Abstract

BackgroundThe effectiveness of Long-Lasting Insecticidal Nets and Indoor Residual Spraying in malaria vector control is threatened by vector resistance to insecticides. Knowledge of mosquito habitats and patterns of insecticide resistance would facilitate the development of appropriate vector control strategies. Therefore, we investigated An. coluzzii larval habitats and resistance to insecticides in the Manoka rural island area compared with the Youpwe suburban inland area, in Douala VI and II districts respectively.MethodsAnopheline larvae and pupae were collected from open water bodies in December 2013 and April 2014 and reared until adult emergence. Two to four day old emerging females were morphologically identified as belonging to the An. gambiae complex and used for WHO susceptibility tests with 4 % DDT, 0.75 % permethrin, and 0.05 % deltamethrin, with or without piperonyl butoxide (PBO) synergist. Control and surviving specimens were identified down to the species using a PCR-RFLP method. Survivors were genotyped for kdr L1014 mutations using Hot Oligonucleotide Ligation Assay.ResultsIn both study sites, ponds, residual puddles, boats, and drains were identified as the major An. gambiae s.l. larval habitats. A total of 1397 females, including 784 specimens from Manoka and 613 from Youpwe, were used for resistance testing. The two mosquito populations displayed resistance to DDT, permethrin and deltamethrin, with variable mortality rates from 1 % to 90 %. The knock-down times were also significantly increased (at least 2.8 fold). Pre-exposure of mosquitoes to PBO did not impact on their mortality to DDT, conversely the mortality rates to permethrin and deltamethrin were significantly increased (7.56 ≤ X2 ≤ 48.63, df = 1, p < 0.01), suggesting involvement of P450 oxidases in pyrethroid resistance. A subsample of 400 An. gambiae s.l. specimens including 280 control and 120 survivors from bioassays were all found to be An. coluzzii species. Only the kdr 1014 F mutation was found in survivors, with 88.5 % (N = 76) and 75 % (N = 44) frequencies in Youpwe and Manoka respectively.ConclusionThis is the first report of An. coluzzii resistance to insecticides in an insular area in Cameroon. Since permanent larval habitats have been identified, larval source management strategies may be trialed in this area as complementary vector control interventions.

Highlights

  • The effectiveness of Long-Lasting Insecticidal Nets and Indoor Residual Spraying in malaria vector control is threatened by vector resistance to insecticides

  • Anopheles arabiensis is mostly found in the Northern savannah Regions, while An. gambiae s.s. and An. coluzzii are widespread throughout Cameroon [8]

  • The similarity of An. coluzzii distribution in the Manoka island area and Youpwe mainland quarter, its presence in the same range of breeding sites, and regular connection between the two settings by boat transportation and patterns of insecticide resistance suggest gene flow between mosquito populations from the two areas. These findings reemphasize the spread of insecticide resistance in species of the An. gambiae complex from various ecological areas in Cameroon, and the need for adequate resistance management strategies

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Summary

Introduction

The effectiveness of Long-Lasting Insecticidal Nets and Indoor Residual Spraying in malaria vector control is threatened by vector resistance to insecticides. The uncontrolled population growth in many areas has led to extensive deforestation, irrigation, and unplanned urbanization These high populations and associated environmental modifications create ecological conditions favouring the proliferation of arthropod vectors, including malaria-transmitting mosquitoes [2]. Mainly based on the extensive use of Long-Lasting Insecticidal Nets (LLINs) and Indoor Residual Spraying (IRS), is a corner stone in current malaria control and elimination strategies [1]. In Cameroon, malaria annually accounts for 35–40 % of deaths in health facilities, 40–45 % of out-patient consultations, and 30 % of hospitalisations [4]. Anopheles arabiensis is mostly found in the Northern savannah Regions, while An. gambiae s.s. and An. coluzzii are widespread throughout Cameroon [8]. In Cameroon, little is known about habitat segregation between An. gambiae s.s. and An. coluzzii in Island areas

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