- Open Access
The effect of screening doors and windows on indoor density of Anopheles arabiensis in south-west Ethiopia: a randomized trial
© Massebo and Lindtjørn; licensee BioMed Central Ltd. 2013
- Received: 2 May 2013
- Accepted: 10 September 2013
- Published: 12 September 2013
Screening of houses might have impact on density of indoor host-seeking Anopheles mosquitoes. A randomized trial of screening windows and doors with metal mesh, and closing openings on eves and walls by mud was conducted to assess if reduce indoor densities of biting mosquitoes.
Mosquitoes were collected in forty houses using Centers for Diseases Control and Prevention (CDC) light traps biweekly in March and April 2011. A randomization of houses into control and intervention groups was done based on the baseline data. Windows and doors of 20 houses were screened by metal mesh, and openings on the walls and eves closed by mud and the rest 20 houses were used as control group. Mosquitoes were collected biweekly in October and November 2011 from both control and intervention houses. A Generalized Estimating Equations (GEE) with a negative binomial error distribution was used to account for over dispersion of Anopheles arabiensis and culicine counts and repeated catches made in the same house.
Screening doors and windows, and closing openings on eves and wall by mud reduced the overall indoor densities of An. arabiensis by 40%. The effect of screenings pronounced on unfed An. arabiensis by resulting 42% reduction in houses with interventions. The total costs for screening windows and doors, and to close openings on the eves and walls by mud was 7.34 USD per house.
Screening houses reduced indoor density of An. arabiensis, and it was cheap and can easily incorporated into malaria vector strategies by local communities, but improving doors and windows fitness for screening should be considered during house construction to increase the efficacy of screenings.
- Anopheles arabiensis
- Screening doors and windows
- Indoor density
- Metal mesh
Malaria vectors control depends mainly on personal protection, environmental management and use of insecticides for indoor residual spraying (IRS) and mosquito net treatment. The efficacy of long-lasting insecticidal nets (LLITNs) and IRS was reduced in an area where malaria vectors were resistant to insecticide in Benin. In Ethiopia, resistance to pyrethroid insecticides by Anopheles arabiensis is increasing[2–4] and, hence, integrated malaria vectors control approach is needed to reduce the challenge from resistance on malaria transmission.
Mosquito-proofing houses have a historical success against malaria vectors[6, 7]. In Missouri, USA, screened houses afforded a considerable degree of protection against malaria vectors and the incidence of malaria was higher in houses without screening where the population was most accessible for biting mosquitoes. Similarly, in Tennessee River area in USA a substantial reduction of the incidence of malaria was obtained by improving rural houses. Recently, modification of houses reduced houses entry of Anopheles gambiae by 78% to 80% in The Gambia. Forty three percent reduction of house entry of An. gambiae was reported by closing eves of houses. Screening houses using mosquito proofing materials significantly reduced indoor density of host seeking An. gambiae[6, 11], and it provides equal protection for all occupants in the houses against bites of malaria vectors. Anopheles arabiensis predominantly bites humans indoors in study site, hence there is a need for additional malaria vector control to reduce house entry and minimize indoors human-vector contact, and divert them to non-human hosts available outdoors. The objective of this study was to assess whether screening windows and doors by metal mesh, and closing openings on eves and walls by mud would reduce indoor densities of An. arabiensis in south-west Ethiopia.
A randomized control trial was conducted to assess the efficacy of screening windows and doors with metal mesh, and closing openings on eves and walls by mud on indoor density of An. arabiensis. The study was done in Chano, a village 15 km north of Arba Minch town in southwest Ethiopia. The nearest sub-village to Lake Abaya (1,350 to 1,850 m from the shore of Lake Abaya, the major larval breeding sites) was purposely selected for screening trial because both epidemiological and entomological[4, 14] findings have shown higher risk malaria exposure in this sub-village than other sub-villages. The detail description of the study area has been reported elsewhere[4, 14].
Forty houses with thatched roof, similar size, found between 1,350 -1,570 m from the main mosquito breeding sites (shore of Lake Abaya), with the number of occupants greater or equal to four and with same number of doors and windows were included for the trial.
Pre-screening mosquito collections
Mosquitoes were collected from all the 40 houses every second week in four consecutive nights per week (10 CDC light traps per night) in April and May 2011. A total of 160 Centers for Diseases Control and Prevention (CDC) light trap nights were conducted to generate the baseline data. Anophelines were identified using a morphological key and classified into unfed, freshly fed, half gravid and gravid based on abdominal condition. Culicines were counted and discarded.
The baseline data of the mean number of An. arabiensis per CDC light trap night (April and May 2011)
Pre-control houses (n = 20)
Pre-intervention houses (n = 20)
N (no. of mosquitoes)
N (no. of mosquitoes)
8.5 (2.3, 14.7)
7.8 (4.8, 10.8)
7.2 (4.1, 10.4)
7.9 (4.4, 11.5)
1.3 (0.7, 1.9)
1.2 (0.7, 1.7)
3 (1.8, 4.2)
3.3 (2, 4.7)
20.3 (12.8, 27.8)
Post-screening mosquito collections
The 40 houses were sampled every second week in October and November 2011 by taking five houses from intervention group and five houses from control group per night for four consecutive nights per week. Anophelines were identified using a morphological key and classified into unfed, freshly fed, half gravid and gravid based on abdominal condition. Culicines were counted and discarded.
The outcome variable of this study was indoor densities of An. arabiensis collected per CDC light trap per night. Mosquito collectors were not masked because CDC light traps are not depending on human skills.
Mosquito data within household was described by mean number of An. arabiensis per CDC light trap per night. A Generalized Estimating Equations (GEE) with a negative binomial error distribution was used to account for over dispersion of An. arabiensis and culicine counts. A first-order autoregressive correlation structure was considered to account a serial correlation between repeated catches made in the same house. The GEE was fitted separately to counts of different abdominal conditions of An. arabiensis and overall culicine to determine the protective effect of screenings against house entry of the species. The mean’s ratio of mosquitoes between screened and control houses were used to determine the percentage reduction of house entry. Non-parametric correlation was used to see the house entry patterns of An. arabiensis in pre-intervention and post-intervention months. All houses were included in analysis because no damaged metal mesh and malfunctioned CDC light traps were observed. The statistical significance of screening effect was tested by P-value obtained from GEEs at 0.05 level. IBM SPSS version 20 (SPSS Inc, Chicago, USA) was used for data entry and analysis.
A verbal consent was obtained from the household head and they provided with insecticide untreated bed nets.
Mosquito abundance and species composition
A total of 4,778 anophelines and 3,111 culicines were collected during the study period. Anopheles arabiensis was the predominant (n = 4249, 89%) species followed by Anopheles marshalli (n = 246, 5.1%) and Anopheles pharoensis (n = 178, 3.7%). Anopheles demeilloni, Anopheles dancalicus, Anopheles cinctus, Anopheles culicifacies, Anopheles funestus, Anopheles obscures, Anopheles tenebrosus, Anopheles parensis, Anopheles rufipes, Anopheles ziemanni, Anopheles garnhami and Anopheles salbaii accounted only 2.2% (n = 105).
House entry patterns of Anopheles arabiensis at different months
House entry of An. arabiensis followed similar patterns before and during intervention. Households with a maximum number of An. arabiensis in the months prior to intervention received higher number during intervention both in control houses (r = 0.72, p <0.001) and houses that were subsequently screenings (r = 0.56, p = 0.01).
The efficacy of intervention on indoor density of An. arabiensis
The efficacy of doors and windows screening on indoor host seeking densities of An. arabiensis (October and November 2011)
# (Wald 95%CI)
2.4 (2.2, 2.7)
1.4 (1.1, 1.9)
2.8 (2.3, 3.6)
1.8 (1.5, 2.1)
0.15 (0.1, 0.4)
0.13 (0.1, 0.3)
2.5 (1.9, 3.5)
1.5 (1.2, 1.9)
7.9 (6.5, 10.1)
4.8 (3.9, 6.2)
Costs for intervention
Cost per household
Cost for metal mesh
1.44 USD * 2.5 m = 3.6 USD
Cost for screening including nails and wooden materials
Closing openings with mud
Total cost per house
The results of this randomized trial show that screening doors and windows, and closing openings on walls and eves by mud reduced the overall indoor densities of An. arabiensis by 40%. Although screening intervention reduced indoor density of An. arabiensis at all abdominal stages, the reduction was substantially higher against unfed An. arabiensis. The intervention was based on locally bought materials, and was affordable.
The houses we assessed were grass thatched, and doors and windows were not well-suited for screenings. The incompatible of doors for screening might reduce the efficacy in such house types. The roofs of grass thatched local houses prevent opening of screened doors outward; consequently, the screened doors were not permanently fixed and people might not used them constantly during the nights before collection.
A house screening study from The Gambia resulted in 43% reduction of house entry of An. gambiae which is comparable to the current study. Although the incidence of malaria infection was not assessed, the previous studies have shown less malaria cases in screened houses than in controls. Moreover, the association between the incidence of malaria and the accessibility of a population to mosquitoes was observed with the highest incidence in the population most accessible for mosquito bites. In The Gambia, screening doors, windows and eves resulted in 59% reduction of indoors density of An. gambiae, and reduced the prevalence of anaemia. Screening houses by plastic insect-screen resulted 80% protection from indoor bites of An. gambiae in The Gambia.
The likely explanation for moderate efficacy the current intervention is that people may not use screened doors in the nights before collection because the screened doors were not permanently fixed as windows. Moreover, An. arabiensis could enter houses when the people open the doors during earlier hours of the night. The small gaps left in the door and windows could also contribute for the moderate reduction of mosquitoes in the intervention houses. Maximum reduction in number of An. arabiensis might be achieved if the screened doors were constantly used by home owner’s, and the doors were compatible for screening. The likely reason for the overall lower number of mosquitoes sampled during intervention (October/November 2011) compared to the pre-intervention period (April/May 2011) was presumably due to the seasonal variation of the area. Study from the same area shows the highest density of mosquitoes in April and May; the months with the highest rainfall than the October and November; the months with short and small rains[4, 14].
The intervention was cheap, and simple to implement and hence, it can be incorporated into an integrated vector management strategy, and combined with IRS and LLITNs. The cost for screening doors and windows and closing openings on eves and walls (7.3 USD per house) was lower than that was used for fully screening houses (9.98 USD per person) and for screening ceilings (8.69 USD per person) in The Gambia. However, improving doors and windows fitness for screening should be considered during house construction to increase the efficacy of screenings.
We received financial support from Centre for International Health, University of Bergen in Norway. Arba Minch University provided transport for fieldwork. Finally, the authors would like to thank the residents of Chano for their voluntariness and allowing us to collect mosquitoes.
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