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Parasites and vectors of malaria on Rusinga Island, Western Kenya



There is a dearth of information on malaria endemicity in the islands of Lake Victoria in western Kenya. In this study malaria prevalence and Plasmodium sporozoite rates on Rusinga Island were investigated. The contribution of different Anopheles species to indoor and outdoor transmission of malaria was also determined.


Active case detection through microscopy was used to diagnose malaria in a 10% random sample of the human population on Rusinga Island and a longitudinal entomological survey conducted in Gunda village in 2012. Nocturnally active host-seeking mosquitoes were captured indoors and outdoors using odour-baited traps. Anopheles species were tested for the presence of Plasmodium parasites using an enzyme linked immunosorbent assay. All data were analyzed using generalized linear models.


Single infections of Plasmodium falciparum (88.1%), P. malariae (3.96%) and P. ovale (0.79%) as well as multiple infections (7.14%) of these parasites were found on Rusinga Island. The overall malaria prevalence was 10.9%. The risk of contracting malaria was higher among dwellers of Rusinga West than Rusinga East locations (Odds Ratio [OR] = 1.5, 95% Confidence Interval [CI] 1.14 – 1.97, P = 0.003). Parasite positivity was significantly associated with individuals who did not use malaria protective measures (OR = 2.65, 95% CI 1.76 – 3.91, p < 0.001). A total of 1,684 mosquitoes, including 74 anophelines, were captured. Unlike Culex species, more of which were collected indoors than outdoors (P < 0.001), the females of An. gambiae s.l. (P = 0.477), An. funestus s.l. (P = 0.153) and Mansonia species captured indoors versus outdoors were not different. The 46 An. gambiae s.l. collected were mainly An. arabiensis (92.3%). Of the 62 malaria mosquitoes tested, 4, including 2 indoor and 2 outdoor-collected individuals had Plasmodium.


The rather significant and unexpected contribution of P. malariae and P. ovale to the overall malaria prevalence on Rusinga Island underscores the epidemiological importance of these species in the big push towards eliminating malaria. Although current entomological interventions mainly target indoor environments, additional strategies should be considered to prevent outdoor transmission of malaria.


Malaria is a public health problem in Kenya despite intense deployment of vector control tools. Malaria prevalence is highest in areas around the shores of Lake Victoria in western Kenya [1,2]. The main tools used for vector control in this region include long lasting insecticidal nets (LLINs) and indoor residual spraying (IRS) [3]. Anopheles gambiae s.l. has been reported to be the main malaria vector in western Kenya [3-6]. The abundance and density of this vector has been clearly documented in the islands of Lake Victoria [4]. However, there is a dearth of information on the role of anophelines in indoor and outdoor transmission in the aforementioned islands. In addition, little information on malaria parasites in these islands is available. Compared to other areas in western Kenya where epidemiological studies have been conducted [5], very little is known on malaria transmission in the islands of Lake Victoria. This study sought to determine malaria prevalence, Plasmodium sporozoite rates and the contribution of different Anopheles species to indoor and outdoor malaria transmission on Rusinga Island, western Kenya. The association between morbidity and use of malaria preventive measures was also evaluated.


Study site

This study was conducted on Rusinga Island, which is located in Mbita sub-county in western Kenya. Rusinga Island is predominantly rural and is connected to the mainland via a causeway at Mbita Point Township. Residents of Rusinga Island rely on the neighbouring Mbita town for regional transportation, access to banking services and other urban economic services. The island covers an area of 42 km2 and the terrain is mainly rocky and hilly. The centre of the Island is characterized by a large hill called Ligogo. Shrubs constitute the main vegetation on the island but the land has been extensively deforested. The island is divided into two administrative sections namely Rusinga East and Rusinga West sub-locations. The dominant ethnic group is Luo who mainly engage in artisanal capture fishing and small-scale trading [7]. Subsistence farming of drought-resistant crops is also practised. The subsistence crops cultivated on Rusinga Island include maize, vegetables, potatoes and millet. Malaria in Mbita sub-county is perennial with peaks occurring in July, shortly after the long rainy season [8]. Fishing is the main economic activity on the island and is mainly conducted by adult males. Women are mostly involved in fish processing and trading. Other fishing-related activities that are carried out on the island include boat making and fish net repair.

Malaria burden and parasite diversity on Rusinga Island

A cross-sectional malaria survey was conducted in all villages on Rusinga Island in October and November 2012 to determine malaria parasite diversity and prevalence. A sample size of 2,240 study participants was determined using the formula proposed by Daniel [9] and Naing et al. [10]. The selected study participants were mobilized by project staff performing home visits and requesting human research subjects to turn up at the nearest one of eight primary schools that served as sentinel malaria testing sites.

Each participant’s body temperature was measured using an electronic thermometer (Hangzhou Hua’an Medical & health instruments Co. Ltd., China). Fever was defined as temperature above 37.5°C. Malaria infection status was tested microscopically using participants’ finger pricked blood smears stained with 10% Giemsa. The blood smears were examined by two experienced microscopists. The first one recorded malaria positivity and identified malaria parasites to species level. The second microscopist performed quality assurance before a final result was determined. A slide was categorized as negative if no malaria parasite was seen after scanning 100 microscope fields. Individuals found positive for malaria were treated with a dose of artemether-lumefantrine (AL) according to the Kenya national guidelines for the diagnosis, treatment and prevention of malaria [11]. Malaria prevalence was calculated as the proportion of participants with malaria from the total number of individuals tested.

Gametocyte prevalence was measured to determine the level of human to mosquito malaria transmission potential. The study participants were screened for gametocytes of P. falciparum only. Blood smears were considered negative if no gametocyte was detected after examining 100 fields. Gametocyte prevalence was calculated as the proportion of human subjects harbouring gametocytes from the overall number tested.

A questionnaire was administered during the malaria survey to determine the association between malaria infection and use of preventive measures. The respondent’s demographic characteristics and use of malaria prevention measures were correlated to their malaria infection status.

Malaria vector species and transmission potential on Rusinga Island

A longitudinal entomological survey was conducted in Gunda village in Rusinga West sub-location from June to December 2012. Nocturnally active host-seeking mosquitoes were captured and their indoor and outdoor densities and species composition determined. The mosquitoes were collected using odour-baited MM-X traps (American Biophysics, Corp., North Kingston, RI) containing a synthetic mosquito attractant known as Mbita blend [12].

The mosquitoes were collected from six randomly selected village houses spaced at least 25 metres apart [13]. The houses were similar in structure with roofs made of iron sheets, walls made of mud and open eaves. Each house had two rooms. Household members were supplied with untreated mosquito nets that were used throughout the study. Each house was fitted with one MM-X trap per night. The MM-X traps were placed above the foot end of a bed occupied by a human subject. Outdoor biting mosquitoes were collected by hanging traps within the peri-domestic environment approximately 15 cm off the ground. The MM-X traps were operated from 6 pm till 7 am the following morning. Mosquitoes were collected for four nights in a week, with alternating nights for indoor and outdoor trapping. The same houses were used throughout the study. Experiments were replicated over 72 nights, 34 nights with six traps per night indoors (i.e. 204 trap nights) and 38 nights with 6 traps per night outdoors (i.e. 228 trap nights).

Captured mosquitoes were counted, sorted by sex and identified morphologically using the keys of Gillies and DeMeillion [14]. Anopheline mosquitoes were preserved using silica gel awaiting further processing. Legs of female mosquitoes were used to identify the sibling species of An. gambiae s.l. using the PCR technique [15]. The head and thorax of female anopheline mosquitoes were tested for the presence of Plasmodium sporozoites using an enzyme linked immusorbent assay (ELISA) [16]. The infection rate of mosquitoes captured during the entomological survey was measured as the proportion of mosquitoes found to contain sporozoites.

Ethical considerations

Ethical clearance was obtained from the Kenya Ethical Review Committee located at the Kenya Medical Research Institute (NON-SSC No. 280). Consent was obtained from participants prior to the malaria survey. Written consent was sought from parents and care givers of children to allow minors to participate in the study. Consent was also obtained from heads of households that provided approval for mosquito collection in houses.

Statistical analysis

Data were analysed using R statistical software version 2.15.2. Data collected during the malaria survey were analyzed using multivariate logistic regression. The outcome of the malaria test (whether positive or negative for malaria parasites) was treated as the dependent variable. The effect of other variables, specifically sex, location and age group were also analyzed. The response variable in the entomology survey was derived from count data (mosquito numbers). The untransformed data was analyzed by fitting generalized linear models [17] with a poisson regression. The packages mass, effects, epicalc, multcomp, lme4, gee, geepack and aod [18] were loaded before running the analysis. The night mosquitoes were captured (day of experiment) was included in the model as a factor. Statistical significance was set at P < 0.05.


Malaria burden and parasite diversity on Rusinga Island

A total of 2,318 individuals from all age groups participated in the malaria survey. The age of study participants ranged from 1 year to 102 years. The majority of the participants were between the age 0 – 14 (n = 1197, 51.7%), while the least were above 60 (n = 131, 5.7%). The median age was 14 years. Of the individuals enrolled in the study 1,263 (54.4%) were female while 1,055 (45.6%) were male (Table 1). Participants from Rusinga East were 1,248 (53.8%) while those from Rusinga West were 1,070 (46.1%).

Table 1 Characteristics of study participants of the survey carried out to determine malaria burden and parasite diversity on Rusinga Island

Overall, blood samples from 252 (10.9%) participants had malaria parasites. Three malaria species were identified namely Plasmodium falciparum, Plasmodium malariae and Plasmodium ovale. Among the 252 individuals harboring malaria parasites 222 (88.1%) were infected with P. falciparum, 10 (3.96%) with P. malariae and 2 (0.79%) with P. ovale. Of the remaining 18 individuals with malaria parasites, 16 (6.34%) had mixed infections of P. falciparum and P. malariae, 1 (0.39%) had a mixed infection of P. falciparum and P ovale and 1 (0.39%) had a mixed infection of all 3 malaria species (Table 2). The overall prevalence of mixed Plasmodium infections was 7.14%.

Table 2 Malaria infection among individuals from Rusinga East and West locations

Out of the total number of blood smears screened for gametocytes 16 (0.7%) participants tested positive. School-going children had the highest burden of gametocytes. Of the 16 individuals with gametocytes 11 (69%) were 0 – 14 years old, 1 (6.25%) was in the 15 – 30 year age bracket, another 1 (6.25%) in the 30 – 45 year age bracket and 3 (18.7%) were in the 45 – 60 year old age bracket (Table 3). Among the gametocyte carriers 6 (37.5%) were from Rusinga East and 10 (62.5%) from Rusinga West. There was a significant association between malaria parasitemia and location (OR = 1.5, 95% CI 1.14 – 1.97, p = 0.003) (Table 4). Individuals who did not use malaria protective measures whilst sleeping were two times more likely to get malaria (95% CI 1.76 – 3.91, p < 0.001) compared to those who did (Table 4).

Table 3 Proportion of participants with gametocytes in the survey carried out to determine malaria burden and parasite diversity on Rusinga Island
Table 4 Factors associated with malaria parasitemia among residents of Rusinga Island

Malaria vector species and transmission potential on Rusinga Island

A total of 1,681 mosquitoes, including both males and females, were collected (Table 5). The species caught were An. gambiae s.l., An. funestus s.l., Culex species, Mansonia species, and Aedes species. Among the collected mosquitoes 79 (4.7%; constituting 74 females and 5 males) belonged to the genus Anopheles while 1,602 (95.3%; constituting 1,357 females and 245 males) were culicine species. Of the total female anophelines collected, An. gambiae s.l. was the most abundant malaria vector (n = 46; 62%). Female An. funestus mosquitoes accounted for 38% (n = 28) of the total female anophelines collected. Overall, Culex species were the most abundant non-malaria mosquitoes collected (n = 1,493).

Table 5 Number of mosquitoes captured inside (204 trap nights) and outside (228 trap nights) houses in Gunda village on Rusinga Island

Although a higher number of female An. gambiae s.l. mosquitoes were captured outdoors (n = 27) than indoors (n = 19) these catches did not differ significantly (P = 0.477). Similarly, there was no statistical difference between the number of female An. funestus s.l. mosquitoes captured indoors versus outdoors (P = 0.153). Of the 46 An. gambiae s.l. mosquitoes subjected to polymerase chain reaction (PCR) analysis, 39 were successfully identified. The rest (7 samples) failed to amplify. Of the 19 An. gambiae s.l. females captured indoors, 12 (92.3%) were identified as An. arabiensis and 1 (7.7%) as An. gambiae s.s. Of the 19 An. gambiae s.l. females captured indoors, 6 failed to amplify. Of the 27 An. gambiae s.l. mosquitoes captured outdoors, 24 (92.3%) were identified as An. arabiensis and 2 (7.7%) as An. gambiae s.s. Only 1 specimen of the 27 An. gambiae s.l. mosquitoes captured outdoors did not amplify. These data indicate that An. arabiensis is the dominant malaria vector among siblings of the An. gambiae complex on Rusinga Island.

Of the total 62 malaria vectors tested for the presence of Plasmodium falciparum sporozoites 28 and 34 were captured indoors and outdoors, respectively. Overall 4 mosquitoes were sporozoite positive of which 2 (7.14%) were captured indoors (1 An. arabiensis and 1 An. funestus) and the other 2 (5.88%) outdoors (1 An. arabiensis and 1 An. funestus). The overall sporozoite infectivity rate was 6.45% (4/62). Site-specific sporozoite rates were 7.14% for indoors and 5.88% for outdoors.

There was a significant difference in the number of Culex spp. captured indoors compared to those captured outdoors (P < 0.001). Among the 1,249 female Culex species of mosquitoes caught 665 (52.2%) were caught indoors and 585 (46.8%) were collected outdoors. No statistical difference was found between the females of Mansonia (P = 0.681) and Aedes mosquito species (P = 0.291) captured indoors and outdoors. Culex species yielded the largest collection of male mosquitoes (n = 244), with significantly higher numbers of the mosquitoes being collected indoors (n = 132; 54.1%) than outdoors (n = 112; 45.9%) (P = 0.038).


In this study, single infections of Plasmodium falciparum, P. malariae and P. ovale as well as multiple infections of these species were observed. The overall malaria prevalence on Rusinga Island was 10.9%. The risk of contracting malaria was higher among dwellers of Rusinga West than Rusinga East locations. Parasite positivity was significantly associated with individuals who did not use malaria protective measures. The numbers of females of the main malaria vectors namely Anopheles gambiae s.l. (consisting largely of An. arabiensis) and An. funestus collected indoors and outdoors did not differ significantly. This was also the case with females of species of Mansonia. On the contrary significantly more male and female Culex species were collected indoors than outdoors. Interestingly the ratios of An. gambiae versus An. arabiensis in samples collected indoors versus outdoors were similar, albeit with overall higher numbers of mosquitoes being collected outdoors. Similarly, the numbers, and more or less the ratios, of malaria infected mosquitoes collected indoors and outdoors were equal.

Malaria prevalence among residents of Rusinga Island was 10.9%. However, a prevalence study conducted on the Island in November 1998 revealed that the prevalence was 24.4% [8]. This suggests that there has been a reduction in the burden of malaria in the study area probably due to the increased use of LLINs [4]. However, the prevalence of malaria reported in this study is generally lower than the 40% reported by Noor et al. around the shores of Lake Victoria in 2009 [1]. Identification of malaria parasites by microscopy largely depends on the skills and experience of the microscopist [19], thus it is likely that the prevalence rate of malaria reported in this study is an underestimate.

Single infections of P. falciparum, P. malariae and P. ovale as well as multiple infections of these parasites were found in the study area. The predominant malaria species on Rusinga Island was P. falciparum. This finding is consistent with those of other studies conducted in Mbita sub-county [8,20,21]. Plasmodium malariae was reported as a minor species responsible for malaria infections on Rusinga Island. Previous studies conducted in the area also documented P. malariae as being responsible for single and co-infections of malaria in Mbita sub-county [20,21]. In this study, single as well as mixed infections of Plasmodium ovale were detected in a few individuals. Reported cases of malaria infections caused by P. ovale are rare and could be because of under-diagnosis or low transmission rates [22,23]. The parasite is known for its low densities [24,25] which contribute to difficulties in diagnosis. Furthermore, the greatest shortcoming of the diagnostic technique used in this study i.e. microscopic examination of patients’ peripheral blood smears stained with Giemsa is low sensitivity. This may explain the small number of individuals diagnosed with P. ovale malaria in the study area. Cases of P. ovale infections have been reported in other areas of western Kenya [26,27].

Malaria burden was found to be unevenly distributed with individuals from Rusinga West location recording more malaria cases. This can be attributed to the higher number of malaria mosquito breeding sites found in Rusinga West compared to Rusinga East (Mukabana, unpublished data). Most of the breeding sites recorded in Rusinga West were man-made [28] and created to sustain livelihood activities. With regards to outdoor fishing activities, more fishing activities are conducted in Rusinga West compared to East. A higher number of fishing beaches engaged in nocturnal fishing activities are found in Rusinga West (five) compared to East (three).

It is not surprising that the gametocyte prevalence detected by microscopy was as low as 0.7%. A study conducted in Mbita hospital, less than two kilometres from Rusinga Island reported a 0.9% prevalence of gametocytes among patients seeking outpatient services [21]. Gametocytes have been known to be low in densities thus can easily go undetected when screened microscopically [29]. Of the total parasite load in an infected person, the proportion of gametocytes has been reported to be 0.2% and 5.7% in children and adults, respectively [30]. Gametocytes are the sexual stages of the malaria parasite responsible for transmission from human to mosquito. This study shows that a small subpopulation of humans is infective and may be responsible for maintaining malaria transmission on Rusinga Island. It is important to note that this infective subpopulation may be higher if the presence of gametocytes is detected using molecular techniques.

This study demonstrated that individuals who did not use malaria protective measures whilst sleeping indoors at night were at a higher risk of malaria. Similar findings have been reported in other parts of Africa [31,32]. The majority of the adult population on Rusinga Island are fishermen who engage in nocturnal outdoor activities and therefore hardly use LLINs consistently. A review conducted by Pulford et al. [33] documented several reasons why people do not sleep under LLINs. Spending time elsewhere, for instance, at the work place at night, was cited as a reason for not using an LLIN even when one was available [33]. An increase in outdoor biting has been reported in several areas in sub-Saharan Africa [34-36]. Although approximately 80% of malaria transmission occurs indoors [37], outdoor malaria transmission is still important. Indoor vector control interventions are effective and have been reported to reduce malaria transmission in several areas [38-40], but are insufficient and extra effort is required to eliminate malaria. This should be especially applied in settings with intense regular nocturnal outdoor human activities. Since malaria transmission occurs where mosquitoes bite humans, vector control strategies need to be developed that also target outdoor biting mosquito populations [41] in order to achieve malaria elimination [42-45].

The lack of a statistical difference between the numbers of female malaria vectors collected indoors and outdoors, with higher numbers of the mosquitoes being collected outdoors than indoors, underscores the epidemiological importance of understanding and investing in outdoor transmission control in the current big push towards eliminating malaria [46]. It is likely that An. arabiensis and An. funestus are responsible for transmitting malaria indoors and outdoors in the study area. Anopheles arabiensis is known to be opportunistic, preferring to feed outdoors [47] on humans and animals depending on availability [48]. Several studies have also reported An. arabiensis as being partially responsible for indoor malaria transmission in several areas [49-52]. Anopheles funestus s.s. Giles has been identified as the main vector among siblings in the An. funestus group found in Mbita sub-county [4]. This vector prefers to rest indoors and feed on humans [53,54].

The findings of this study corroborate those of Futami et al. [4] who reported that An. arabiensis had replaced An. gambiae as the main malaria vector in the study area. Similar cases of species shifts among populations of malaria vectors have been reported elsewhere in Kenya [3,55,56] and Tanzania [57]. The species shifts among An. gambiae and An. arabiensis populations were reported to occur after wide coverage, ownership, and use of LLINs [3,55]. Anopheles arabiensis has been known to survive in areas with wide coverage of both LLINs and Indoor Residual Spraying (IRS) [5,34,56]. Killeen [46] indicated that An. arabiensis mosquitoes have adopted a behaviour that is instrumental in avoiding prolonged exposure to insecticides. These malaria vectors exit houses immediately after entry if a human host is sleeping under an LLIN [46], suggesting that the mosquito either enters another house or searches for a blood meal host outdoors. This particular behaviour has been reported in several studies [58-60].

Interestingly the ratios of An. arabiensis versus An. funestus in samples collected indoors versus outdoors were similar. This touches on the lack of bias of the sampling tool for indoor and outdoor collections. A possible explanation is that since outdoor collections were done on the outer walls of houses, we were dealing with the same mosquito subpopulations. The finding that no significant difference was found in density of An. arabiensis and An. funestus found indoors and outdoors is most likely explained by the few number of mosquitoes captured. It is statistically difficult to show differences in indoor and outdoor mosquito densities when general mosquito densities are low. It is unlikely that the low density of anopheline mosquitoes captured on Rusinga Island reflects a lack of efficacy of the MM-X trap as a sampling tool. The trap has been successfully used in sampling wild mosquitoes in sub-Saharan Africa [12,61-63]. More specifically, MM-X traps baited with the Mbita blend (as used in this study) have been shown to trap high numbers of Anopheles mosquitoes in other areas of western Kenya [12]. Also worth noting is that although there were few anophelines the numbers of culicine mosquitoes trapped in this study were high, indicating good sampling efficacy of the MM-X traps.

High densities of Culex mosquito species were recorded in this study. Other non-malaria vectors captured included Mansonia and Aedes spp. The presence of these mosquitoes indicates the potential transmission of arboviruses in Mbita sub-county. However, arboviral diseases have not been diagnosed in health facilities in Mbita sub-county, probably due to lack of diagnostic tools. We posit that the aforementioned non-malaria vectors are involved in nuisance biting in the area. One point is that targeting Anopheles species and leaving out culicine species may reduce acceptance of malaria control interventions among target communities because of the continuing biting menace from the unaffected Culex population [64-66].

It was interesting to note that the numbers and more or less the ratios, of malaria infected mosquitoes collected indoors and outdoors were equal. Malaria mosquitoes mainly bite at night when humans are asleep [47]. Thus, individuals who use indoor mosquito control tools are presumably protected from malaria infective bites. The front-line malaria vector control interventions specifically IRS and LLINs are effective indoors, which is a major space for insecticidal exposure [37]. These indoor interventions do not protect individuals who spend a significant part of their time outdoors and at night. This is the case of the capture fishing community of Rusinga Island where, in addition, the local malaria vectors prefer to blood-feed at night [4,47,67-69]. Huho and others [37] indicate that human behaviour is an important determinant in the place where malaria transmission occurs and it is strongly argued that outdoor transmission persists in areas with intense nocturnal outdoor activities [46,70]. The convergence between outdoor nocturnal fishing activities, preference for night-biting by local malaria vectors and the similarity in sporozoite rates between malaria mosquitoes collected indoors and outdoors exemplifies the vicious cycling of the disease in rural Africa.

Malaria mosquitoes on Rusinga Island were found to be low in density. This may be explained by climatic conditions, particularly fluctuating rainfall intensity experienced in recent years in the study area. The low adult mosquito density has previously been reported by Futami et al. [4] who compared densities of An. gambiae s.l. females in selected years from 1999 to 2010. Futami and others [4] reported a 95% decline in densities of An. gambiae s.l. which was attributed to an increase in bednet coverage. Evidence collected in the study reported herein implies that a small population of malaria vectors is responsible for malaria cases on Rusinga Island. Small populations of malaria vectors can sustain high malaria transmission in endemic areas [71]. Low densities of malaria vectors also imply that malaria vectors on Rusinga Island are highly efficient and maintain stable malaria transmission throughout the year. Elimination of malaria from Rusinga Island will require an increase in the use of interventions that target indoor transmission as well as novel interventions to control outdoor transmission.


The rather significant and unexpected contribution of P. malariae and P. ovale to the overall malaria prevalence on Rusinga Island underscores the epidemiological importance of these species in the big push towards eliminating malaria. Although current entomological interventions mainly target indoor environments, additional strategies should be invented to prevent outdoor transmission of malaria.



Confidence interval


circumsporozoite antibodies


Enzyme-linked immunosorbent assay


Health Demographic Surveillance System


Indoor residual spraying


Mosquito magnet-x trap


Polymerase chain reaction


Odds ratio


  1. 1.

    Noor AM, Gething PW, Alegana VA, Patil AP, Hay SI, Muchiri E, et al. The risks of malaria infection in Kenya in 2009. BMC Infect Dis. 2009;9:180.

  2. 2.

    DOMC. 2010 Kenya malaria indicator survey. Nairobi, Kenya: DOMC, KNBS and ICF Macro; 2011.

  3. 3.

    Bayoh MN, Mathias DK, Odiere MR, Mutuku FM, Kamau L, Gimnig JE, et al. Anopheles gambiae: historical population decline associated with regional distribution of insecticide-treated bed nets in western Nyanza province, Kenya. Malar J. 2010;9:62.

  4. 4.

    Futami K, Dida GO, Sonye GO, Lutiali PA, Mwania MS, Wagalla S, et al. Impacts of insecticide treated bed nets on anopheles gambiae s.l. Populations in Mbita district and Suba district, western Kenya. Parasit Vectors. 2014;7(1):63.

  5. 5.

    Bayoh MN, Walker ED, Kosgei J, Ombok M, Olang GB, Githeko AK, et al. Persistently high estimates of late night, indoor exposure to malaria vectors despite high coverage of insecticide treated nets. Parasit Vectors. 2014;7(1):380.

  6. 6.

    Minakawa N, Dida GO, Sonye GO, Futami K, Njenga SM. Malaria vectors in Lake Victoria and adjacent habitats in western Kenya. PLoS One. 2012;7(3), e32725.

  7. 7.

    Opiyo P, Mukabana WR, Kiche I, Mathenge E, Killeen GF, Fillinger U. An exploratory study of community factors relevant for participatory malaria control on Rusinga Island, Western Kenya. Malar J. 2007;6:48.

  8. 8.

    Mutero CM, Ouma JH, Agak BK, Wanderi JA, Copeland RS. Malaria prevalence and use of self-protection measures against mosquitoes in Suba District, Kenya. East Afr Med J. 1998;75(1):11–5.

  9. 9.

    Daniel WW. Biostatistics: a foundation for analysis in the health sciences. 7th ed. New York: John Wiley & Sons; 1999.

  10. 10.

    Naing L, Winn T, Rusli BN. Practical issues in calculating the sample size for prevalence studies. Arch Orofac Sci. 2006;1:9–14.

  11. 11.

    MOPHS, MMS: National Guidelines for the Diagnosis, Treatment and Prevention of Malaria in Kenya, Third edn: Ministry of Public Health and Sanitation; 2010.

  12. 12.

    Mukabana WR, Mweresa CK, Otieno B, Omusula P, Smallegange RC, van Loon JJ, et al. A novel synthetic odorant blend for trapping of malaria and other African mosquito species. J Chem Ecol. 2012;38(3):235–44.

  13. 13.

    Hill N, Lenglet A, Arnez AM, Carneiro I. Plant based insect repellent and insecticide treated bed nets to protect against malaria in areas of early evening biting vectors: double blind randomised placebo controlled clinical trial in the Bolivian Amazon. BMJ. 2007;335(7628):1023.

  14. 14.

    Gillies MT, Coetzee M. A supplement to the anophelinae of African South of the Sahara. South African Institute of Medical Research: Johannesburg; 1987.

  15. 15.

    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(4):520–9.

  16. 16.

    Wirtz RA, Duncan JF, Njelesani EK, Schneider I, Brown AE, Oster CN, et al. ELISA method for detecting Plasmodium falciparum circumsporozoite antibody. Bull World Health Organ. 1989;67(5):535–42.

  17. 17.

    O’Hara RB, Kotze DJ. Do not log-transform count data. Methods Ecol Evol. 2010;1:118–22.

  18. 18.

    Team RDC. R: A language and environment for statistical computing. R Foundation for Statistical Computing: Vienna, Austria; 2011.

  19. 19.

    Bell D, Wongsrichanalai C, Barnwell JW. Ensuring quality and access for malaria diagnosis: how can it be achieved? Nat Rev Microbiol. 2006;4:S7–20.

  20. 20.

    Manoti MC: Prevalence of Plasmodium parasites in malaria vectors and human hosts from western Kenya. MSc thesis. Egerton University, Department of Biological Sciences; 2013.

  21. 21.

    Gouagna LC, Okech BA, Kabiru EW, Killeen GF, Obare P, Ombonya S, et al. Infectivity of Plasmodium falciparum gametocytes in patients attending rural health centres in western Kenya. East Afr Med J. 2003;80(12):627–34.

  22. 22.

    Faye FBK, Konaté L, Rogier C, Trape JF. Plasmodium ovale in a highly malaria endemic area of Senegal. Trans R Soc Trop Med Hyg. 1998;92:522–5.

  23. 23.

    Faye FB, Spiegel A, Tall A. Diagnostic criteria and risk factors for Plasmodium ovale malaria. J Infect Dis. 2002;186:690–5.

  24. 24.

    Mueller I, Zimmerman PA, Reeder JC. Plasmodium malariae and Plasmodium ovale–the “bashful” malaria parasites. Trends Parasitol. 2007;23(6):278–83.

  25. 25.

    Collins WE, Jeffery GM. Plasmodium ovale: parasite and disease. Clin Microbiol Rev. 2005;18(3):570–81.

  26. 26.

    Munyekenye OG, Githeko AK, Zhou G, Mushinzimana E, Minakawa N, Yan G. Plasmodium falciparum spatial analysis, Western Kenya highlands. Emerg Infect Dis. 2005;11(10):1571–7.

  27. 27.

    Bashir IM, Otsyula N, Awinda G, Spring M, Schneider P, Waitumbi JN. Comparison of PfHRP-2/pLDH ELISA, qPCR and microscopy for the detection of Plasmodium events and prediction of sick visits during a malaria vaccine study. PLoS One. 2013;8(3), e56828.

  28. 28.

    Weckenbrock P: Livelihoods, Vulnerability and the Risk of Malaria on Rusinga Island/Kenya. Swiss Tropical Institute; 2005

  29. 29.

    Okell LC, Ghani AC, Lyons E, Drakeley CJ. Submicroscopic infection in Plasmodium falciparum-endemic populations: a systematic review and meta-analysis. J Infect Dis. 2009;200(10):1509–17.

  30. 30.

    Ouedraogo AL, Bousema T, de Vlas SJ, Cuzin-Ouattara N, Verhave JP, Drakeley C, et al. The plasticity of Plasmodium falciparum gametocytaemia in relation to age in Burkina Faso. Malar J. 2010;9:281.

  31. 31.

    Chirebvu E, Chimbari MJ, Ngwenya BN. Assessment of risk factors associated with malaria transmission in Tubu village, northern Botswana. Malar Res Treat. 2014;2014:403069.

  32. 32.

    Amuta E, Houmsou R, Wama E, Ameh M. Malarial infection among antenatal and maternity clinics attendees at the federal medical centre, Makurdi, Benue State, Nigeria. Infect Dis Rep. 2014;6(1):5050.

  33. 33.

    Pulford J, Hetzel MW, Bryant M, Siba PM, Mueller I. Reported reasons for not using a mosquito net when one is available: a review of the published literature. Malar J. 2011;10:83.

  34. 34.

    Russell TL, Govella NJ, Azizi S, Drakeley CJ, Kachur SP, Killeen GF. Increased proportions of outdoor feeding among residual malaria vector populations following increased use of insecticide-treated nets in rural Tanzania. Malar J. 2011;10:80.

  35. 35.

    Govella NJ, Okumu FO, Killeen GF. Insecticide-treated nets can reduce malaria transmission by mosquitoes which feed outdoors. Am J Trop Med Hyg. 2010;82(3):415–9.

  36. 36.

    Reddy MR, Overgaard HJ, Abaga S, Reddy VP, Caccone A, Kiszewski AE, et al. Outdoor host seeking behaviour of Anopheles gambiae mosquitoes following initiation of malaria vector control on Bioko Island, Equatorial Guinea. Malar J. 2011;10:184.

  37. 37.

    Huho B, Briet O, Seyoum A, Sikaala C, Bayoh N, Gimnig J, et al. Consistently high estimates for the proportion of human exposure to malaria vector populations occurring indoors in rural Africa. Int J Epidemiol. 2013;42(1):235–47.

  38. 38.

    Fullman N, Burstein R, Lim SS, Medlin C, Gakidou E. Nets, spray or both? The effectiveness of insecticide-treated nets and indoor residual spraying in reducing malaria morbidity and child mortality in sub-Saharan Africa. Malaria J. 2013;12:62.

  39. 39.

    Bekele D, Belyhun Y, Petros B, Deressa W. Assessment of the effect of insecticide-treated nets and indoor residual spraying for malaria control in three rural Kebeles of Adami Tulu District, South Central Ethiopia. Malar J. 2012;11:127.

  40. 40.

    Okumu FO, Moore SJ. Combining indoor residual spraying and insecticide-treated nets for malaria control in Africa: a review of possible outcomes and an outline of suggestions for the future. Malar J. 2011;10:208.

  41. 41.

    Lindblade KA. Commentary: does a mosquito bite when no one is around to hear it? Int J Epidemiol. 2013;42(1):247–9.

  42. 42.

    Govella NJ, Ferguson H. Why Use of interventions targeting outdoor biting mosquitoes will be necessary to achieve malaria elimination. Front Physiol. 2012;3:199.

  43. 43.

    mal ERACGoVC. A research agenda for malaria eradication: vector control. PLoS Med. 2011;8(1):e1000401.

  44. 44.

    Ferguson HM, Dornhaus A, Beeche A, Borgemeister C, Gottlieb M, Mulla MS, et al. Ecology: a prerequisite for malaria elimination and eradication. PLoS Med. 2010;7(8), e1000303.

  45. 45.

    Takken W, Knols BG. Malaria vector control: current and future strategies. Trends Parasitol. 2009;25(3):101–4.

  46. 46.

    Killeen GF. Characterizing, controlling and eliminating residual malaria transmission. Malar J. 2014;13(1):330.

  47. 47.

    White GB. Anopheles gambiae complex and disease transmission in Africa. Trans R Soc Trop Med Hyg. 1974;68(4):278–301.

  48. 48.

    Muriu SM, Muturi EJ, Shililu JI, Mbogo CM, Mwangangi JM, Jacob BG, et al. Host choice and multiple blood feeding behaviour of malaria vectors and other anophelines in Mwea rice scheme, Kenya. Malar J. 2008;7:43.

  49. 49.

    Mwangangi JM, Muturi EJ, Muriu SM, Nzovu J, Midega JT, Mbogo C. The role of Anopheles arabiensis and Anopheles coustani in indoor and outdoor malaria transmission in Taveta District, Kenya. Parasit Vectors. 2013;6:114.

  50. 50.

    Tirados I, Costantini C, Gibson G, Torr SJ. Blood-feeding behaviour of the malarial mosquito Anopheles arabiensis: implications for vector control. Med Vet Entomol. 2006;20(4):425–37.

  51. 51.

    Kerah-Hinzoumbe C, Peka M, Antonio-Nkondjio C, Donan-Gouni I, Awono-Ambene P, Same-Ekobo A, et al. Malaria vectors and transmission dynamics in Goulmoun, a rural city in south-western Chad. BMC Infect Dis. 2009;9:71.

  52. 52.

    Muturi EJ, Muriu S, Shililu J, Mwangangi J, Jacob BG, Mbogo C, et al. Effect of rice cultivation on malaria transmission in central Kenya. Am J Trop Med Hyg. 2008;78(2):270–5.

  53. 53.

    Mbogo CN, Kabiru EW, Muiruri SK, Nzovu JM, Ouma JH, Githure JI, et al. Bloodfeeding behavior of Anopheles gambiae sl and Anopheles funestus in Kilifi District, Kenya. J Am Mosq Control Assoc. 1993;9:225–7.

  54. 54.

    Githeko AK, Service MW, Mbogo CM, Atieli FK, Juma FO. Origin of blood meals in indoor and outdoor resting malaria vectors in western Kenya. Acta Trop Med Int Health. 1994;58:307–16.

  55. 55.

    Mutuku FM, King CH, Mungai P, Mbogo C, Mwangangi J, Muchiri EM, et al. Impact of insecticide-treated bed nets on malaria transmission indices on the south coast of Kenya. Malar J. 2011;10:356.

  56. 56.

    Mwangangi JM, Mbogo CM, Orindi BO, Muturi EJ, Midega JT, Nzovu J, et al. Shifts in malaria vector species composition and transmission dynamics along the Kenyan coast over the past 20 years. Malar J. 2013;12:13.

  57. 57.

    Russell TL, Lwetoijera DW, Maliti D, Chipwaza B, Kihonda J, Charlwood JD, et al. Impact of promoting longer-lasting insecticide treatment of bed nets upon malaria transmission in a rural Tanzanian setting with pre-existing high coverage of untreated nets. Malar J. 2010;9:187.

  58. 58.

    Kitau J, Oxborough RM, Tungu PK, Matowo J, Malima RC, Magesa SM, et al. Species shifts in the Anopheles gambiae complex: do LLINs successfully control Anopheles arabiensis? PLoS One. 2012;7(3), e31481.

  59. 59.

    Okumu FO, Kiware SS, Moore SJ, Killeen GF. Mathematical evaluation of community level impact of combining bed nets and indoor residual spraying upon malaria transmission in areas where the main vectors are Anopheles arabiensis mosquitoes. Parasit Vectors. 2013;6:17.

  60. 60.

    Okumu FO, Mbeyela E, Lingamba G, Moore J, Ntamatungiro AJ, Kavishe DR, et al. Comparative field evaluation of combinations of long-lasting insecticide treated nets and indoor residual spraying, relative to either method alone, for malaria prevention in an area where the main vector is Anopheles arabiensis. Parasit Vectors. 2013;6:46.

  61. 61.

    Okumu FO, Madumla EP, John AN, Lwetoijera DW, Sumaye RD. Attracting, trapping and killing disease-transmitting mosquitoes using odor-baited stations - The Ifakara Odor-Baited Stations. Parasit Vectors. 2010;3:12.

  62. 62.

    Qiu YT, Smallegange RC, Braak CJF, Spitzen J, Loon J, Jawara M, et al. Attractiveness of MM-X traps baited with human or synthetic odor to mosquitoes (diptera: culicidae) in the Gambia. J Med Entomol. 2007;44(6):970–83.

  63. 63.

    Jawara M, Awolola TS, Pinder M, Jeffries D, Smallegange RC, Takken W, et al. Field testing of different chemical combinations as odour baits for trapping wild mosquitoes in The Gambia. PLoS One. 2011;6(5), e19676.

  64. 64.

    Stephens C, Masamu ET, Kiama MG, Keto AJ, Kinenekejo M, Ichimori K, et al. Knowledge of mosquitos in relation to public and domestic control activities in the cities of Dar es Salaam and Tanga. Bull World Health Organ. 1995;73(1):97–104.

  65. 65.

    Mazigo HD, Obasy E, Mauka W, Manyiri P, Zinga M, Kweka EJ, et al. Knowledge, attitudes, and practices about malaria and its control in rural Northwest Tanzania. Malar Res Treat. 2010;2010:794261.

  66. 66.

    Sangoro O, Kelly AH, Mtali S, Moore SJ. Feasibility of repellent use in a context of increasing outdoor transmission: a qualitative study in rural Tanzania. Malar J. 2014;13:347.

  67. 67.

    Minakawa N, Seda P, Yan G. Influence of host and larval habitat distribution on the abundance of African malaria vectors in western Kenya. Am J Trop Med Hyg. 2002;67(1):32–8.

  68. 68.

    Shililu JI, Mbogo CM, Mutero CM, Gunter JT, Swalm C, Regens JL, et al. Spatial distribution of Anopheles gambiae and Anopheles funestus and malaria transmission in Suba District, Western Kenya. Insect Sci Appl. 2003;23:187–96.

  69. 69.

    Mathenge EM, Gimnig JE, Kolczak M, Ombok M, Irungu LW, Hawley WA. Effect of permethrin-impregnated nets on exiting behavior, blood feeding success, and time of feeding of malaria mosquitoes (Diptera: Culicidae) in western Kenya. J Med Entomol. 2001;38(4):531–6.

  70. 70.

    Durnez L, Coosemans M: Residual transmission of malaria: an old issue for new approaches: Intech; 2013

  71. 71.

    Trung HD, Van Bortel W, Sochantha T, Keokenchanh K, Quang NT, Cong LD, et al. Malaria transmission and major malaria vectors in different geographical areas of Southeast Asia. Trop Med Int Health. 2004;9(2):230–7.

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We thank the residents of Rusinga Island for participating in the surveys. The authors wish to thank the International Development Research Centre (IDRC) for funding this study (Grant no. 104263–006). EAO was supported by the African Regional Postgraduate Programme in Insect Science (ARPPIS) through a fellowship from the German Academic Exchange Service (DAAD) administered by the International Centre of Insect Physiology and Ecology, Kenya (icipe). We wish to thank Caroline Manoti Moseti and Ibrahim Kiche for supervising and co-ordinating malaria survey activities. We are grateful to Michael Otieno, Byronne Omondi, Ronald Ngala Odera, Louryne Matiku, Leonida Ang’iro, Kennedy Onyango, Maurine Odira, David Otieno, Luphine Odongo, Maurine Odhiambo, and Maureen Nyaura for helping to collect the malaria survey data.

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Correspondence to Wolfgang R Mukabana.

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The authors declare that they have no competing interests.

Authors’ contributions

EAO, LWI and WRM conceived and designed the experiments. LO was instrumental in the acquisition of data. EAO and WRM analysed the data and wrote the manuscript. All authors read and approved the final manuscript.

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Olanga, E.A., Okombo, L., Irungu, L.W. et al. Parasites and vectors of malaria on Rusinga Island, Western Kenya. Parasites Vectors 8, 250 (2015).

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  • Malaria
  • Malaria prevalence
  • Plasmodium falciparum
  • P. malariae
  • P. ovale
  • Malaria
  • Anopheles
  • Culex
  • Mansonia
  • Indoor transmission
  • Outdoor transmission
  • Capture fishing
  • Rusinga Island
  • Kenya


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