:1–520
- 32. Atmosoedjono S, Bangs MJ. Illustrated key to the female anophelines of Indonesia (O'Connor C.T., and Soepanto A., 1979): An English translation and revision. Ministry of Health, Jakarta, Indonesia. 1989;1–40
- 33. Wooden J, Kyesn S, Sibley CH. PCR and strain identification in Plasmodium falciparum. Parasitol Today. 1993;9:303–305. pmid:15463789
- 34. Felsenstein J. Confidence limits on phylogenies: An approach using the bootstrap. Evolution. 1985: 39:783–791. pmid:28561359
- 35. Tamura K, Nei M, Kumar S. Prospects for inferring very large phylogenies by using the neighbor-joining method. Proc. Nat. Acad. Sci. (USA). 2004: 101:11030–11035. pmid:15258291
- 36. Tamura K, Stecher G, Peterson D, Filipski A, Kumar S. MEGA6: Molecular evolutionary genetics analysis version 6.0. Mole. Biol. Evol. 2013:30: 2725–2729. pmid:24132122
- 37. Saitou N, Nei M. The neighbor-joining method: A new method for reconstructing phylogenetic trees. Mole. Biol. Evol. 1987: 4:406–425. pmid:3447015
- 38. Mayr E, Ashlock PD. Principals of Systematic Zoology. 2nd edition. McGraw Hill, New York. 1991. https://doi.org/10.2307/2412606
- 39. Donnelly MJ, Pinto J, Girod R, Besansky NJ, Lehmann T. Revisiting the role of introgression vs shared ancestral polymorphisms as key processes shaping genetic diversity in a recently separated sibling species of the Anopheles gambiae complex. Heredity. 2004;92:61–68. pmid:14666125
- 40. Foley DH, Wilkerson RC, Cooper RD, Volovsek ME, Bryan JH. A molecular phylogeny of Anopheles annulipes (Diptera: Culicidae) sensu lato: the most species-rich anopheline complex. Mole Phylo Evol. 2007;43:283–297. pmid:17126567
- 41. Avise JC, Arnold J, Bell RM, Bermingham E, Lamb T, Neigel JE, et al. Intraspecific phylogeography: The mitochondrial DNA bridge between population genetics and systematics. Annu Rev Ecol Syst. 1987; 18:489–422
- 42. Simon C. Molecular systematics at the species boundary: Exploiting conserved and variable regions of the mitochondrial genome of animals via direct sequencing from amplified DNA. In: Molecular Techniques in Taxonomy. Hewitt G. M., Johnston A. W. B., and Young J. P. W. (eds.). Springer-Verlag, Berlin. 1991; p. 35–71. https://doi.org/10.1007/978-3-642-83962-7_4
- 43. Allio R, Donega S, Galtier N, Nabholz B. Large variation in the ratio of mitochondrial to nuclear mutation rate across animals: implications for genetic diversity and the use of mitochondrial DNA as a molecular marker. Mol Biol Evol. 2017;34(11):2762–2772. pmid:28981721
- 44. Hoy MA. Insect molecular genetics: an introduction to principals and applications. Academic Press, San Diego. 1994
- 45. Suwonkerd W, Ritthison W, Ngo CT, Tainchum K, Bangs MJ, Chareonviriyaphap T. Vector biology and malaria transmission in Southeast Asia. In: Manguin S. (ed.). Anopheles Mosquitoes—New Insights into Malaria Vectors. InTech Open Access Publisher, Rijeka, Croatia. 2013. p. 273–325. https://doi.org/10.5772/56347
- 46. Reid JA. Systematics of malaria vectors–anopheline systematics and malaria control, with special reference to Southeast Asia. Misc Publ Entomol Soc Am. 1970;7:52–62
- 47. Syafruddin D, Bangs MJ, Sidik D, Elyazar I, Asih PB, Chan K, et al. Impact of a spatial repellent on malaria incidence in two villages in Sumba, Indonesia. Am J Trop Med Hyg. 2014 91(6):1079–1087. pmid:25311699
- 48. Trung HD, Van Bortel W, Sochantha TK, Keokenchanh NT, Quang LD, Cong, et al. Malaria transmission and major malaria vectors in different geographical areas of Southeast Asia. Trop Med Intern Hlth. 2014; 9:230–237. pmid:15040560
- 49. Ritthison W, Tainchum K, Manguin S, Bangs MJ, Chareonviriyaphap T. Biting patterns and host preference of Anopheles epiroticus in Chang Island, Trat Province, eastern Thailand. J Vector Ecol. 2014;39:361–371. pmid:25424266
- 50. Sumruayphol S, Apiwathnasorn C, Komalamisra N, Ruangsittichai J, Samung Y, Chavalitshewinkoon-Petmitr P. Bionomic status of Anopheles epiroticus Linton & Harbach, a coastal malaria vector, in Rayong Province, Thailand. Southeast Asian J Trop Med Publ Hlth. 2010;41:541–547. pmid:20578540
- 51. Chowanadisai L, Krairiksh S, Thanasripukdikul S. Microbial control of Anopheles sundaicus, a malaria vector in Thailand, by Bacillus sphaericus 2362. Mosq Borne Dis Bull. 1989; 6:39–44.
- 52. Phoomkhong W, Bangs MJ, Chareonviriyaphap T. Discriminating lethal concentrations for pyrethroid compounds used in susceptibility monitoring of Anopheles epiroticus, a malaria vector in Thailand. Acta Tropica. 2018;185:255–260. pmid:29856988
- 53. Indris-Idram NS, Sudomo M, Soejitno , Saptoro . Anopheles sundaicus as malaria vector of mangrove deforested coastal areas in Padang Cermin Subdistrict, South Lampung Regency, Indonesia [in Bahasa Indonesia]. Bull Penelit Kesehat. 2000;28:481–489
- 54. Davidson JR, Sukowati S, Shinta , Asih PBS, Syafruddin D, Baskin RN, et al. Using barrier screens to characterize mosquito composition, flight activity, and abdominal status in South Lampung, Indonesia. Parasit Vectors. 2018;11:440. pmid:30064507