Skip to main content


We’d like to understand how you use our websites in order to improve them. Register your interest.

Presence of susceptible wild strains of Anopheles gambiae in a large industrial palm farm located in Aboisso, South-Eastern of Côte d’Ivoire



The effectiveness of malaria control programmes through implementation of vector control activities is challenged by the emergence of insecticide resistance. In the South-Eastern region of Côte d’Ivoire, where palm oil plantations remain the predominant agricultural crop, the susceptibility of wild Anopheles gambiae sensu lato species is still unknown and thus requires a particular attention. The current study was carried out to address the gap by in-depth characterization of susceptibility level of An. gambiae mosquitoes from Ehania-V1 to WHO-recommended doses of six insecticides belonging to available classes and also to screen a subset for target site mutations and possible inhibition of P450 enzymes.


Overall results showed variable resistance profile across WHO-recommended insecticides tested. Mortalities ranged from 8.3% (the lowest mortality was recorded with DDT) to 98% (the highest mortality was recorded with fenitrothion). Importantly, mortality to deltamethrin, an important pyrethroid used in public health for impregnation of mosquito nets was close to 98%, precluding a possible susceptibility to this insecticide, albeit further investigations are required. Pre-exposure of An. gambiae s.l. to PBO did not show any significant variation across insecticides (p = 0.002), although a partial increase was detected for alphacypermethrin and bendiocarb, suggesting a low of activity of cytochrome P450 enzymes (p = 0.277). High frequency of kdr L1014F was recorded in both Anopheles coluzzii (91%) and in An. gambiae (96%), associated with ace-1 R G119S mutation at low frequency (<20%).


The high mortality rate to deltamethrin, organophosphate and the non-detection of P450 activity in resistance observed in Ehania-V1 appears as a positive outcome for further control strategies as metabolic-based P450 resistance remains major challenge to manage. These results should help the National Malaria Control Programme when designing strategies for vector control in palm oil areas of Côte d’Ivoire.


Malaria is a major public health problem in Africa with a burden estimated to over 190 million cases and 395,000 deaths, mainly among children under five [1]. The dominant Anopheline mosquitoes responsible for the transmission of malaria parasites in Africa are mainly Anopheles funestus and the three complex sibling species Anopheles gambiae (formerly An. gambiae s.s. S form), Anopheles coluzzii (formerly An. gambiae s.s. M form), Anopheles arabiensis. Vector control based on the use of chemical insecticides through long-lasting insecticide-treated nets (LLIN) and indoor residual spraying (IRS) is one of the most effective measures to prevent malaria transmission [1]. Actually, pyrethroids are the only insecticide class approved for LLINs and also used in IRS programme worldwide [2]. Several studies have demonstrated LLIN and IRS effectiveness in Anopheles mosquito control [3, 4], therefore, a reduction of malaria cases and childhood mortality [5]. Strong evidence of impact of current vector control interventions in malaria reduction has recently been reported [6], in which both LLINs and IRS accounted for 78% reduction of malaria cases between 2000 and 2015, and artemisinin-based combination therapy (ACT) accounted for 22%. However, such effort could be compromised if new compounds development is not rapidly undertaken to support the current existing active ingredients. It is also important to note that pyrethroid resistance nearly ubiquitous in various regions was first detected in Cote d’Ivoire, especially in Bouaké town in 1993 [7]. Soon after, several cases of resistance have also been detected in many African countries including Benin [8], Mali [9] and Cameroon [10]. Unfortunately, resistance is also being rapidly reported to other classes of insecticides [11,12,13,14,15].

Up-to-date, key identified resistance mechanisms included (i) mediated amino-acid changes at the target sites of insecticides, leucine to serine (L1014S) or leucine to phenylalanine (L1014F) in the voltage sodium channel gate (kdr mutations for pyrethroids and DDT) and glycine to serine at codon 119 (G119S Ace 1 R mutation for organophosphates and carbamates) and (ii) insecticides detoxification by metabolic enzymes i.e. non-specific esterases, (NSE), mixed-function oxidase (MFO) and glutathione S-transferases (GST). In Côte d’Ivoire, resistance mechanisms have been investigated at both phenotypic [1517] and genetic level [18].

The sources of selection pressure for resistance remain always a debate. However, the use of insecticides in agriculture has been incriminated [19]. Extensive use of insecticides against agricultural pests, mainly on cotton and irrigated rice farms, has led to the development of resistance in Anopheles which negatively impacted malaria control interventions [19].

In the context of a lack of new insecticide classes for malaria control for 30 years and none for the next 6–9 years, vector control relies on improved management of existing insecticides. A key to this is to carry out an in-depth characterization of existing resistance mechanisms. Given the place and role of palm oil production in the economy of Côte d’Ivoire and efforts made to control pests by applying insecticides, it appears crucial to undertake a study to deeply monitor insecticide resistance level in oil palm plantations in Cote d’Ivoire.

This is the first study implemented in an industrial palm oil farm, in order to assess the susceptibility level of the main malaria vectors An. gambiae s.l. to World Health Organization (WHO)-recommended insecticide classes, and beyond, the corresponding target-sites mutation frequency.


Study site

Ehania-V1 is located in the South-eastern Côte d’Ivoire, 140 km from Abidjan (Geographical coordinates: longitude: 5°14′N, latitude: 2°46′W), and 60 km from Ghana (Fig. 1). Bordered by Noé and Aboisso, Ehania-V1 is the biggest industrial palm oil farm (30,000 hectares) belonging to the company PALMCI created in 1969 and privatized in 1997. The yield constitutes 32% of the annual palm oil yield of the country. The company plays a role of guidance and supervision of 8097 out-growers.

Fig. 1

Mapping of Côte d’Ivoire showing Ehania-V1, the study site

Employees and plantations workers are part of the 12,300 inhabitants of PALMCI industrial unit. Schools and dispensaries are free of charge for workers and their families as well as local communities. The presence of palm plantations in this area was a good opportunity to improve transport facilities for the flow of products. Climate is equatorial with four seasons: high dry season (December to February); high rainy season (Mars to July); Small dry season (August to September) and small rainy season (October to November). In the last 10 years, average annual rainfall was around 1500 mm. The vegetation is composed by evergreen forest. The main ethnic group was Akan. Various types of pesticides (described in Additional file 1) were used for crop protection against insects, rodents and fungus.

Insecticide susceptibility

Larvae of Anopheles gambiae s.l. were collected from natural breeding habitats in and around Ehania-V1 between June and July 2013. Larvae were reared to adults for bioassays in Institut Pierre Richet insectarium (IPR) in Bouaké, Central Côte d’Ivoire. All larvae were provided a diet of Tetra Mikromin fish food until adult stage.

WHO-tube bioassays were carried out using impregnated papers of diagnostic concentrations of six insecticides belonging to the four approved classes: one organochlorine (4% DDT), three pyrethroids (0.05% deltamethrin, 0.05% alpha-cypermethrin and 0.75% permethrin), one organophosphate (1% fenitrothion) and one carbamate (0.1% bendiocarb).

Four batches of 25–27 unfed females of wild An. gambiae s.l. and the reference laboratory Kisumu strain, which is free of any detectable resistance mechanisms and raised in the same conditions, 2–3 day-old were exposed to insecticide-treated papers for 60 min at 25 ± 2 °C and 80% relative humidity (RH). Papers without insecticide were used as control. The number of mosquitoes knocked down was recorded at 10 min intervals during the exposure period with pyrethroids and DDT, as the knock down rate shown to be a sensitive indicator for early detection of resistance. After the exposure time, mosquitoes were supplied with 10% sugar solution and mortality was scored 24 h later.

Synergist PBO assays

Complementary synergist assays were performed using piperonyl butoxide (PBO), an inhibitor of monooxygenases, in order to assess the involvement of detoxifying enzymes in the production of resistant phenotypes. Mosquitoes were pre-exposed to 4% PBO-impregnated filter papers for 1 h and then exposed to insecticide-impregnated papers for additional 1 h according to WHO procedures. Final mortalities recorded 24 h later following exposure were compared between the synergized and non-synergized samples. The susceptible Kisumu strain was not synergized. Exposed mosquitoes to insecticides were individually kept on silica gel and stored in refrigerator (−20 °C) for molecular analysis.

DNA extraction, molecular forms and target site resistance monitoring

Genomic DNA samples from 50 mosquitoes randomly selected among the dead and surviving mosquitoes from WHO tube bioassays were analyzed by polymerase chain reaction (PCR). Genomic DNA was extracted on individual mosquitoes according to Collins et al. [20]. Anopheles gambiae s.l. mosquitoes were identified to species according to Scott et al. [21] and Santolamazza et al. [22]. The presence of L1014F and L1014S kdr alleles was assessed using allele-specific PCR [23]. The PCR–RFLP diagnostic test was used to detect the presence of the G119S mutation (ace-1 R gene) according to Weill et al. [24].

Biochemical analysis

Biochemical assays were performed to quantify and assess the amounts of MFO (cytochrome P450) and GSTs, and the activity levels of NSE for both α- and β-naphthyl acetate as described in WHO book [25]. Batches of 30–35 unfed female mosquitoes (2–3 days old) from the Ehania-V1 strain were used per microtitre plate. Each plate also contained 5–10 specimens (2–3 day-old female mosquitoes from the susceptible Kisumu strain for further comparison. These specimens have not been exposed to any insecticides but frozen at −80 °C prior to biochemical analysis.

Statistical analysis

Mortality rate of each insecticide was calculated as the proportion of dead mosquito 24 h post-exposure at 95% confidence intervals. No correction was performed using Abbott’s formula [26], as the mortality rates in all controls tests were always less than 5%. WHO [2] criteria were used to evaluate susceptible/resistant phenotype of mosquito strains. Thus, mortality rates >98 and <90% indicated susceptibility and resistance, respectively. For mortalities ranged between 90 and 97% resistance is suspected and the presence of resistant genes in the population must be confirmed by further investigation (additional bioassay tests with the same insecticide and/or by conducting molecular or biochemical assays for known resistance mechanisms). Statistical analyses were performed with STATA version 10.4 (Stata Corporation; College Station, TX, USA) and statistical significance was set at 5%.

The time to knock down 50 and 95% (KdT50 and KdT95) of pyrethroid and DDT-tested mosquitoes were estimated using a log-time probit model with Polo Plus 1.0 software (LeOra Software). The KdT50 and KdT95 values were also estimated in synergist assays for pyrethroid and DDT. The ratio between KdT50 of resistant strains and susceptible strains referred as resistance ratio (RR50) was calculated, with Chi square (χ2) to compare groups. Mann–Whitney non-parametric test was used to compare the mean enzymatic level/activities of monooxygenases, NSEs and GSTs between the wild An. gambiae s.l. from Ehania-V1 and the susceptible Kisumu strain.


Mortality and knock-down rates

Mosquitoes displayed variable levels of mortality at 24 h, following exposure to the seven insecticides tested (Table 1). Mortality rates were above 90% for fenithrothion (98.0%) and deltamethrin (97.6%). However, DDT (8.3%), permethrin (39.6%) and alphacypermethrin (63.8%) yielded mortality rate below the WHO-referenced threshold (90%). The mortality rates in the control never exceeded 5% and so there was no need to correct with Abbott’s formula.

Table 1 Distribution of mortality to insecticides in An. gambiae s.l. 24 h post-exposure

The knock-down effects of pyrethroids and DDT on the An. gambiae s.l. population from Ehania-V1 compared to susceptible Kisumu strain are summarized in Table 2. The KdT50 values for An. gambiae Kisumu strain were approximately 12.6, 15.2 and 18.1 min for deltamethrin, alphacypermethrin and permethrin, respectively. KdT50 and KdT95 values recorded for wild An. gambiae s.l. population were approximately 57 and 122.6 min for deltamethrin and 83.9 and 144.7 min for alphacypermethrin, respectively (Table 2). However, KdT50 and KdT95 could not be determined as less than 50% of mosquitoes tested were knocked down after 60 min.

Table 2 Knockdown time (KdT) for 50 and 95% of tested An. gambiae Kisumu and An. gambiae s.l. Ehania-V1 to pyrethroids and DDT

Effect of synergist PBO

Absence vs presence of PBO in insecticide was compared to show the effect of PBO (Fig. 2). There was 3.4 and 9.0% increase in mortality rates recorded with bendiocarb and alphacypermethrin, respectively, when PBO was added, compare to these insecticides alone (bendiocarb: PBO absence = 87.25% vs PBO presence = 90.65% and alphacypermethrin: PBO absence = 63.81% vs PBO presence = 72.81%) without significant difference (p = 0.4325 and p = 0.1629, respectively). However, a slight decrease was observed in permethrin mortality rate, (PBO absence = 39.60% vs PBO presence = 36.89%); (p = 0.69040). Patterning DDT plus PBO a null mortality rate was observed (PBO absence = 8.33% vs PBO presence = 0%); (p = 0. 0032).

Fig. 2

Distribution of mortality rates of An. gambiae s.l. with or without PBO in Ehania in 2013

Anopheles gambiae species identification and kdr L1014F and ace-1 R G119S allele frequencies

Of the subset number of An. gambiae s.l. mosquitoes (n = 46) analyzed for sibling species identification, only An. coluzzii and An. gambiae s.s. were found in sympatry in Ehania-V1, and An. coluzzii was predominant (72 vs 28%, Table 3). High frequency of kdr 1014F mutation was found in both An. gambiae (91%) and An. coluzzii (96%). The ace-1 G119S mutation was found in these two species populations but at very low frequency (from 12 to 19%) and only at heterozygote state.

Table 3 Genotype frequencies of the kdr (L1014F) and ace-1 R (G119S) loci in An. gambiae s.l. population from Ehania-V1

Biochemical analyses

Mean level activities of the NSE (α- and β-naphthyl acetate) and mean amounts of MFO (cytochrome P450 s) and GST are presented in Table 4. The mean level activities of NSE for α- and β-naphthyl acetate were 0.081 and 0.084 μmol/mim/mg respectively in Kisumu strain. In wild population from Ehania-V1, mean α- and β-esterase was 0.187 and 0.175 μmol/mim/mg and both values are significantly higher than those recorded in Kisumu strain (p < 0.001). The GST level activity was significantly higher in the wild population from Ehania-V1 than in Kisumu strain (Ehania-V1 = 1.778, Kisumu = 0.226; p < 0.001. The An. gambiae s.l. population from Ehania-V1 showed comparable production of MFO (cytochrome P450s) amount to the laboratory susceptible strain Kisumu (Ehania-V1 = 0.119, Kisumu = 0.074; p = 0.277, Ns).

Table 4 Mean level of NSE, MFO and GST activity in An. gambiae s.l. tested population


This study was the first carried out in the area of Ehania-V1 to monitor the susceptibility status of malaria vector An. gambiae s.l. to WHO-recommended insecticides. Mortality rates with fenithrothion and deltamethrin was above the threshold set by WHO (90%). While resistance to pyrethroid insecticides is widely reported in Africa and particularly in the majority of the districts of Côte d’Ivoire [18, 27], the results showed apparent susceptibility to deltamethrin at this site in the South Eastern region. More investigation is required to confirm the resistance status of malaria vectors to this insecticide. The highest mortality rate observed with deltamethrin could provide a perspective for control together with organophosphate insecticides in this region. However, the current the results should be treated cautiously for two reasons. First, decrease in resistance to insecticide could result from the declining of selection pressure asserted by the use of this insecticide in a specific area. Indeed, previous report on susceptibility to deltamethrin was made in cotton field area of Korhogo, Northern Côte d’Ivoire following the breakdown of use of this insecticide during the political crisis [28]. This political crisis was also extended to all the country and impacted most agricultural settings of interest. Ehania region was also concerned by this disturbance of regular agricultural practices. Second possible reason could be linked to the frequency of insecticide application within the palm oil farm during the last decade. The study questionnaire administrated to the chief of workers to collect information on pesticides provided a list of insecticides used in Ehania-V1 industrial palm oil farm (Additional file 1). Listed pesticide formulations was also included Decis®, a deltamethrin based-product, but its frequency of use remains unknown yet and will also require more clarification in near future. However, a significant increase in knockdown time might be an indicator for the early detection of deltamethrin resistance [8]. Thus, more investigation will be necessary to understand the profile of deltamethrin use in public health and agriculture in the region. The mortality rates to DDT and other pyrethroids such as alphacypermethrin and permethrin were less than 90%. It was impossible to determine this knockdown time especially for permethrin and DDT. However, the knockdown time of wild An. gambiae exposed to alphacypermethrin and deltamethrin was more than four times higher compared to the susceptible An. gambiae Kisumu strain. In Ehania-V1, An. gambiae were also shown to be resistant to bendiocarb but the mortality was seven times lower than the one reported in a previous study from Tiassalé [12].

Similar to other regions of Côte d’Ivoire, including San Pédro, Abidjan, Man, Abengourou, Yamoussoukro and Korhogo [29], both An. coluzzii and An. gambiae s.s. were found in Ehania-V1 locality within the An. gambiae complex with An. coluzzii predominant. The abundance of An. coluzzii was repeatedly reported in the Southern part of Côte d’Ivoire [12, 15].

Only kdr L1014F mutation was detected in An. gambiae s.s. and An. coluzzii from Ehania-V1, at overall high frequency compared to those reported in the western region of Côte d’Ivoire with low frequencies (0–20%). Findings are similar to studies carried out in the Northern (Korhogo, Kaforo) region with high frequencies of kdr L1014F mutation (70 and 80%) [29].

In Tiassalékro (Southern Côte d’Ivoire) where An. gambiae showed multiple resistance to insecticide classes, this mutation frequency was high (83%) [12], but below the one observed in Ehania-V1. Furthermore <20% of ace-1 R G119S allele proportion has been found in the study site. The results confirm those of Ahoua et al. [15], which previously showed the absence of homozygous resistant individuals at the ace-1 locus.

Results from synergist assays (PBO) showed no significant effect on mortality rate after pre-exposition to insecticides. Therefore, MFO was probably not involved in resistance in this area in contrast to results from M’Bé, in Central Côte d’Ivoire [30]. Indeed a significant difference in GST and NSE activity was observed when comparing wild strains to the susceptible Kisumu strain. The non-detection of P450 activity in resistance observed in Ehania-V1 appears as a positive outcome for further control strategies as metabolic-based P450 resistance remains a major challenge for the control of malaria vectors in the Africa region.

The strong resistance recorded for DDT, permethrin and alphacypermethrin may be also due to the presence of several environmental pollutants and pesticide residues caused by the extensive use of insecticides to treat palm trees and crops since 1969 [31].


Resistance of An. gambiae s.l. from Ehania-V1 was likely due to kdr and probably to esterase activities for alphacypermethrin and ace-1 R for bendiocarb. Multiple mechanisms of resistance in Ehania-V1’s mosquito’s population were suspected and require in-depth investigation. The increase ability of Anopheles populations to resist to lethal doses of insecticides has reduced the efficacy of most insecticides used for vector control. Bendiocarb resistance is also emerging in Ehania-V1 mosquitoes and further investigation will be needed to understand the mechanisms. Selection pressure asserted by the use of insecticides in agriculture and probably in public health could be a cause of the resistance in major insecticides in this region. However, an apparent susceptibility to deltamethrin has been identified and if confirm, may precludes perspective for malaria control along with organophosphate in Ehania. These results should be shared with the National Malaria Control Programme in Côte d’Ivoire in order to encourage collaboration with the PALMCI health department toward strong complementary analysis and potential plan for implementation of further control strategies based on deltamethrin and/or organophosphates.



Palm oil Company of Côte d’Ivoire


World Health Organization


National Malaria Control Programme


long-lasting insecticide-treated nets


indoor residual spraying


  1. 1.

    WHO. World malaria report 2016. Geneva: World Health Organization; 2016.

    Google Scholar 

  2. 2.

    WHO. Test procedures for insecticide resistance monitoring in malaria vector mosquitoes. Geneva: World Health Organization; 2013.

    Google Scholar 

  3. 3.

    Lengeler C. Insecticide-treated bed nets and curtains for preventing malaria. Cochrane Database Syst Rev. 2009;2:CD000363.

    Google Scholar 

  4. 4.

    Pluess B, Taner FC, Lengeler C, Sharp BL. Indoor residual spraying for preventing malaria. Cochrane Database Syst Rev. 2010;4:CD006657.

    Google Scholar 

  5. 5.

    Zaim M, Aito A, Nakashima N. Safety of pyrethroid-treated mosquito nets. Med Vet Entomol. 2000;114:1–5.

    Article  Google Scholar 

  6. 6.

    Bhatt S, Weiss DJ, Cameron E, Bisanzio D, Mappin B, Dalrymple U, et al. The effect of malaria control on Plasmodium falciparum in Africa between 2000 and 2015. Nature. 2015;526:207–11.

    CAS  Article  PubMed  PubMed Central  Google Scholar 

  7. 7.

    Elissa N, Mouchet J, Rivière F. Resistance of Anopheles gambiae s.s. to pyrethroids in Côte d’Ivoire. Ann Soc Belg Med Trop. 1993;73:291–4.

    CAS  PubMed  Google Scholar 

  8. 8.

    Chandre F, Darrier F, Manga L, Akogbeto M, Faye O, Mouchet J, et al. Status of pyrethroid resistance in Anopheles gambiae sensu lato. Bull World Health Organ. 1999;77:230–4.

    CAS  PubMed  PubMed Central  Google Scholar 

  9. 9.

    Fanello C, Petrarca V, della Torre A, Santolamazza F, Dolo G, Coulibaly M, et al. The pyrethroid knock-down resistance gene in the Anopheles gambiae complex in Mali and further indication of incipient speciation within An. gambiae s.s. Insect Mol Biol. 2003;12:241–5.

    CAS  Article  PubMed  Google Scholar 

  10. 10.

    Etang J, Manga L, Chandre F, Guillet P, Fondjo E, Mimpfoundi R, et al. Insecticide susceptibility status of Anopheles gambiae s.l. (Diptera: Culicidae) in the Republic of Cameroon. J Med Entomol. 2003;40:491–7.

    CAS  Article  PubMed  Google Scholar 

  11. 11.

    WHO. World malaria report 2015. Geneva: World Health Organization; 2015.

    Google Scholar 

  12. 12.

    Edi CV, Koudou BG, Jones CM, Weetman D, Ranson H. Multiple insecticide resistance in Anopheles gambiae mosquitoes, Southern Côte d’Ivoire. Emerg Infect Dis. 2012;18:1508–11.

    CAS  Article  PubMed  PubMed Central  Google Scholar 

  13. 13.

    Corbel V, Hougard JM, N’Guessan R, Chandre F. Evidence for selection of insecticide resistance due to insensitive acetylcholinesterase by carbamate-treated nets in Anopheles gambiae s.s. (Diptera: Culicidae) from Côte d’Ivoire. J Med Entomol. 2003;40:985–8.

    CAS  Article  PubMed  Google Scholar 

  14. 14.

    N’Guessan R, Darriet F, Guillet P, Carnevale P, Traoré-Lamizana M, Corbel V, et al. Resistance to carbosulfan in Anopheles gambiae from Ivory Coast based on reduced sensitivity of acetylcholinesterase. Med Vet Entomol. 2003;17:19–25.

    Article  PubMed  Google Scholar 

  15. 15.

    Ahoua Alou LP, Koffi AA, Adja AM, Tia E, Kouassi PK, Koné M, et al. Distribution of ace-1 R and resistance to carbamates and organophosphates in Anopheles gambiae s.s. populations from Côte d’Ivoire. Malar J. 2010;9:167.

    Article  PubMed  PubMed Central  Google Scholar 

  16. 16.

    Konan KG, Koné AB, Konan YL, Fofana D, Konan KL, Diallo A, et al. Resistance of Anopheles gambiae s.l. to pyrethroids and DDT at Tiassalékro, an irrigated rice-growing village in the southern forest of Ivory Coast. Bull Soc Pathol Exot. 2011;104:303–6 (in French).

    CAS  Article  PubMed  Google Scholar 

  17. 17.

    Ahoua Alou LP, Koffi AA, Adja AM, Assi SB, Kouassi KP, N’Guessan R. Status of pyrethroid resistance in Anopheles gambiae s.s. M form prior to the scaling up of long-lasting insecticidal nets (LLINs) in Adzopé, Eastern Côte d’Ivoire. Parasites Vectors. 2012;5:289.

    Article  PubMed  PubMed Central  Google Scholar 

  18. 18.

    Edi CV, Djogbénou L, Jenkins AM, Regna K, Muskavitch MA, Poupardin R, et al. CYP6 P450 enzymes and ACE-1 duplication produce extreme and multiple insecticide resistance in the malaria mosquito Anopheles gambiae. PLoS Genet. 2014;10:e1004236.

    Article  PubMed  PubMed Central  Google Scholar 

  19. 19.

    Diabaté A, Baldé T, Chandre F, Akogbeto M, Guiguemde TR, Darriet F, et al. The role of agricultural use of insecticides in resistance to pyrethroids in Anopheles gambiae s.l. in Burkina Faso. Am J Trop Med Hyg. 2002;67:617–22.

    PubMed  Google Scholar 

  20. 20.

    Collins FH, Finnerty V, Petrarca V. Ribosomal DNA-probes differentiate five cryptic species in the Anopheles gambiae s.s. complex. Parasitology. 1998;30:231–40.

    Google Scholar 

  21. 21.

    Scott JA, Brogdon WG, Collins FH. Identification of single specimens of the Anopheles gambiae complex by the polymerase chain reaction. Am J Trop Med Hyg. 1993;49:520–9.

    CAS  PubMed  Google Scholar 

  22. 22.

    Santolamazza F, Mancini E, Simard F, Qi Y, Tu Z, della Torre A. Insertion polymorphisms of SINE200 retrotransposons within speciation islands of Anopheles gambiae molecular forms. Malar J. 2008;7:168.

    Article  Google Scholar 

  23. 23.

    Martinez-Torres D, Chandre F, Williamson MS, Darriet F, Bergé JB, Devonshire P, et al. Molecular characterization of pyrethroid knock-down resistance kdr in the major malaria vector Anopheles gambiae s.s. Insect Mol Biol. 1998;7:179–84.

    CAS  Article  PubMed  Google Scholar 

  24. 24.

    Weill M, Malcolm C, Chandre F, Mogensen K, Berthomieu A, Marquine M, et al. The unique mutation in ace-I giving high insecticides resistance is easily detectable in mosquito vectors. Insect Mol Biol. 2004;13:1–7.

    CAS  Article  PubMed  Google Scholar 

  25. 25.

    WHO. Techniques to detect resistance mechanisms (Field and laboratory manual). Geneva: World Health Organization; 1998.

    Google Scholar 

  26. 26.

    Abbott WS. A method for computing the effectiveness of an insecticide. J Econ Entomol. 1925;18:265–76.

    CAS  Article  Google Scholar 

  27. 27.

    Ranson H, N’Guessan R, Lines J, Moiroux N, Nkuni Z, Corbel V. Pyrethroid resistance in African anopheline mosquitoes: what are the implications for malaria control? Trends Parasitol. 2011;27:91–8.

    CAS  Article  PubMed  Google Scholar 

  28. 28.

    Koffi AA, Ahoua Alou LP, Adja MA, Koné M, Chandre F, N’Guessan R. Update on resistance status of Anopheles gambiae s.s. to conventional insecticides at a previous WHOPES field site “Yaokoffikro” 6 years after the political crisis in Côte d’Ivoire. Parasites Vectors. 2012;5:68.

    CAS  Article  PubMed  PubMed Central  Google Scholar 

  29. 29.

    Koffi AA, Ahoua Alou LP, Kabran JPK, N’Guessan R, Pennetier C. Re-visiting insecticide resistance status in Anopheles gambiae from Côte d’Ivoire: a nation-wide informative survey. PLoS ONE. 2013;8:e82387.

    Article  PubMed  PubMed Central  Google Scholar 

  30. 30.

    Sinka ME, Bangs MJ, Manguin S, Coetzee M, Mbogo CM, Hemingway J, et al. The dominant Anopheles vectors of human malaria in Africa, Europe and Middle East: occurrence data, distribution maps and bionomic precis. Parasites Vectors. 2010;3:117.

    Article  PubMed  PubMed Central  Google Scholar 

  31. 31.

    Palmci. Liste des produits insecticides utilisés par les agents de PALMCI pour lutter contre les insectes. Working paper. Aboisso, Cote d’Ivoire; 2016.

Download references

Authors’ contributions

CMAS designs the study, collects data and drafted the paper. MAA contributed to study design, coordinated field activities and read the paper. KAA provide insecticides and contributed in drafting the paper. LPAA conducted laboratory work, interpreted the data and revised the manuscript. AFO contributed to data analysis and revised the paper. EAVC analyzed and interpreted the data and contributed to improvement of the manuscript prior publication. DM contributed to improvement of the manuscript prior publication. BGK designed the study, coordinated field activities, revised the manuscript and assisted with data analysis. TY supervised the study. All authors read and approved the final manuscript.


The authors are grateful to all the participants in the study. They thank the local authorities, the IFU Director, the IFU workers, and local population of Ehania-V1 for their consent to carry out our study and for their participation. Special thanks go to Jean-Paul Kabran Kouamé from Institut Pierre Richet, Bouaké and Aboubakar Siddick from Centre de Recherche Entomologique de Cotonou (Benin) for their technical assistance during WHO susceptibility test.

Competing interests

The authors declare that they have no competing interests.

Consent for publication

Consent form for publication was signed by all authors and was submitted during the first submission. This form is submitted again during the resubmission.

Ethics approval and consent to participate

This proposal was reviewed and approved by the Scientific Committee of Institut Pierre-Richet prior to his implementation.


The current work was funded by core funds from Institut Pierre Richet located in Bouake, Central Cote d’Ivoire and Centre Suisse de Recherches Scientifiques en Cote d’Ivoire. EACV is funded by the Wellcome Trust under Grant No. 110430/Z/15/Z.

Publisher’s Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Author information



Corresponding author

Correspondence to Benjamin G. Koudou.

Additional file

Rights and permissions

Open Access This article is distributed under the terms of the Creative Commons Attribution 4.0 International License (, which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. The Creative Commons Public Domain Dedication waiver ( applies to the data made available in this article, unless otherwise stated.

Reprints and Permissions

About this article

Verify currency and authenticity via CrossMark

Cite this article

Sadia-Kacou, C.M.A., Alou, L.P.A., Edi, A.V.C. et al. Presence of susceptible wild strains of Anopheles gambiae in a large industrial palm farm located in Aboisso, South-Eastern of Côte d’Ivoire. Malar J 16, 157 (2017).

Download citation


  • Malaria
  • Indoor Residual Spray
  • G119S Mutation
  • Piperonyl Butoxide
  • Insecticide Class


By submitting a comment you agree to abide by our Terms and Community Guidelines. If you find something abusive or that does not comply with our terms or guidelines please flag it as inappropriate. Please note that comments may be removed without notice if they are flagged by another user or do not comply with our community guidelines.