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Revealing the microbiome diversity and biocontrol potential of field Aedes ssp.: Implications for disease vector management

Abstract

The mosquito Aedes spp. holds important relevance for human and animal health, as it serves as a vector for transmitting multiple diseases, including dengue and Zika virus. The microbiome’s impact on its host’s health and fitness is well known. However, most studies on mosquito microbiomes have been conducted in laboratory settings. We explored the mixed microbial communities within Aedes spp., utilizing the 16S rRNA gene for diversity analysis and shotgun metagenomics for functional genomics. Our samples, which included Ae. aegypti and Ae. albopictus, spanned various developmental stages—eggs, larvae, and adults—gathered from five semiurban areas in Mexico. Our findings revealed a substantial diversity of 8,346 operational taxonomic units (OTUs), representing 967 bacterial genera and 126,366 annotated proteins. The host developmental stage was identified as the primary factor associated with variations in the microbiome composition. Subsequently, we searched for genes and species involved in mosquito biocontrol. Wolbachia accounted for 9.6% of the 16S gene sequences. We observed a high diversity (203 OTUs) of Wolbachia strains commonly associated with mosquitoes, such as wAlb, with a noticeable increase in abundance during the adult stages. Notably, we detected the presence of the cifA and cifB genes, which are associated with Wolbachia’s cytoplasmic incompatibility, a biocontrol mechanism. Additionally, we identified 221 OTUs related to Bacillus, including strains linked to B. thuringiensis. Furthermore, we discovered multiple genes encoding insecticidal toxins, such as Cry, Mcf, Vip, and Vpp. Overall, our study contributes to the understanding of mosquito microbiome biodiversity and metabolic capabilities, which are essential for developing effective biocontrol strategies against this disease vector.

Introduction

Mosquitoes are insects with complete metamorphosis (holometabolous) since their larvae differ remarkably from the adult state in their anatomy, ecology, and feeding. Mosquitoes have four life stages: eggs, larvae, and pupae that are aquatic and the adult stage that flies. The larvae feed on insects carcasses and debris [1], while adults have a proboscis that allows them to feed on nectars, and in some species, females feed on blood [2]. The site where mosquitoes develop has been reported as one of the factors that shape their microbiome [35]. However, the abundance of each bacterium within the microbiome is determined by the mosquito stage, sex, and species [6]. The microbiome of mosquito eggs comprises Actinobacteria, Firmicutes, and Cyanobacteria [7]. These phyla are also found in larvae; however, as the aquatic stages develop, the bacterial diversity increases [5]. The adults develop wings during metamorphosis, and the mouth structure changes completely. The change in the adult diet results in essential changes in the microbiome. In adults, the microbiome diversity decreases and is dominated by Proteobacteria [8]. The high carbohydrate concentration favors Enterobacteria growth [5]. In females, iron intake generates free radicals, increasing the abundance of Enterobacteriaceae and Flavobacteriaceae [5, 9, 10]. It is interesting that in the laboratory, Ae. aegypti adults from different parts of the world converge on a very similar microbiome [11]. In addition, vertical transmission of Wolbachia has been reported in mosquitoes. This intracellular bacterium has been identified in more than 60% of insects worldwide [12].

Recent studies on the gut microbiota of field collected Aedes spp. Mosquitoes reveal a limited diversity at higher taxonomic levels across various geographical regions. The free living adults are also dominated by Proteobacteria joined by Actinobacteria, Bacteroidetes, and Firmicutes [6]. Common bacterial families such as Pseumonadaceae, Enterobacteriaceae, Acetobacteraceae, Rickettsiaceae, and Moraxellaceae have been identified as widespread through these vectors [6, 13]. These findings are consistent across different species of wild mosquitoes, including Anopheles spp. [14]. Notably, inter-individual variability in microbiota composition is high, with some OTUs being exclusive to individual mosquitoes [13, 15]. Mosquito microbiota are afected by the blood source they feed on; human blood-fed mosquitoes harbor an array of human skin-associated bacteria [7]. It has been validated in the field that the microbiome of free-living larvae is determined by their habitat [16]. Interestingly, in the field, it has been observed that the microbial diversity of larvae has different taxa than that of adults before they feed [17]. Many of the studies in free living mosquito have focused on monitoring Wolbachia infection for control campaigns. Wolbachia genus is commonly found in Ae. albopictus [18]. However, in some countries of the world, the presence of Wolbachia in Ae. aegypti has not been detected [19], while in some studies, Wolbachia has been found [20, 21].

Aedes spp. is a global problem, as it transmits different diseases in humans and animals. They are reported as the main vector for dengue fever, chikungunya, and Zika virus [22]. Controlling mosquito populations is the most efficient way to prevent these viral diseases. Global climate change has allowed the displacement of mosquitoes to new places. Aedes aegypti that used to be in tropical regions are now detected in large cities in temperate regions [23]. The distribution of mosquitoes in these new places increases the need to improve the types of biocontrol strategies. Two bacterial biocontrol strategies have been successfully used to control mosquitoes: Bacillus thuringiensis as a larvicide [24] and Wolbachia spp. by interfering with the development of mosquitoes and protecting them from diseases [25]. Bacillus thuringiensis spores are added in food pellets to the water where the larvae grow [26]. Spore toxins kill larvae by forming pores in the midgut epithelium. These pores cause osmotic shock in the cells, leading to larval dehydration and death [27]. In contrast, Wolbachia gives rise to cytoplasmic incompatibility (CI). Embryo development is prevented when the male is infected and the female is not infected. Wolbachia has been used in two types of biocontrol strategies. In the first strategy, the incompatible insect technique (IIT), males transfected with a Wolbachia strain that does not exist in the wild are released; due to CI, these males reduce the mosquito population [28]. In the population replacement strategy (PRS), male and female mosquitoes are released with a Wolbachia strain that confers viral protection; this Wolbachia is fixed by CI [29].

Biocontrol strategies have been successful where they have been applied, but the different groups of microorganisms used as insecticides in mosquitoes have tended to lose effectiveness due to insect adaptation [26, 30]. Therefore, identifying new candidates for biocontrol use (whether new varieties of known species or new microorganisms) and determining the scope of the strategies already implemented in other insect populations is essential. Here, we describe the microbiome of Aedes ssp. in south-central Mexico and investigate the mosquito microbiome in real-world communities; our study remarks on the relevance of exploring microbial diversity in natural mosquito populations. Hence, we investigated bacterial diversity using 16S amplicons and microbial community metabolic capacity using shotgun metagenomics. Furthermore, we identified genes coding for insecticidal toxins carried by mosquitoes captured in semiurban environments. We defined the composition of bacteria previously reported as possible biocontrol agents. Our goal is to delve into overall diversity and coding genes to gain insights into mosquito-microbe interactions and contribute to the continuing development of microbe-directed mosquito biocontrol procedures.

Materials and methods

Sampling

We analyzed 14 samples, each representing a unique site and a specific developmental stage of mosquito populations. For each of the samples, we gathered 30 individuals to ensure enough DNA for metagenomic analysis. In the case of adult mosquitoes and larvae, all dissected organs were combined into a single sample. All larvae were obtained from the same water tank, and similarly, all eggs were collected from the same ovitrap. For the collection of adults, it was necessary to search for them in one to four houses within the same neighborhood.

Five localities in Mexico were sampled in June and July 2016 (rainy season). These localities have an incidence of dengue. The sampling sites were chosen based on the advice of the National Center for Disease Control and Prevention Programs (CENAPRECE). All the sites were semiurban single-family houses with roofs, ground-open water tanks, and electricity. The houses could have drainage, septic tanks, or latrines. Some houses had windows that were always open (no glass) or pets. Geographic location, temperature, and pressure data were collected (S1 Table in S1 File). Eggs were sampled from ovitraps that were one-liter plastic containers with a filter paper placed half way down. Females oviposited in the aerial paper section. Larvae were collected from the house’s water tanks or buckets, that were outdoors, using a plastic Pasteur pipette and deposited in jars with distilled water. Adult mosquitoes were collected from the indoors air with vacuum cleaners adapted with filters.

On the sampling day, the specimens were transported to the laboratory, adults and larvae were identified, and adults were separated by sex. The preliminary taxonomic analysis was conducted utilizing a stereoscopic microscope, coupled with the entomological expertise of CENAPRESE personnel. Larvae were classified by species employing dichotomous keys as per Mañez-Bernal & Martinez-Campos [31]. The species and sex of adults were determined using the pictorial key by Rueda [32]. While the intent was to exclusively collect Ae. aegypti, subsequent DNA analysis also revealed the presence of Ae. albopictus. The morphological assessment enabled us to exclude sites where Culex genus mosquitoes were prevalent.

During the four hours after the collection, the dissection was carried out. Larvae and adults were dissected to obtain intestines, salivary glands, ovaries, and Malpighian tubes [33]. Larvae were rinsed with water before disection procedure. Females displaying a red abdomen indicative of recent blood consumption were excluded to maximize the extraction of mosquito-derived bacterial DNA. No further analyses were conducted to determine whether the individuals had previously ingested blood. The organs of each individual were stored in batches of 30 individuals. The eggs were carefully removed with a clean spatula. Adult and larvae batches were resuspended in 3 ml of Hank’s salt medium (Sigma‒Aldrich) and kept at -80°C until processing. Eggs were sotored dry. The handling of the samples was carried out with gloves. All solutions, tubes, and tips were sterile, while work surfaces and laboratory equipment were constantly cleaned with 70% ethanol.

Ethics statement

No specific permits were required to collect field mosquitos since Ae. Aegipty, Ae albopictus or Culex are not listed on the Red List of the International Union for Conservation of Nature (IUCN; http://www.iucnredlist.org/search). Moreover, mosquitoes, particularly Aedes spp. are classified within the national standard NOM-032-SSA2-2014 (for Epidemiological Surveillance, Promotion, Prevention And Control Of Vector Transmitted Diseases) as vectors requiring epidemiological surveillance and regular monitoring. The collection of eggs, larvae, and adult mosquitoes was carried out employing the methodology and as part of the control activities endorsed by the National Center for Disease Control and Prevention Programs (CENAPRECE), adhering to the guidelines set forth in the "Methodological Guide for Entomovirological Surveillance’’. We obtained oral consent from the homeowners where the sampling was conducted. The project has been registered within Universidad Autonoma Metropolitana under the number UAMC-DCN-47301018.

DNA extraction and sequencing

DNA extraction was performed with PowerSoil DNA Isolation Kit (Qiagen) following the manufacturer’s instructions and optimized with phenol‒chloroform. Briefly, sample batches (approximately 250 μL) were vortexed for 10 min in bead tubes with 60 μL of C1 solution, 100 μL chloroform (Sigma‒Aldrich), and 100 μL phenol (Sigma‒Aldrich). Next, 16S ribosomal amplicons were generated using the 341F (5’-CCTACGGGNGGCWGCAG-3’) and 805R (5’-ACTACHVGGGTATCTAATCC-3’) primers. These amplified V3-V4 regions had a fragment size of approximately 464 bp. Amplicon sequencing was performed using the MiSeq Illumina platform (2x300 bp). Microbial DNA enrichment was performed for shotgun sequencing using the NEBNext® Microbiome DNA Enrichment Kit (New England Biolabs, NEB) following the manufacturer’s instructions. For shotgun sequencing, the Illumina NextSeq system (2x150) was utilized. Both 16S amplicon and shotgun sequences were generated using the LABSERGEN Langebio Cinvestav Irapuato platform.

Sequence processing

Raw amplicon sequences were pair-end merged using CASPER [34]. Joined sequences were matched for 97% similarity using CD-HIT-EST [35]. One sequences for each OTU was selected using QIIME [36]. Taxonomic assignment was performed using the SILVA [37] database. Singletons and chimeras were removed using Chimera Slayer [38].

Shotgun reads were host filtered with bowtie2. Sequences were aligned with the genome from Ae. aegypti (strain LVP_AGWG, PRJNA318737). Subsequently, all nonhost sequences were quality filtered with Trimmomatic. The resulting sequences were assembled using SPADES [39]. A second assembly was performed with Velvet [40] for sequences discarded by SPADES. The resulting sequences (contigs and unassembled sequences) were annotated using BLAST [41] and DIAMOND [42] using the nonredundant M5nr database. The annotation obtained was compared with the application programming interfaces (APIs) of interest: PATRIC [43], RefSeq [44], and Ontology [45]. The taxonomic assignation was performed using Kraken [46]. The Bacterial Pesticidal Protein Resource Center database was used for toxin identification [47]. The molecular taxonomic classification of the mosquitoes was performed by identifying the ITS2 sequences directly from the reads, to avoid any chimera, followed by a BLAST against the RefSeq database [44]. Genome recruitments were performed from the raw sequences per sample using bowtie2 [48] and compared with reference genomes to determine resemblance and abundance within the metagenomes. The bacterial reference genomes used were Wolbachia wMel from Drosophila melanogaster ASM1658442v1 (NCBI NZ_CP046925.1), Wolbachia wPip from Culex quinquefasciatus (NCBI PRJNA30313), and Wolbachia wAlbB from Ae. aegypti (NCBI PRJEA76855).

Statistical analysis

After the construction of the OTUs, ASV and shotgun metagenomic data were processed using R project standard functions or R packages such as "phyloseq2" [49] and "ggplot2" [50]. Alpha diversity metrics were calculated using the OTUs generated from the amplicon sequences of the 16S ribosomal gene, utilizing the “phyloseq2” package. Comparative analyses were performed, generating upset graphs and nonmetric dimensional scaling using Bray‒Curtis distance.

Phylogenetic analysis

The OTUs assigned to Wolbachia and Bacillus were compared with the closest sequences of reference-type strains obtained from RDP [51] and RefSeq [44]. The sequences of the two OTU groups and their references were aligned using SSU-align [52], and the trees were built using FastTree [53] with default options (NJ and 1000 resamples). The trees were edited and annotated for presentation with iTol [54].

Results

Aedes spp. microbiome general description

All mosquitoes were collected from five locations in Mexico (S1 Fig in S1 File). These semiurban areas are characterized by a warm subhumid climate. Our study analyzed 14 samples, each representing a unique site and a specific developmental stage of the mosquito lifecycle, including eggs, larvae, female adults, and male adults. For each sample, we collected 30 individuals. Unfortunately, larvae and eggs were sourced from only two locations. Prior to molecular analysis, we had performed a taxonomic identification of the Aedes spp. Mosquitoes by morphological characterization. Of the 14 samples subjected to 16S gene amplicon analysis, eight underwent additional shotgun sequencing, encompassing all life stages of mosquitoes from the two sites. Through ITS2 analysis on these eight samples, we determined that four samples consisted exclusively of Ae. aegypti (samples: larvae_s1, larvae_s2, females_s1, male_s1), while the other four were a mix of Ae. albopictus and Ae. aegypti (samples: eggs_s1, eggs_s2, females_s2, male_s2) (S1 Table in S1 File). We obtained 1,882,521 amplicon reads of the 16S gene clustered into 8,346 OTUs from 967 genera. In addition, we obtained 118,220,137 filtered reads from shotgun sequencing, from which 126,366 bacterial proteins were annotated (S2 Table in S1 File). We also analyzed the diversity using ASV to enable these data to be compared with many other datasets. The general descriptions are similar, although the precise numbers change. The most significant difference with the OTU analysis lies in the exclusion of rare organisms. We detected 4,829 ASVs from 563 genera (S2 Table in S1 File, and S2 Fig in S1 File).

Alpha diversity indexes were estimated through analysis of the 16S data. Diversity during the aquatic life stages (Simpson index 4.7 ± 0.4) exceeded that observed in adult stages (Simpson index 2.0 ± 0.5). This pattern of diversity was consistent across all assessed metrics (richness, Shannon, Simpson, and Chao1) (S3, S4 Tables in S1 File). Amplicon analysis showed that the phylum Proteobacteria was the most abundant (67.8%), whereas the other phyla had much lower values, i.e., Actinobacteria (11.3%), Firmicutes (10.3%), Bacteroidetes (5%), and Cyanobacteria (1.3%). Proteobacteria were more abundant in the adult stages (73.3% adults and 35.8% aquatic), and Actinobacteria were more abundant in the aquatic stages (5.6% adults and 30.1% aquatic). Interestingly, photosynthetic Cyanobacteria and Chloroflexi were more abundant in the aquatic stages (Fig 1, S3 Fig in S1 File, and S5 Table in S1 File). Shotgun reads were also classified taxonomically.

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Fig 1. Phylogenetic profile of Ae. aegypti microbiome from 16S amplicon sequences.

A) Genus distribution. B) Phyla distribution. C) Beta diversity plot (nonmetric multidimensional scaling, NMDS).

https://doi.org/10.1371/journal.pone.0302328.g001

The predominant OTUs in the complete system are those abundant in adult mosquitoes, whereas they are not the dominant ones in eggs and larvae. The dominant adult OTUs corresponded to the genera Zymobacter sp., Bacillus sp., Wolbachia sp., Enterobacter sp., and Ornithimicrobium sp., whereas Pseudoxanthomonas sp. was dominant in eggs (S6 Table in S1 File). The comparative set analysis shows that 190 genera were shared across developmental stages, although only 16 were detected in all samples. The eggs were the most diverse and had 223 unique genera. Despite being in the same developmental stage, only 288 genera were shared between females and males, whereas eggs and larvae shared 392 genera, including the 190 ubiquitous genera (S4 Fig in S1 File).

Metagenome analysis showed that 49.7% of the shotgun reads belonged to bacteria. We detected many fungal sequences, and 43.5% of the shotgun sequences belonged to the phylum Ascomycota. Bacteria were more abundant in the adult stages (70.5% adults and 28.9% aquatic) (S7 Table in S1 File). We grouped the samples by developmental stage and not by sample location because the beta diversity analyses suggested that there was community similarity (Fig 1, and S5 Fig in S1 File).

Through the analysis of metagenomes, we assessed the metabolic capabilities of the microbiome. Notably, the ’female_s1’ sample exhibited a significantly higher proportion of genes associated with respiration, accounting for 76%, an evident contrast to the 3–5% observed in other samples (Fig 2). This rise in respiration is primarily attributed to an increase in the gene for cytochrome oxidases and respiratory complex I (S6 Fig in S1 File). Intriguingly, genes related to virulence and defense were found to be more prevalent during the egg and larvae stages, with percentages ranging from 3 to 6%, than in adults, where they accounted for only 0.9 to 1.6%. This suggests a reduction in these genes as development progresses. Within this metabolic category, we also noted a shift in gene types; eggs and larvae predominantly featured ton and tol trasport genes and efflux pumps, whereas in adults, type I and IV secretion systems were more abundant. In aquatic samples, phosphate metabolism genes were overrepresented, whereas adults showed a higher abundance of maltose and maltodextrin utilization genes. Certain genes, such as those for DNA replication and peptidoglycan synthesis, were highly represented across all samples. Across the entire system, the most prevalent metabolic category comprised gene groups (i.e. clustering based subsystems) that are not yet well-described, underscoring the importance of continuing research in bacterial physiology and classical genetics (Fig 2). Beta diversity analyses, including NMDS and PCoA of the metagenomic data, demonstrated that samples clustered according to the developmental stage (S7 Fig in S1 File).

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Fig 2. Ae. aegypti metabolic profiles from shotgun sequences.

The SEED subsystems are shown to describe the main metabolic features.

https://doi.org/10.1371/journal.pone.0302328.g002

Potential biocontrol agents

We searched for microbes and genes that could be used for the biocontrol of mosquitoes. We incorporated insights from comprehensive reviews by Scolari et al., [6] and Gao et al., [55], which highlighted a spectrum of microbes already identified as pathogens [6, 55]. Additionally, we inspected the classifications of entomopathogenic activity mechanisms, drawing upon the frameworks set by Crickmore et al., [47] and the Bacterial Pesticidal Protein Database [47]. Our search was targeted towards microbes and genes that held potential for the biocontrol of mosquitoes, leading to the identification of multiple genera of interest due to their known insecticidal properties and relevance to biocontrol. We identified multiple bacteria with known biocontrol interest: Bacillus, Wolbachia, Serratia, Enterobacter, Spiroplasma, Rickettsia, Lysinibacillus, and Clostridium. We also identified several genera of fungi already reported to have entomopathogenic activity: Smittium, Conidiobolus, Metarhizium, Tolypocladium, Pythium, and Beauveria.

We identified 519 contigs containing coding genes for biosynthesis of 102 different toxins (Fig 3). The Crystal type (Cry) protein was the most abundant insecticidal toxin, with 371 sequences assigned to 78 Cry protein families. Cry8Ma2 stood out with 87 sequences, and Cry1Ib6 had 35 sequences. The other group of frequent toxins was the Make Caterpillars Floppy (Mcf) group, with 74 sequences assigned to four different Mcf clusters. Other groups of toxins identified included alpha-helical pesticidal protein (App); nonspecific cytolytic (Cyt); membrane attack complex/perforin (Mpf); Mtx2-related pesticidal protein (Mpp); mosquitocidal Mtx1 protein (Mtx); toxin-10 pesticidal proteins (Tpp); vegetative insecticidal protein (Vip); Vip2, the active component of the Vpa/Vpb binary pesticidal protein (Vpa); Vip1, the binding domain of the Vpa/Vpb binary pesticidal protein (Vpb) and holding class for pesticidal proteins (Xpp) (Fig 3). The samples with the most toxins were the eggs from site 2 (29 toxins, 129 sequences) and the females from site 2 (28 toxins, 157 sequences). In general, each toxin was observed only in one sample. Two toxin genes were shared between egg samples and four between females and males from site 2. In one larval sample, no toxin was detected, and in one female sample, only one gene was detected (Fig 3).

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Fig 3. Insecticidal toxins detected in metagenomic shotgun sequences.

The heatmap shows the observed sequences annotated as toxins in the Bacterial Pesticidal Protein Resource Center database. Each toxin type is highlighted in different colors. The Crystal type (Cry) protein family encompasses 78 representative sequences.

https://doi.org/10.1371/journal.pone.0302328.g003

A dominant group in the mosquito microbiome was the genus Bacillus. We identified 221 OTUs from Bacillus, representing 12% of sequences (143,775) (S8 Table in S1 File). Bacillus OTUs were identified as B. cereus, B. pumilus, B. firmus, B. aquimaris, B. vallismortis, B. thuringiensis, and Bacillus sp. We constructed a 16S phylogenetic tree with the Bacillus sequences to describe their diversity in the mosquito microbiome. The Bacillus tree showed that the populations were divided into two groups: eggs and females. To identify the phylogenetic placement of the OTUs, the tree included sequences from reference strains. There were 13 Bacilli in the clade of B. cereus that came from aquatic and adult stages. However, none were identical to B. cereus or B. thuringiensis type strains. Only two OTUs were detected in all four stages, including the most abundant, corresponding to B. seohaeanensis and B. pseudofirmus (Fig 4).

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Fig 4. Bacillus diversity in mosquito microbiomes.

A) Neighbor-joining tree of the Bacillus OTUs along with ATCC reference strains of Bacillus thuringiensis, B. cereus, B. amyloliquefaciens, B. subtilis, and B. atrophaeus. B) UpSet diagram of the distribution of Bacillus shared OTUs.

https://doi.org/10.1371/journal.pone.0302328.g004

The genus Wolbachia was found in various samples in a nonhomogeneous pattern. We assigned 203 Wolbachia OTUs with more than two occurrences from 115,296 sequences (S9 Table in S1 File). These constituted 9.6% of the total system. However, the Wolbachia abundance in each sample ranged from 0 to 32%. In the sample ’males_s2,’ no OTUs were detected despite the identification of Ae. albopictus within that sample. While in the samples exclusive to Ae. aegypti, only six Wolbachia OTUs were present, which also appeared in other samples. Adult samples exhibited a shared presence of 116 OTUs. As expected, the presence of Wolbachia in aquatic stages was minimal for all samples (0.037%). Wolbachia was not found in males from site 2. In contrast, females from site 3 showed 158 Wolbachia OTUs. Wolbachia abundances or diversities were not similar within a sampling location or sex (S9 Table in S1 File). A phylogenetic tree was constructed for a more detailed description, including reference sequences (Fig 5). The tree showed that the OTUs corresponded primarily to strains of Wolbachia from supergroup B, and 9 OTUs were associated with supergroup A. However, both supergroups were abundant and prevalent among Wolbachia OTUs.

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Fig 5. Wolbachia diversity in mosquito microbiomes.

A) Neighbor-joining tree of the Wolbachia 16S rRNA gene OTUs. Rickettsia canadensis, Gordonia lacunae, and Salmonella enterica were used as outgroups. OTUs from Supergroup A are highlighted in blue, while Supergroup B is highlighted in yellow. B) UpSet diagram of the distribution of Wolbachia shared OTUs.

https://doi.org/10.1371/journal.pone.0302328.g005

The recruitment of Wolbachia sequences in the metagenomes was conducted to understand similarities to Wolbachia previously isolated from Aedes mosquitoes and other Diptera, such as Culex and Drosophila. We used three strains of Wolbachia as reference genomes: wAlbB (PRJEA76855), wPip (PRJNA30313), and wMel (NZ_CP046925.1). The sample from site 2 presented more Wolbachia sequences, so the recruitment of that sample had better coverage. The genome coverage of the wAlbB strain was almost complete in the sample from the female from site 2 (wAlbB 83.05%, wMel 60.72%, and wPip 58.46%). The wAlbB recruitment showed a distribution across the entire genome of sequences with identities of 100%, so it is feasible that this strain was in this sample. Recruitment also confirmed Wolbachia diversity because there were many hits with identities between 85 and 99% throughout the genome (Fig 6 and S9 Table in S1 File).

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Fig 6. Recruitment of Wolbachia.

Wolbachia genomes analyzed against the sample of females from site 2. A) wAlbB PRJEA76855. B) wPip PRJNA30313. C) wMel NZ_CP046925.1.

https://doi.org/10.1371/journal.pone.0302328.g006

We searched for cif genes associated with cytoplasmic incompatibility generated by Wolbachia. Cif genes were only identified in the adult samples from site 2, which were the samples with the highest number of Wolbachia sequences. We identified 425 sequences corresponding to four cifA and 16 types of cifB. The genes were similar to Wolbachia cif genes found in Culex pipientis, Nasonia oneida, and Ceratitis capitata (S9 Table in S1 File).

Discussion

The microbiome of the Aedes spp. collected in Mexico was similar to those already reported for field and laboratory mosquitoes. Proteobacteria, Actinobacteria, and Firmicutes were the most abundant phyla; together, they accounted for 89% of the system, and an increase in Proteobacteria was observed in the adult stage [6, 5658]. We observed a doubling of Proteobacteria in adults (from 35 to 73%), which is expected due to the change in diet. For females, blood intake promotes the growth of bacteria tolerant to reducing oxide environments [9]. Genera exhibited a unique distribution pattern across each sample, with only 16 genera consistently present throughout. We observed a small core and a high proportion of rare OTUs, suggesting stochasticity within their natural environment [59]. This could also be indicative of intense competition among the bacteria or temporal instability within the bacterial communities. Studies focusing on isolated individuals have demonstrated significant variability between individuals, aligning with the observed small core [15, 60]. As in other studies, we detected that the most abundant egg genus is Pseudodoxanthomonas [56, 61]. Mycobacterium is the most abundant genus in larvae (in agreement with Zouache [16]). It is not typical for Zymobacter to be dominant in adults; however, its presence is typical [62], and in a field study in Malaysia, Zymobacter was also one of the most frequent bacteria [63].

Our beta diversity analyses demonstrated that the mosquito developmental stage is the primary determinant of the mosquito microbiome. However, other studies of field mosquitoes have suggested that the sampling site is a significant factor in shaping mosquito microbiomes [6]. In our case, the impact of the developmental stage appears to have been more substantial than that of the location or microenvironment characteristics. Additionally, the variability in species presence—some samples containing only one species and others two—also proved to be a less critical factor than the developmental stage. Yet, we cannot completely dismiss the potential influence of the collection site in this study, as only one sample per site per state was examined.

The female samples exhibited little resemblance to each other. In particular, the female sample S1 is dominated by Pantoea and Ornithinimicrobium. Pantoea is an aerobic bacterium; it is commonly found in insects, and has been reported to boost insect fitness by metabolizing a wide range of compounds, including toxic substances [64]. This ability to compete and survive in various environments makes numerous species within this genus attractive candidates for biocontrol and bioremediation applications [64]. Ornithinimicrobium is also aerobic, and remains largely uncharacterized in terms of its metabolic or ecological traits. The observed taxonomic diversity between female samples corresponds to distinct metabolic gene patterns. It is documented that adults’ microbiomes resemble those of pupae upon emergence; however, the microbiome undergoes a complete transformation after the first feeding and can be shaped by different blood meal sources or the elapsed time post-blood ingestion [5, 65, 66]. The microbiome of adult mosquitoes is molded by the accessibility of varied food sources, such as differences in nectar and blood [10]. Our sampling protocol does not provide the means to ascertain whether the females had previously fed or if other environmental factors may have influenced the microbiome. The substantial proportion of genes related to respiration in the female sample from site 1 suggests that these mosquitoes have likely blood fed. Aquatic samples display a more diverse metabolism, and despite differences in bacterial genera, they show high metabolic resemblance. Genes associated with virulence, disease, and defense are found to be less prevalent in the adult stages.

The shotgun sequencing analysis also allowed us to detect fungi associated with these mosquitoes. In eggs and larvae, Mycosphaerella was widely dominant. Mycosphaerella is a pest found in Diptera from plant galls [67]. In adults, the most common fungi were Aspergillus and Metarhizium. Aspergillus is a ubiquitous filamentous fungus that is typically found in the soil but is also capable of colonizing insects such as Tenebrio molitor, Apis mellifera, and Anopheles coluzzii [68]. In Ae. aegypti, the Aspergillus prevalence was between 4 and 7% of adult samples. Interestingly, some species of the Aspergillus genus have been reported to have entomopathogenic functions in mosquitoes [69]. Like Aspergillus, Metarhizium is a soil fungus that includes entomopathogenic species. M. anisopliae is commercially produced as a biocontrol agent against agricultural pests, including mosquitoes [70]. In addition, Metarhizium coinfection decreased the load of dengue virus in female Ae. aegypti [71]. Moreover, transgenic M. anisopliae have been developed that prevent Plasmodium transmission [72]. The disadvantage of using M. anisopliae as a biocontrol agent is that it is not specific to mosquitoes [70]. It is worth mentioning that in our samples, 3.91 and 0.66% of the adult female sequences corresponded to Plasmodium.

Detection of Wolbachia in mosquitoes is highly variable. Wolbachia has been reported as a prevalent and the most abundant taxon for Ae. albopictus [8]. Numerous investigations have failed to identify Wolbachia in Ae. Aegypti [30, 73, 74]. Nevertheless, Wolbachia has been found in Ae. aegypti in the Philippines, Thailand, and Panamá in low abundance [21,59, 75]. Numerous studies have been directed towards detecting Wolbachia, given its significance for biocontrol. Most research has employed endpoint PCR using specific primers for Wolbachia supergroups A and B. Additionally, a variety of other methods have been utilized, including PCR, real-time PCR (qPCR), restriction fragment length polymorphism (RFLP), multilocus sequence typing (MLST), and massive sequencing of the 16S ribosomal gene [76]. A major limitation of amplifying specific sequences is the potential to miss other strains. For massive 16S sequence analyses, a notable constraint is that when using Amplicon Sequence Variants (ASVs), the less abundant sequences are often discarded [77]. These methodological differences could be the reason for the high Wolbachia diversity observed in our study.

Although we determined that the presence of Wolbachia was null for some samples and sites, in other samples, Wolbachia was one of the most abundant OTUs. We identified 203 OTUs, which constituted 6% of the amplicon sequences; most corresponded to the Wolbachia B supergroup, and nine OTUs corresponded to the A supergroup. Wolbachia strains are divided by molecular differences into eight phylogenetic supergroups (A-H). Wolbachia supergroups A and B are commonly associated with arthropods and have both been detected in Aedes spp. [78]; co-infection of both groups is even prevalent in Ae. albopictus [21]. Experiments using qPCR have demonstrated that group B is more abundant [66]. Genomic analyses indicate a low frequency of intergroup recombination, suggesting that the supergroups occupy distinct niches (Wang et al., 2020). The variation in strain diversity and the sporadic occurrence of Wolbachia imply that, at least for the less common strains, vertical transmission of Wolbachia in Aedes ssp. is inefficient and no solid symbiotic relationship promotes the natural selection of infected mosquitoes. In addition, only two strains were observed in eggs and five in larvae, suggesting that most Wolbachia colonization occurs in the adult stage.

Cytoplasmic incompatibility (CI) biocontrol in Ae. aegypti has been carried out with Wolbachia-free mosquitoes [79], but in mosquitoes naturally infected with Wolbachia, like Ae. albopictus, cytoplasmic incompatibility processes have been generated by crossing a different phylogenetic group from the same mosquito species or other species, such as D. melanogaster [80]. Notably, we did not observe the wMel strain used in biocontrol experiments in the field. In this work, we found that the diversity of sequences associated with cifA was much lower than that of cifB (4 and 16 genes, respectively). However, we do not know the potential activity of these genes to recover CI.

The Wolbachia distribution in Aedes spp. suggests that biocontrol by release from Wolbachia-transfected mosquitoes could have different efficiencies in different populations of Aedes spp. These biocontrol strategies depend on cytoplasmic incompatibility (CI), directly in the case of the incompatible insect technique (IIT) or to amplify the effect of the population replacement strategy (PRS). When vertical transfer is not efficient, CI is not efficient; the possibility of a diversity of Wolbachia in females could include rescue by cifA expression in females [81]. Cytoplasmic incompatibility rescue becomes less likely than vertical transmission when the introduced strain has a different phylogenetic origin, whereas vertical transmission efficiency can be improved with temperature-resistant Wolbachia strains [30]. Regardless, the results using PRS are impressive. In Indonesia, it was possible to reduce the incidence of dengue by 77% owing to the release of mosquitoes transfected with wMel [82].

We identified 221 Bacillus OTUs, of which 13 corresponded to the Bacillus thuringiensis and B. cereus groups. Because we detected 78 Cry toxins, we assumed the presence of Bt. We found that the B. thuringiensis clade is only abundant in the aquatic stages of the mosquito life cycle, which could indicate its adult toxicity. The genes for Cry and Mcf toxins found in different samples in apparently healthy specimens would not prevent consideration of these toxins or bacteria as biocontrol agents. In total, 102 toxins were identified, including Cry toxins. The gene sequences of these toxins differ from those previously reported, so samples from free-living mosquitos are an excellent source of toxin biodiversity.

We also detected other bacteria with mosquito biocontrol potential. Spiroplasma is a male-killing bacterium for Coleoptera [83]; Serratia prevents malaria in the mosquito and is an insect pathogen [84]; Clostridium restricts systemic CHIKV infection [85] and produces larvicidal toxins [86]; and Lysinibacillus can produce antimalarial siderophores [87]. We also found Enterobacter, which has been used to express transgenic toxins in the midgut mosquito (paratransgenic control) [88].

Conclusion

We identified a source of microorganisms and toxins with insecticidal potential in different mosquito populations, mainly in eggs. We determined that the microbiome is strongly associated with the mosquito developmental stage. Additionally, we detected Wolbachia with the potential to generate and recover cytoplasmic incompatibility. Understanding the microbiome of wild mosquito eggs and larvae could be relevant for developing future biocontrol strategies.

Supporting information

S1 File. Supplementary figures and tables.

https://doi.org/10.1371/journal.pone.0302328.s001

(PDF)

Acknowledgments

We thank Casandra Gonzalez-Acosta (CENAPRECE) for her comments on the experimental design and access to the Centro Regional de Control de Vectores (CERECOVE). We thank the staff of the CERECOVE Panchimalco; Jorge L. Peralta, Alejandro Orozco B., Andrés J Martínez G., Antelmo Viveros P., Lucio L., Rosa T., Rosa M., and Hernández N. for their help during the sampling. We appreciate the assistance of Dr. Mario A. Ocampo (CIBAC-UAMX) in mosquito management.

References

  1. 1. Merritt R. Feeding Behavior, Natural Food, And Nutritional Relationships Of Larval Mosquitos. Annual Review of Entomology. 1992; 37(1), 349–376.
  2. 2. Peach D A H, Gries R, Zhai H, Young N, Gries G. Multimodal floral cues guide mosquitoes to tansy inflorescences. Scientific Reports. 2019; 9(1), 1–10. pmid:30846726
  3. 3. Coon K L, Brown M R, Strand M R. Mosquitoes host communities of bacteria that are essential for development but vary greatly between local habitats. Molecular Ecology. 2016; 25(22), 5806–5826. pmid:27718295
  4. 4. Dickson L B, Jiolle D, Minard G, Moltini-Conclois I, Volant S, Ghozlane A, et al. Carryover effects of larval exposure to different environmental bacteria drive adult trait variation in a mosquito vector. Science Advances. 2017; 3(8), 1–15. pmid:28835919
  5. 5. Wang Y, Gilbreath T M, Kukutla P, Yan G, Xu J. Dynamic Gut Microbiome across Life History of the Malaria Mosquito Anopheles gambiae in Kenya. PLoS ONE. 2011; 6(9), e24767. pmid:21957459
  6. 6. Scolari F, Casiraghi M, Bonizzoni M. Aedes spp. and Their Microbiota: A Review. Frontiers in Microbiology. 2019; 10(September), 1–19. pmid:31551973
  7. 7. Muturi E J, Ramirez J L, Rooney A P, Dunlap C. Association between fertilizer-mediated changes in microbial communities and Aedes albopictus growth and survival. Acta Tropica. 2016; 164, 54–63. pmid:27562215
  8. 8. Muturi E J, Ramirez J L, Rooney A P, Kim C-H. Comparative analysis of gut microbiota of mosquito communities in central Illinois. PLOS Neglected Tropical Diseases. 2017; 11(2), e0005377. pmid:28245239
  9. 9. Champion C J, Xu J. The impact of metagenomic interplay on the mosquito redox homeostasis. Free Radical Biology and Medicine. Elsevier B.V. 2017; pmid:27880869
  10. 10. Muturi E J, Dunlap C, Ramirez J L, Rooney A P, Kim C H. Host blood-meal source has a strong impact on gut microbiota of Aedes aegypti. FEMS Microbiology Ecology. 2018; 95(1), 1–9. pmid:30357406
  11. 11. Dickson L B, Ghozlane A, Volant S, Bouchier C, Ma L, Vega-Rúa A, et al. Diverse laboratory colonies of Aedes aegypti harbor the same adult midgut bacterial microbiome. Parasites & Vectors. 2018; 11(1), 207. pmid:29587819
  12. 12. Hilgenboecker K, Hammerstein P, Schlattmann P, Telschow A, Werren J H. How many species are infected with Wolbachia?—A statistical analysis of current data. FEMS Microbiology Letters. 2008; 281(2), 215–220. pmid:18312577
  13. 13. Kang X, Wang Y, Li S, Sun X, Lu X, Rajaofera M J N, et al. Comparative Analysis of the Gut Microbiota of Adult Mosquitoes From Eight Locations in Hainan, China. Frontiers in Cellular and Infection Microbiology. 2020; 10(December), 1–12. pmid:33384969
  14. 14. Santos N A C, Carvalho V R, Souza-Neto J A, Alonso D P, Ribolla P E M, Medeiros J F, et al. Bacterial Microbiota from Lab-Reared and Field-Captured Anopheles darlingi Midgut and Salivary Gland. Microorganisms. 2023; 11(5). pmid:37317119
  15. 15. Rosso F, Tagliapietra V, Albanese D, Pindo M, Baldacchino F, Arnoldi D, et al. Reduced diversity of gut microbiota in two Aedes mosquitoes species in areas of recent invasion. Scientific Reports. 2018; 8(1), 1–11. pmid:30382151
  16. 16. Zouache K, Martin E, Rahola N, Gangue M F, Minard G, Dubost A, et al. Larval habitat determines the bacterial and fungal microbiota of the mosquito vector Aedes aegypti. FEMS Microbiology Ecology. 2022; 98(1), 1–11. pmid:35147188
  17. 17. Rodpai R, Boonroumkaew P, Sadaow L, Sanpool O, Janwan P, Thanchomnang T, et al. Microbiome Composition and Microbial Community Structure in Mosquito Vectors Aedes aegypti and Aedes albopictus in Northeastern Thailand, a Dengue-Endemic Area. Insects. 2023; 14(2), 184. pmid:36835753
  18. 18. Kittayapong P, Baimai V, O’Neill S L. Field prevalence of Wolbachia in the mosquito vector Aedes albopictus. American Journal of Tropical Medicine and Hygiene. 2002; 66(1), 108–111. pmid:12135259
  19. 19. Gloria-Soria A, Ayala D, Bheecarry A, Calderon-Arguedas O, Chadee D D, Chiappero M, et al. Global genetic diversity of Aedes aegypti. Molecular Ecology. 2016; 25(21), 5377–5395. pmid:27671732
  20. 20. Audsley M D, Ye Y H, McGraw E A. The microbiome composition of Aedes aegypti is not critical for Wolbachia-mediated inhibition of dengue virus. PLOS Neglected Tropical Diseases. 2017; 11(3), e0005426. pmid:28267749
  21. 21. Carvajal T M, Hashimoto K, Harnandika R K, Amalin D M, Watanabe K. Detection of Wolbachia in field-collected Aedes aegypti mosquitoes in metropolitan Manila, Philippines. Parasites & Vectors. 2019; 12(1), 361. pmid:31340862
  22. 22. Akiner M M, Demirci B, Babuadze G, Robert V, Schaffner F. Spread of the Invasive Mosquitoes Aedes aegypti and Aedes albopictus in the Black Sea Region Increases Risk of Chikungunya, Dengue, and Zika Outbreaks in Europe. PLoS Neglected Tropical Diseases. 2016; 10(4), 1–5. pmid:27115737
  23. 23. Kuri-Morales P, Correa-Morales F, González-Acosta C, Sánchez-Tejeda G, Dávalos-Becerril E, Fernanda Juárez-Franco M, et al. First report of Stegomyia aegypti (= Aedes aegypti) in Mexico City, Mexico. Medical and Veterinary Entomology. 2017; 31(2), 240–242. pmid:28106260
  24. 24. Boisvert M, Boisvert J. Effects of bacillus thuringiensis var. israelensis on target and nontarget organisms: A review of laboratory and field experiments. Biocontrol Science and Technology. 2000; 10(5), 517–561.
  25. 25. Jeffries C L, Walker T. Wolbachia Biocontrol Strategies for Arboviral Diseases and the Potential Influence of Resident Wolbachia Strains in Mosquitoes. Current Tropical Medicine Reports. 2016; 3(1), 20–25. pmid:26925368
  26. 26. Tetreau G, Grizard S, Patil C D, Tran F-H, Tran Van V, Stalinski R, et al. Bacterial microbiota of Aedes aegypti mosquito larvae is altered by intoxication with Bacillus thuringiensis israelensis. Parasites & Vectors. 2018; 11(1), 121. pmid:29499735
  27. 27. Pardo-López L, Soberón M, Bravo A. Bacillus thuringiensis insecticidal three-domain Cry toxins: Mode of action, insect resistance and consequences for crop protection. FEMS Microbiology Reviews. 2013; 37(1), 3–22. pmid:22540421
  28. 28. Soh S, Ho S H, Ong J, Seah A, Dickens B S, Tan K W, et al. Strategies to Mitigate Establishment under the Wolbachia Incompatible Insect Technique. Viruses. 2022; 14(6), 1132. pmid:35746601
  29. 29. Yen P-S, Failloux A-B. A Review: Wolbachia-Based Population Replacement for Mosquito Control Shares Common Points with Genetically Modified Control Approaches. Pathogens 2020; 9(5), 404. pmid:32456036
  30. 30. Ross P A, Ritchie S A, Axford J K, Hoffmann A A. Loss of cytoplasmic incompatibility in Wolbachia-infected Aedes aegypti under field conditions. PLOS Neglected Tropical Diseases. 2019; 13(4), e0007357. pmid:31002720
  31. 31. Mañez-Bernal S, Martinez-Campos C. Clave para la identificación de larvas de mosquitos comunes en las áreas urbanas y suburbanas de la República Mexicana (Diptera: Culicidae). Folia Entomol. 1994; Mex., 92(June), 43–73.
  32. 32. Rueda L M. Pictorial keys for the identification of mosquitoes (Diptera: Culicidae) associated with Dengue Virus Transmission. Zootaxa. 2004; 589.
  33. 33. Coleman J, Juhn J, James A A A. Dissection of Midgut and Salivary Glands from Ae. aegypti Mosquitoes. Journal of Visualized Experiments. 2007; (5), 2007. pmid:18979026
  34. 34. Kwon S, Lee B, Yoon S. CASPER: Context-aware scheme for paired-end reads from high-throughput amplicon sequencing. BMC Bioinformatics. 2014; pmid:25252785
  35. 35. Huang Y, Niu B, Gao Y, Fu L, Li W. CD-HIT Suite: a web server for clustering and comparing biological sequences. Bioinformatics. 2010;(Oxford, England), 26(5), 680–682. pmid:20053844
  36. 36. Caporaso J G, Kuczynski J, Stombaugh J, Bittinger K, Bushman F D, Costello E K, et al. R. QIIME allows analysis of high-throughput community sequencing data. Nature Methods. 2010; pmid:20383131
  37. 37. Quast C, Pruesse E, Yilmaz P, Gerken J, Schweer T, Yarza P, et al. The SILVA ribosomal RNA gene database project: Improved data processing and web-based tools. Nucleic Acids Research. 2013; pmid:23193283
  38. 38. Haas B J, Gevers D, Earl A M, Feldgarden M, Ward D V, Giannoukos G, et al. Chimeric 16S rRNA sequence formation and detection in Sanger and 454-pyrosequenced PCR amplicons. Genome Research. 2011; 21(3), 494–504. pmid:21212162
  39. 39. Bankevich A, Nurk S, Antipov D, Gurevich A A, Dvorkin M, Kulikov A S, et al. SPAdes: A new genome assembly algorithm and its applications to single-cell sequencing. Journal of Computational Biology. 2012; pmid:22506599
  40. 40. Zerbino D R, Birney E. Velvet: Algorithms for de novo short read assembly using de Bruijn graphs. Genome Research. 2008; pmid:18349386
  41. 41. Camacho C, Coulouris G, Avagyan V, Ma N, Papadopoulos J, Bealer K, et al. BLAST+: Architecture and applications. BMC Bioinformatics. 2009; 10, 421. pmid:20003500
  42. 42. Buchfink B, Reuter K, Drost H-G. Sensitive protein alignments at tree-of-life scale using DIAMOND. Nature Methods. 2021; 18(4), 366–368. pmid:33828273
  43. 43. Wattam A R, Abraham D, Dalay O, Disz T L, Driscoll T, Gabbard J L, et al. PATRIC, the bacterial bioinformatics database and analysis resource. Nucleic Acids Research. 2014; pmid:24225323
  44. 44. O’Leary N A, Wright M W, Brister J R, Ciufo S, Haddad D, McVeigh R, et al Reference sequence (RefSeq) database at NCBI: current status, taxonomic expansion, and functional annotation. Nucleic Acids Research. 2016; 44(D1), D733–D745. pmid:26553804
  45. 45. Ashburner M, Ball C A, Blake J A, Butler H, Cherry J M, Eppig J T, et al. Creating the Gene Ontology resource: Design and implementation. Genome Research. 2001; pmid:11483584
  46. 46. Wood D E, Salzberg S L. Kraken: Ultrafast metagenomic sequence classification using exact alignments. Genome Biology. 2014; pmid:24580807
  47. 47. Crickmore N, Berry C, Panneerselvam S, Mishra R, Connor T R, Bonning B C. A structure-based nomenclature for Bacillus thuringiensis and other bacteria-derived pesticidal proteins. Journal of Invertebrate Pathology. 2021; pmid:32652083
  48. 48. Langmead B, & Salzberg S L. Fast gapped-read alignment with Bowtie 2. Nature Methods. 2012; pmid:22388286
  49. 49. McMurdie P J, Holmes S. Phyloseq: An R Package for Reproducible Interactive Analysis and Graphics of Microbiome Census Data. PLoS ONE. 2013; 8(4). pmid:23630581
  50. 50. Wickham H. ggplot2: Elegant Graphics for Data Analysis. Journal of the Royal Statistical Society: Series A (Statistics in Society). 2011; Vol. 174.
  51. 51. Cole J R, Wang Q, Fish J A, Chai B, McGarrell D M, Sun Y, et al. Ribosomal Database Project: Data and tools for high throughput rRNA analysis. Nucleic Acids Research. 2014; pmid:24288368
  52. 52. Nawrocki E P. Structural RNA Homology Search and Alignment using Covariance Models. Washington University School of Medicine. 2009;
  53. 53. Price M N, Dehal P S, Arkin A P. FastTree: Computing Large Minimum Evolution Trees with Profiles instead of a Distance Matrix. Molecular Biology and Evolution. 2009; 26(7), 1641–1650. pmid:19377059
  54. 54. Letunic I, Bork P. Interactive tree of life (iTOL) v5: An online tool for phylogenetic tree display and annotation. Nucleic Acids Research. 2021; 49(W1), W293–W296. pmid:33885785
  55. 55. Gao H, Cui C, Wang L, Jacobs-Lorena M, Wang S. Mosquito Microbiota and Implications for Disease Control. Trends in Parasitology. 2020; 36(2), 98–111. pmid:31866183
  56. 56. Coon K L, Vogel K J, Brown M R, Strand M R. Mosquitoes rely on their gut microbiota for development. Molecular Ecology. 2014; 23(11), 2727–2739. pmid:24766707
  57. 57. Valiente Moro C, Tran F H, Raharimalala F N, Ravelonandro P, Mavingui P. Diversity of culturable bacteria including Pantoea in wild mosquito Aedes albopictus. BMC microbiology. 2013; 13, 70. pmid:23537168
  58. 58. Yadav K K, Bora A, Datta S, Chandel K, Gogoi H K, Prasad G B, Veer V. Molecular characterization of midgut microbiota of Aedes albopictus and Aedes aegypti from Arunachal Pradesh, India. Parasites & vectors. 2015; 8, 641. pmid:26684012
  59. 59. Bennett K L, Gómez-Martínez C, Chin Y, Saltonstall K, McMillan W O, Rovira J R, Loaiza J R. Dynamics and diversity of bacteria associated with the disease vectors Aedes aegypti and Aedes albopictus. Scientific Reports. 2019; 9(1), 1–12. pmid:31434963
  60. 60. Rodríguez-Ruano S M, Juhaňáková E, Vávra J, Nováková E Methodological Insight Into Mosquito Microbiome Studies. Frontiers in Cellular and Infection Microbiology. 2020; 10(March), 1–10. pmid:32257962
  61. 61. MacLeod H J, Dimopoulos G, Short S M. Larval Diet Abundance Influences Size and Composition of the Midgut Microbiota of Aedes aegypti Mosquitoes. Frontiers in Microbiology. 2021; 12(June), 1–14. pmid:34220739
  62. 62. Hegde S, Khanipov K, Albayrak L, Golovko G, Pimenova M, Saldaña M A, et al. Microbiome Interaction Networks and Community Structure From Laboratory-Reared and Field-Collected Aedes aegypti, Aedes albopictus, and Culex quinquefasciatus Mosquito Vectors. Frontiers in Microbiology. 2018; 9(SEP), 1–16. pmid:30250462
  63. 63. Lee J M, Yek S H, Wilson R F, Rahman S. Characterization of the Aedes albopictus (Diptera: Culicidae) holobiome: Bacterial composition across land use type and mosquito sex in Malaysia. Acta Tropica. 2020; 212, 105683. pmid:32888935
  64. 64. Walterson A M, Stavrinides J. Pantoea: insights into a highly versatile and diverse genus within the Enterobacteriaceae. FEMS Microbiology Reviews. 2015; 39(6), 968–984. pmid:26109597
  65. 65. Sarma D K, Kumar M, Dhurve J, Pal N, Sharma P, James M M, et al Influence of Host Blood Meal Source on Gut Microbiota of Wild Caught Aedes aegypti, a Dominant Arboviral Disease Vector. Microorganisms. 2022; 10(2), 332. pmid:35208787
  66. 66. Wang X, Liu T, Wu Y, Zhong D, Zhou G, Su X, et al. Bacterial microbiota assemblage in Aedes albopictus mosquitoes and its impacts on larval development. Molecular Ecology. 2018; 27(14), 2972–2985. pmid:29845688
  67. 67. Osorio J A, Crous C J, Wingfield M J, De Beer Z W, Roux J. An assessment of mangrove diseases and pests in South Africa. Forestry. 2017; 90(3), 343–358.
  68. 68. Fredensborg B L, Kálvalíð I F í, Johannesen T B, Stensvold C R, Nielsen H V, Kapel C. M O. Parasites modulate the gut-microbiome in insects: A proof-of-concept study. PLoS ONE. 2020; 15(1), 1–18. pmid:31935259
  69. 69. Scholte E-J. An Entomopathogenic Fungus for Control of Adult African Malaria Mosquitoes. Science. 2005; 308(5728), 1641–1642. pmid:15947190
  70. 70. Ginsberg H S, Bargar TA, Hladik M L, Lubelczyk C. Management of Arthropod Pathogen Vectors in North America: Minimizing Adverse Effects on Pollinators. Journal of Medical Entomology. 2017; 54(6), 1463–1475. pmid:28968680
  71. 71. Garza-Hernández J A, Rodríguez-Pérez M A, Salazar M I, Russell T L, Adeleke M A, de Luna-Santillana E de J, et al. Vectorial Capacity of Aedes aegypti for Dengue Virus Type 2 Is Reduced with Co-infection of Metarhizium anisopliae. PLoS Neglected Tropical Diseases. 2013; 7(3), e2013. pmid:23505581
  72. 72. Fang W, Vega-Rodríguez J, Ghosh A K, Jacobs-Lorena M, Kang A, St Leger R J. Development of transgenic fungi that kill human malaria parasites in mosquitoes. Science. 2011; 331(6020), 1074–1077. pmid:21350178
  73. 73. Allman M J, Fraser J E, Ritchie S A, Joubert D A, Simmons C P, Flores H A. Wolbachia’s deleterious impact on aedes aegypti egg development: The potential role of nutritional parasitism. Insects. 2020; 11(11), 1–14. pmid:33120915
  74. 74. Audsley M D, Seleznev A, Joubert D A, Woolfit M, O’Neill S L, McGraw E A. Wolbachia infection alters the relative abundance of resident bacteria in adult Aedes aegypti mosquitoes, but not larvae. Molecular Ecology. 2018; 27(1), 297–309. pmid:29165845
  75. 75. Coon K L, Brown M R, Strand M R. Mosquitoes host communities of bacteria that are essential for development but vary greatly between local habitats. Molecular Ecology. 2016; 25(22), 5806–5826. pmid:27718295
  76. 76. Inácio da Silva L M, Dezordi F Z, Paiva M H S, Wallau G L. Systematic Review of Wolbachia Symbiont Detection in Mosquitoes: An Entangled Topic about Methodological Power and True Symbiosis. Pathogens. 2021; 10(1), 39. pmid:33419044
  77. 77. Chiarello M, McCauley M, Villéger S, Jackson C R. Ranking the biases: The choice of OTUs vs. ASVs in 16S rRNA amplicon data analysis has stronger effects on diversity measures than rarefaction and OTU identity threshold. PloS one. 2022; 17(2), e0264443. pmid:35202411
  78. 78. Werren J H, Baldo L, Clark M E. Wolbachia: Master manipulators of invertebrate biology. Nature Reviews Microbiology. 2008; 6(10), 741–751. pmid:18794912
  79. 79. Xi Z, Khoo C C H, Dobson S L. Ecology: Wolbachia establishment and invasion in an Aedes aegypti laboratory population. Science. 2005; 310(5746), 326–328. pmid:16224027
  80. 80. Altinli M, Gunay F, Alten B, Weill M, Sicard M. Wolbachia diversity and cytoplasmic incompatibility patterns in Culex pipiens populations in Turkey. Parasites & Vectors. 2018; 11(1), 198. pmid:29558974
  81. 81. Liang X, Liu J, Bian G, Xi Z. Wolbachia Inter-Strain Competition and Inhibition of Expression of Cytoplasmic Incompatibility in Mosquito. Frontiers in Microbiology. 2020; 11. pmid:32765466
  82. 82. Utarini A, Indriani C, Ahmad R A, Tantowijoyo W, Arguni E, Ansari M R, et al. Efficacy of Wolbachia-Infected Mosquito Deployments for the Control of Dengue. New England Journal of Medicine. 2021; 384(23), 2177–2186. pmid:34107180
  83. 83. Dudek K, Huminska K, Wojciechowicz J, Tryjanowski P. Metagenomic survey of bacteria associated with the invasive ladybird Harmonia axyridis (Coleoptera: Coccinellidae). European Journal of Entomology. 2017; 114, 312–316.
  84. 84. McQuade R, Stock S P. Secretion systems and secreted proteins in gram-negative entomopathogenic bacteria: Their roles in insect virulence and beyond. Insects. 2018; 9(2). pmid:29921761
  85. 85. Winkler E S, Shrihari S, Hykes B L, Handley S A, Andhey P S, Huang Y J S, et al. The Intestinal Microbiome Restricts Alphavirus Infection and Dissemination through a Bile Acid-Type I IFN Signaling Axis. Cell. 2020; 1–18. pmid:32668198
  86. 86. Minard G, Mavingui P, Moro C V. Diversity and function of bacterial microbiota in the mosquito holobiont. Parasites & Vectors 2013; 6(1), 146. pmid:23688194
  87. 87. Ganley J G, Pandey A, Sylvester K, Lu K-Y, Toro-Moreno M, Rütschlin S, Bradford J M, et al. A Systematic Analysis of Mosquito-Microbiome Biosynthetic Gene Clusters Reveals Antimalarial Siderophores that Reduce Mosquito Reproduction Capacity. Cell Chemical Biology 2020; 27(7), 817–826.e5. pmid:32619453
  88. 88. Riehle M A, Moreira C K, Lampe D, Lauzon C, & Jacobs-Lorena, M. Using bacteria to express and display anti-Plasmodium molecules in the mosquito midgut. International Journal for Parasitology 2007; 37(6), 595–603. pmid:17224154