- Open Access
Malaria vector populations across ecological zones in Guinea Conakry and Mali, West Africa
© Coulibaly et al. 2016
- Received: 18 December 2015
- Accepted: 30 March 2016
- Published: 8 April 2016
Malaria remains a pervasive public health problem in sub-Saharan West Africa. Here mosquito vector populations were explored across four sites in Mali and the Republic of Guinea (Guinea Conakry). The study samples the major ecological zones of malaria-endemic regions in West Africa within a relatively small distance.
Mosquito vectors were sampled from larval pools, adult indoor resting sites, and indoor and outdoor human-host seeking adults. Mosquitoes were collected at sites spanning 350 km that represented arid savannah, humid savannah, semi-forest and deep forest ecological zones, in areas where little was previously known about malaria vector populations. 1425 mosquito samples were analysed by molecular assays to determine species, genetic attributes, blood meal sources and Plasmodium infection status.
Anopheles gambiae and Anopheles coluzzii were the major anophelines represented in all collections across the ecological zones, with A. coluzzii predominant in the arid savannah and A. gambiae in the more humid sites. The use of multiple collection methodologies across the sampling sites allows assessment of potential collection bias of the different methods. The L1014F kdr insecticide resistance mutation (kdr-w) is found at high frequency across all study sites. This mutation appears to have swept almost to fixation, from low frequencies 6 years earlier, despite the absence of widespread insecticide use for vector control. Rates of human feeding are very high across ecological zones, with only small fractions of animal derived blood meals in the arid and humid savannah. About 30 % of freshly blood-fed mosquitoes were positive for Plasmodium falciparum presence, while the rate of mosquitoes with established infections was an order of magnitude lower.
The study represents detailed vector characterization from an understudied area in West Africa with endemic malaria transmission. The deep forest study site includes the epicenter of the 2014 Ebola virus epidemic. With new malaria control interventions planned in Guinea, these data provide a baseline measure and an opportunity to assess the outcome of future interventions.
- Malaria Transmission
- Blood Meal
- Ecological Zone
- Established Infection
Malaria remains a prominent public health and financial burden across much of sub-Saharan African. To date, control efforts have been centered on vector control, largely through use of insecticide-treated bed nets (ITNs) or indoor residual insecticide spraying (IRS) . Recent work has focused on potential genetic modification of vectors, but tools for practical implementation are not yet available. While insecticides are effective in the short term, selection of genetic resistance in the vector population by various mechanisms can decrease efficacy of control, or even allow rebound of transmission [2, 3].
Malaria intervention histories vary widely across Africa, and the Republic of Guinea (Guinea Conakry) has been relatively devoid of large-scale national malaria control efforts. The country has the eighth highest malaria mortality among 43 African nations, and the lowest proportion of children under 5 years old sleeping under an ITN, 47 %, as compared to 87 % in neighbouring Mali . Guinea was the presumed site of emergence of Ebola virus from an animal reservoir that led to the 2014 West African epidemic [5, 6]. Malaria control and surveillance were neglected during the Ebola epidemic, and resurgence of malaria transmission and other public health problems are expected as a result [7–9].
There are also disparities in the level of knowledge of the malaria vectorial system between countries. While vector populations have been extensively studied in some areas of West Africa, for example Mali and Burkina Faso, information from Guinea Conakry is surprisingly sparse. Only one previous published paper characterizes mosquito vector populations in Guinea Conakry . Nevertheless, the region offers unique opportunities, because the high ecological diversity in close proximity allows studies that capture all of the major ecological zones of malaria transmission across West Africa, while minimizing geographic variables. Moreover, because of the relative absence of prior national malaria control interventions, such as mass ITN distribution in Guinea Conakry, collected data can provide crucial baseline information on vector populations prior to intervention, a piece of data often missing in evaluation and planning of mosquito control strategies. In the current study, sampling was carried out across ecological zones from arid savannah in the north to deep forest in the south, and employed multiple collection methods at all sites. The analysis of the samples characterizes the vector population in a little-studied region of West Africa.
All reported collections occurred in October and November in 2012. In the Yanfolila district of Mali, which includes Takan and Toumani Oulena study sites, the overall mean temperature range was 21–30 °C and the mean relative humidity range is 37–73 %, although Takan is more arid and Toumani Oulena more humid. The average temperature at the Koundara site was 21 °C with 92 % relative humidity while in Koraboh it was 24 °C and 86 % relative humidity. Epidemiological data for malaria are sparse, although self-presented cases of fever at district-level clinics from 2006 (uncorrected for district population size) can provide an estimate . The savannah sites displayed a highly seasonal pattern with a peak of >2000 fever cases/month from June–September and very low otherwise, similar to the well-studied Sudanian savannah zones of neighbouring Mali or Burkina Faso [12–14]. The district of Kissidougou, including the semi-forest site of Koraboh, displayed >2500 cases/month in every month except April. The district of Macenta, including the deep forest site of Koundara, displayed >1400 cases/month in every month of the year, with a peak of 1700 in September and October.
At each site, mosquitoes were collected using three different methods: (1) human-landing capture (HLC), (2) indoor manual aspirator or pyrethroid spray catch, and (3) larval capture, where the first and second instar larvae were raised to adult in a field insectary under standard insectary conditions prior to DNA isolation from the adults; and the third and fourth instar larvae were preserved directly for DNA isolation, without rearing in the insectary. The two distinct methods of larval collection were used to control for possible genetic bias inherent in lab rearing of captured larvae. Across sites, all types of larval sites were sampled, including both temporary and permanent sites. Human-landing captures were performed both inside dwellings and outside (>10 m from dwelling) at night between 18:00 and 06:30. The indoor aspirator or spray catches were done in the morning between 06:00 and 12:00. Adult specimens or third and fourth instar larvae were preserved immediately in 80 % ethanol until later DNA extraction. First and second instar larvae were raised to adults in nearby field insectaries and upon emergence were preserved in 80 % ethanol. DNA was extracted from mosquitoes using DNAzol by the provided protocol (Invitrogen, CA, USA).
DNA isolation and species identification
Genomic DNA was isolated from individual mosquitoes using DNAzol (Invitrogen, CA, USA). DNAs were resuspended in distilled water and stored at −20 °C. All samples were typed by a molecular diagnostic assay to determine species status within the A. gambiae species complex . If this assay failed to yield a diagnostic band, the ribosomal gene ITS2 region was PCR amplified , Sanger-sequenced, and the resulting sequence was used to search the NCBI nr database using blast. Mosquito species calls based on ITS2 sequence used a threshold of >98 % nucleotide identity. In total, 390 samples were analysed from Koraboh, 329 from Koundara, 345 from Takan and 361 from Toumani Oulena. All samples were genotyped for mosquito species. For the remainder of attributes, all human-landing capture samples and random subsets of spray and larval caught samples were analysed, with sample sizes indicated with each figure. All genomic DNAs were isolated from whole mosquitoes or larvae.
Genotyping the 2La chromosome inversion
Molecular karyotyping of the paracentric 2La inversion was done using published methods . When product bands other than those reported were seen, they were sequenced and compared with other non-standard product sizes previously reported [18, 19]. These non-standard sizes were assigned as wild-type (2La+) or inverted (2La) based on sequence and published information. The non-standard sizes are generally the result of insertion of mobile elements such as MITEs into the inversion breakpoint .
Genotyping of the kdr-w mutation
The mutation of the para gene, L1014F, called West African kdr or kdr-w, which is associated with pyrethroid insecticide resistance, was genotyped by a published PCR diagnostic assay , and in a small number of samples (n = 15–18 samples per population) a short amplicon generated with the Agd1 and Agd2 primers was amplified and sequenced to genotype the East African kdr mutation, L1014S, also called kdr-e. The geographic names of these mutations are a misnomer, as the East African kdr mutation has been detected in samples from West Africa . Across all sampling sites, kdr genotypes for 70 samples were confirmed by Sanger sequencing.
Molecular detection of blood meal source
To determine the source of blood meal, published assays were modified based on amplification of the mitochondrial cytB gene. Blood meal source was typed in all those mosquitoes with a visibly detectable blood meal. Visible blood meal rates were >95 % in indoor spray-caught samples and also included some human-landing capture samples, presumably seeking a second blood meal in the same gonotrophic cycle. All samples were initially typed with a published method , but due to amplification of mosquito DNA in negative control samples, a new reverse primer was created and optimized to minimize mosquito amplification. Using cytb forward 5′-GAG GMC AAA TAT CAT TCT GAG G-3′ from  and newly designed cytb Rev 5′-CGR AAT ATT ATG CTT YGT TG-3′ samples were assayed in a 25 µl PCR reaction containing 1.5 µl undiluted genomic DNA, 1 × PCR buffer, 3 mM MgCl2, 0.4 µM primers. Cycling conditions were an initial denaturation of 95 °C for 1 min followed by 35 cycles of 95 °C for 30 s, 56 °C for 50 s and 72 °C for 1 min followed by a final extension of 72 °C for 5 min.
The primers amplify a 549 bp fragment that was subsequently digested with restriction enzymes, EarI and ApaI. EarI is diagnostic for blood meals derived from humans and goat/sheep. If the blood meal is human in origin, the EarI digest cuts once resulting in bands of 248 and 301 base pairs. If the blood meal is goat or sheep in origin, the band sizes following EarI digestion will be 194 and 355 base pairs. Distinguishing goat from sheep requires sequencing of the original band. Digestion of the cytB amplicon with ApaI yields products 257 and 292 bp in length if the blood meal is bovine in origin. All products that are uncut after independent digestions with EarI and ApaI were Sanger sequenced and blasted against the nr database at Genbank. All blood meal assays included positive control animal genomic DNAs purchased from a commercial source (Zyagen, CA, USA). A reconstruction experiment was done by serial dilution of human DNA into mosquito DNA, which determined that within a typical mosquito DNA sample, the limit of detection for human DNA was 0.05–0.005 pg.
Molecular detection of Plasmodium falciparum in blood-fed and unfed mosquitoes
The presence of Plasmodium falciparum was determined using a PCR assay that amplifies a portion of the parasite cytB gene. The assay is a modification of reported methods [22, 23], producing a 902 bp PCR fragment. Initially the assays were run independently and were later combined and modified to improve specificity and sensitivity. The PCR based detection of P. falciparum used forward primer PFcytblongF 5′-ATACATGCACGCAA CAGGTGCTTCTC-3′  and reverse primer MitR2 5′-TGTTTGCTTGGGAGCTGTAA-3′ . The PCR reaction was 1x Accuprime Supermix II (Invitrogen, CA, USA), 1 pmol of each primer and 2 µl of undiluted mosquito genomic DNA (or 1 µl of control P. falciparum DNA serial dilution). PCR conditions were 35 cycles at 94 °C for 40 s, 61 °C for 40 s and 72 °C for 90 s. The limit of detection was determined by serial dilution of P. falciparum DNA, ranging from 6.775–0.0006775 pg, and a standard curve was run with every PCR. Serial dilutions of P. falciparum stock DNA were made fresh for each independent PCR experiment, and control reactions were run alongside all experimental samples. The limit of detection for P. falciparum was 0.06775 pg/µl (or ~2 P. falciparum genome equivalents). All samples that tested positive were independently retested to confirm results.
The P. falciparum detection assay was performed on all adult mosquito samples positive for a human blood meal (i.e., visually positive for a blood meal and positive for human blood) to estimate the P. falciparum exposure rate (the rate at which mosquitoes take a blood meal that contains P. falciparum parasites). The P. falciparum assay was also performed on all adult samples not positive for a visible blood meal, to estimate the rate of established infections in the mosquito. Exposure rate was estimated from all blood-fed mosquitoes, including indoor-resting spray catch as well as HLC.
For human-landing capture of mosquitoes, the study protocol was reviewed and approved by the institutional and national health ethical review boards (Comité National d’Ethique pour la Recherche en Santé) of The Republic of Guinea (reference number N′003/CNFRSR/MAF/13) and (Comité d’Ethique Institutionelle/FMPOS) of the Republic of Mali (reference number Traore-37). The study procedures, benefits and risks were explained to collectors and their informed consent was obtained. All collectors were followed and symptomatic subjects were treated with the combination of artemether–lumefantrine (Coartem®) according to relevant regulations of the Republic of Guinea and Republic of Mali Ministries of Health.
A 350 km ecological sampling zone was established from the Mali border in the north of Guinea Conakry, to the south of the country near the border with Liberia (Fig. 1). Study sites were located in the following ecological zones: arid savannah (village of Takan), humid savannah (Toumani Oulena), semi-forest (Koraboh), and deep forest (Koundara). The range of ecologies sampled across this relatively short distance is representative of the major zones of malaria transmission present throughout West Africa.
Adult mosquitoes were sampled by techniques that collect behaviourally discrete groups of mosquitoes: human-landing capture (HLC) inside and outside of houses (indoor and outdoor human host-seeking), and pyrethroid spray capture inside houses (indoor-resting). In addition, larvae were sampled from breeding pools around the villages, which should represent an unbiased collection of Anopheles species in proportion to their relative abundance in the overall population. This study surveys mosquito vectors in Guinea Conakry and Mali for species composition, blood meal source, and multiple molecular attributes with potential importance to vector control and malaria transmission. The data permits comparison of the different features according to ecological variables, as well as comparison with the only other reported survey of Guinea Conakry vectors, using mosquitoes collected 6 years prior in 2006 .
Finally, a small number of other species were found, including the vector Anopheles funestus, the largely zoophilic Anopheles rufipes, and A. gambiae/A. coluzzii hybrids. Interestingly, no Anopheles arabiensis were sampled among the 1425 mosquitoes across all sampling methodologies and ecologies. This contrasts with species present in the Sudanian savannah zone of Burkina Faso, also during the rainy season as in the current study, where A. arabiensis comprised nearly 50 % of the larval pool species composition .
In the previous reported survey in Guinea Conakry based on collections made in 2006 , two sites displayed predominantly A. gambiae, with A. coluzzii present at >5 %. One of these sites, Siguiri, is ecologically comparable to the current semi-forest site of Koraboh with similar species composition, while the other site, Boffa, is in the west of Guinea Conakry, a region not included in the current study. However, at Siguiri 1.3 % (2/156) A. arabiensis were reported previously, while none were observed in the current study using twice the sample size. The third site of the 2006 sampling was Mt Nimba, in the south near the current deep forest site of Koundara. Mt Nimba displayed 38 % A. gambiae and 61 % A. coluzzii, in distinction to the predominance of A. gambiae at Koundara. However, the Mt Nimba site appears to be a more arid disturbed habitat as compared to Koundara (Fig. 1 compared to ), thus not ecologically equivalent, and probably more suitable for A. coluzzii. In 2006, A. funestus were also present (Siguiri n = 15, Mt Nimba n = 35) while in the current study only one was collected, at the humid savannah site. The 2006 samples were collected in July–August and the current samples in October–November, so there could be a seasonal difference. Overall, the species distributions appear largely similar between the 2006 and 2012 collections.
kdr mutation frequency
It is interesting that the previous reported survey in Guinea Conakry based on collections made in 2006 displayed considerably lower kdr frequencies . In 2006, the L1014F kdr-w allele was present in A. gambiae at a frequency of 0.14 from Mt. Nimba, near the current deep forest site that displayed kdr-w frequency of 0.997 in A. gambiae 6 years later in 2012 (of 384 mosquitoes, only one was heterozygous). The 2006 collection detected the kdr-w allele present at a frequency of 0.24 in A. gambiae at a site in the west of the country that is not comparable to any of current sites. The 2006 overall kdr-w allele frequency in A. coluzzii was 0.03, while by 2012 the overall frequency in A. coluzzii was 0.77 and A. gambiae was 0.99. In 2005, the proportion of households with at least one ITN was <1 % while by 2012 the figure had increased to 47 %, even in the absence of previous national mass distribution of ITNs, which was planned to begin in 2013 or 2014 . The observed kdr increase could thus be a consequence of exposure to ITNs in the intervening 6 years , or may be driven by the agricultural use of pesticides, or by other ecological changes. In any case, from 2006 to 2012, although vector species composition remained essentially stable, the frequency of kdr-w increased sharply. By 2012, before the first national mass ITN distribution in Guinea Conakry, kdr-w was already essentially fixed in the vector population.
The presence of P. falciparum was measured among the mosquitoes carrying a human blood meal, and was termed the exposure rate, that is, the rate at which mosquitoes taking a human blood meal were exposed to parasites. Exposure rate includes the parasite challenge rate by infectious gametocytes, but it also includes other unknown factors: the developmental stage of parasites, including maturity of gametocytes if any, as well as the rate of signals originating in previously established infections and not the blood meal. Plasmodium falciparum presence was also measured in mosquitoes not carrying a visible blood meal, and was termed the rate of established P. falciparum infections since the signal could not have originated directly from blood. Partitioning exposure and established infection was done to avoid bias and to obtain the most robust measures of these two epidemiologically important values. Exposure rate was estimated from all blood-fed mosquitoes, including indoor-resting spray catch as well as HLC.
Mosquito sampling and analysis throughout four ecological zones spanning the range of malaria transmission ecologies present across West Africa provides useful insights for the design, implementation and evaluation of vector control strategies. Additionally, choice of vector sampling method can influence the conclusions that are reached. Baseline data presented here, collected prior to systematic vector control intervention, can be valuable to design, evaluate and monitor vector control strategies. Given that 25–34 % of human host-seeking (HLC) mosquitoes were collected outdoors, indoor-directed control measures (e.g., ITNs and IRS) will miss a portion of the vector population and thus may have limited effectiveness to control vectors. Despite the low level of previous mass distribution of ITNs in Guinea Conakry, the vector population is nearly fixed for the kdr-w resistance mutation. This could diminish both immediate and long-term impact of ITNs for malaria control in the country.
BC, AHB, MBC, SFT, KDV and MMR conceived and designed the study; BC, RK, MBC, ON collected samples, BE and MMR did the experiments, collected and analyzed the data, KDV and MMR wrote the paper. All authors read and approved the final manuscript.
We acknowledge the assistance of Emmanuel Bischoff with the map generation for Fig. 1. This work received financial support to KDV from the European Commission, FP7 Infrastructures #228421 Infravec; European Research Council, Support for frontier research, Advanced Grant #323173; National Institutes of Health, NIAID R01 #AI073685; and French Laboratoire d’Excellence “Integrative Biology of Emerging Infectious Diseases” #ANR-10-LABX-62-IBEID. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
The authors declare that they have no competing interests.
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