Skip to main content


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

Bacterial larvicides used for malaria vector control in sub-Saharan Africa: review of their effectiveness and operational feasibility


Several trials and reviews have outlined the potential role of larviciding for malaria control in sub-Saharan Africa (SSA) to supplement the core indoor insecticide-based interventions. It has been argued that widespread use of long-lasting insecticide-treated nets (LLINs) and indoor residual spraying (IRS) interventions in many parts of Africa result in many new areas with low and focal malaria transmission that can be targeted with larvicides. As some countries in SSA are making good progress in malaria control, larval source management, particularly with bacterial larvicides, could be included in the list of viable options to maintain the gains achieved while paving the way to malaria elimination. We conducted a review of published literature that investigated the application of bacterial larvicides, Bacillus thuringiensis var. israelensis (Bti) and/or Bacillus sphaericus (Bs) for malaria vector control in SSA. Data for the review were identified through PubMed, the extensive files of the authors and reference lists of relevant articles retrieved. A total of 56 relevant studies were identified and included in the review. The findings indicated that, at low application rates, bacterial larvicide products based on Bti and/or Bs were effective in controlling malaria vectors. The larvicide interventions were found to be feasible, accepted by the general community, safe to the non-target organisms and the costs compared fairly well with those of other vector control measures practiced in SSA. Our review suggests that larviciding should gain more ground as a tool for integrated malaria vector control due to the decline in malaria which creates more appropriate conditions for the intervention and to the recognition of limitations of insecticide-based vector control tools. The advancement of new technology for mapping landscapes and environments could moreover facilitate identification and targeting of the numerous larval habitats preferred by the African malaria vectors. To build sustainable anti-larval measures in SSA, there is a great need to build capacity in relevant specialties and develop organizational structures for governance and management of larval source management programmes.


Malaria mosquito vector control in sub-Saharan Africa (SSA) relies on the use of insecticide-treated bednets and/or indoor residual spraying with insecticide. These interventions have been shown to be effective and the recent decline in malaria prevalence in many parts of Africa has been attributed in part to their wide-scale use for mosquito control [1]. However, emerging and widespread insecticide resistance threatens the success made with these tools [2,3,4]. In addition, insecticide-based interventions have been reported to be the major drive towards the observed behavioral adaptation by malaria vectors [5, 6]. To maintain the gains achieved in malaria control over the last decade, it is crucial to implement measures that will mitigate insecticide resistance and behavioral adaptation by malaria vectors [7].

Mosquito larval control interventions have proven records of lowering malaria transmission and even eradication of malaria mosquitoes [8]. It has been shown that unlike adult mosquitoes, larvae cannot change their behavior to avoid a control intervention targeted at larval habitats [9]. Moreover, a larval control strategy also serves to extend the useful life of insecticides against adult mosquitoes by reducing the size of the population being selected for resistance and the strategy is equally effective in controlling both indoor and outdoor biting mosquitoes. Integrating larval source reduction with adult mosquito control interventions like insecticide-treated bednets has therefore been considered to be a highly effective strategy to control malaria [10]. Larviciding with chemical agents was historically an important component of malaria vector control [8, 11]. However, due to significant adverse effects to other non-target species, chemical larvicides have received less attention in the past decades. Instead, preference has been shifted to the use of microbial larvicides Bacillus thuringiensis var. israelensis (Bti) and Bacillus sphaericus (Bs), which selectively kill mosquito larvae with negligible effect to non-target organisms [12].

Despite the proven role of larval control and the historical success of such interventions in malaria control, larviciding has remained largely neglected for malaria control in SSA [13]. The World Health Organization (WHO) recommends larviciding to be used in moderate to low transmission settings as a supplement to core interventions (long-lasting insecticide-treated nets [LLINs] and indoor residual spraying [IRS]) in settings where larval habitats are few, fixed and findable, such as urban areas, desert fringes, high altitudes and rural areas with high population densities [14]. Of particular relevance to this recommendation, it has been argued that intensification of LLINs and IRS interventions in many parts of Africa will result in many new areas with low and focal malaria transmission [14]. Moreover, the WHO calls for a search for viable supplementary strategies for managing vector-borne diseases and reducing reliance on chemical insecticides [15]. Likewise, it has been argued that the current malaria control interventions constitute a necessary but insufficient set of measures to ensure a sustainable control and thus larviciding could play an important role when other vector control interventions have achieved their maximum practical impact [14].

In the past decades, there has been growing evidence suggesting that larval source management by applying bacterial larvicides Bti and Bs has the potential to lower the density of mosquito vectors, as previously summarized [12, 16]. The efficacy and safety of Bti and Bs have been reported to be high making them ideal for inclusion in the integrated vector management (IVM) programmes for mosquito-borne disease control [12]. However, control efficacy of Bti and Bs has also been reported to vary greatly, mainly due to factors related to target mosquitoes (species of mosquito, their respective feeding strategies, age and density of larvae), larval habitat conditions (temperature, solar radiation, depth of water, turbidity, organic contents and presence of vegetation) and larvicide properties (application rates, toxin contents, type of carrier, how effective the material reach the target, settling rate, means of application and frequent of treatment) [17]. Due to this heterogeneity of their activity, the general consensus suggests that a larviciding strategy can be appropriate and useful for malaria control in some specific settings, whereas in other settings such efforts are unlikely to be cost-effective [14]. To be effective, application of Bti and Bs, like any other larviciding intervention should be guided by adequate knowledge of the prevailing mosquito vectors, their ecology and the properties of the bacterial larvicide used [12, 16].

As some countries in sub-Saharan Africa are making good progress in malaria control, larviciding, particularly with bacterial larvicides, needs to be included in the list of viable options to intensify elimination campaigns. Thus, information on the effectiveness and feasibility of applying bacterial larvicides for mosquito control is important for designing and implementing larvae control operations to supplement interventions targeting adult mosquitoes. Here, we reviewed the available literature on the use of bacterial larvicides for malaria vector control in SSA in order to provide an informed background for designing and implementing larvae control using bacterial larvicides. The present review was designed to complement available literature on larval source management by reviewing only studies on bacterial larvicides used for malaria vector control and limited its scope to studies conducted in SSA.


Search strategy and article selection

Articles for this review were identified through PubMed, as well as from the extensive files of the authors and the reference lists of relevant articles. The PubMed search was conducted by using the following search terms: “microbial larvicide” or “Bacillus thuringiensis israelensis” or “Bacillus sphaericus”. The PubMed search resulted in 1112 articles, of which 1077 were excluded (after screening titles and abstracts) because they did not address the effect of bacterial larvicides on malaria vectors or malaria transmission, or the studies were not from the SSA region. Moreover, a total of 21 relevant articles were obtained from the files of the authors and the reference lists of identified relevant articles. Thus, a total of 56 articles were considered for full-text reading and used for this review. Operational studies with more than one published article that reported different outcome measure of interest were all included. For articles that reported the impact of bacterial larvicides on combined malaria and non-malaria vectors or of bacterial larvicides combined with other control methods, only data on malaria vectors and on control effects attributable to microbial larvicides were considered. Data from the selected articles were extracted onto a data extraction form created in Microsoft Excel to easily assess and compare information on key study aspects such as bacterial larvicide products, experimental designs, surveyed larval habitats, the feasibility of the application, the impact of larvicides, effect size, intervention costs, safety and acceptability. Due to the wide range and heterogeneity of the study designs, larvicide products tested, application rates and effect size reported, data for the laboratory, semi-field and field studies are presented separately in the results section. Studies conducted in laboratory settings using laboratory colonized malaria vectors were classified as “laboratory studies” whereas those conducted in simulated field conditions (artificial larval habitats set in open fields) with field collected or laboratory reared mosquitoes were categorized as “semi-field studies”. “Field studies” included trials against natural vector populations in natural breeding habitats of malaria vectors.


Description of the reviewed studies

A total of 56 studies were reviewed. More than half (n = 32, 57.1%) were conducted in three countries, namely Kenya (n = 11, 19.6%), Tanzania (n = 11, 19.6%) and Burkina Faso (n = 10, 17.9%) (Fig. 1). The articles were published from 1987 to 2019 and represented over 3 decades of testing of bacterial larvicides in SSA. Of the 56 reviewed articles, 8 (14.3%) had non-interventional components, dealing mainly with community acceptability and/or cost analysis of larvicide interventions. Of the remaining 48 articles, 3, 3 and 32 reported studies that evaluated the activity of larvicides in laboratory, semi-field and field settings only, respectively, whereas 10 articles reported a mixture of these types of studies (Table 1).

Fig. 1

Number of reviewed publications by country. For publications involving multi-country studies, each country was counted towards the total, e.g. Kenya and Tanzania [94] and Botswana and Zimbabwe [79]. Note: Zaire: now The Democratic Republic of the Congo

Table 1 Overview of the reviewed articles reporting on bacterial larvicides tested in sub-Saharan Africa, and on the type of studies they describe

Of the 39 field studies that involved larvicide application, 24 (61.5%) were conducted in rural settings, whereas 15 (38.5%) were conducted in urban or peri-urban settings (Table 2). Four of these (10.3%) reported on two large-scale larvae control operations conducted in western Kenya and Dar es Salaam, Tanzania. A variety of Anopheles larval habitats were reported in the reviewed articles and these differed considerably within the trial sites. Application of bacterial larvicides in the field studies targeted An. gambiae (s.l.) and An. funestus, the major malaria vectors in SSA (Table 2).

Table 2 Reviewed field studies on bacterial larvicides tested in sub-Saharan Africa, including information on study areas, survey periods, larval habitats and their associated malaria vectors

Bacterial larvicide products evaluated

An overview of the evaluated bacterial larvicide products in the reviewed studies is shown in Table 3. Five studies did not specify Bti and/or Bs products evaluated [18,19,20,21,22]. Of the reviewed field studies that reported larvicide application, 13 (33.3%) tested Bti and Bs concurrently (in alternating fashion or in separate larval habitats in the same study site) whereas 13 (33.3%) and 7 (17.9%), respectively, tested only Bti or Bs. Six (15.4%) studies tested larvicide products that were formulated with a combination of both Bti and Bs toxins, namely FourStar® briquettes, VectoMax® corn granules (CG) and Culinexcombi® tablets. Water-dispersible granules (WDG) and CG formulations of the commercial strains of Bti were the majority of larvicide products tested in the reviewed studies, reported by 19 and 11 studies, respectively. In the reviewed studies, application rates for the bacterial larvicide products varied considerably with a strain of the bacterium (Bti or Bs), product formulation and inherent potency of the product as measured by their toxicity in international toxic units per milligram (ITU/mg).

Table 3 Commercial bacterial larvicide products based on Bacillus thuringiensis var. israelensis and Bacillus sphaericus applied in the reviewed studies from sub-Saharan Africa

The activity of Bti and Bs in laboratory settings

Ten (17.9%) of the reviewed articles presented the findings of the efficacy of Bti and Bs on An. gambiae (s.l.) and An. funestus in laboratory settings (Table 4). The bio-potency of Bti and Bs based products varied between 1500–10,000 Bti ITU/mg and 650–1600 Bs ITU/mg, respectively. In most cases, laboratory experiments were conducted for 24 and 48 h for Bti and Bs, respectively. For Bti, the lethal concentration value that caused 50 and 90/95% mortality of An. gambiae (s.l.) larvae (LC50 and LC90/95) ranged between 0.006–0.662 mg/l and 0.132–1.743 mg/l, respectively. For Bs, the LC50 and LC90/95 values for the same mosquito species ranged between 0.002–0.342 mg/l and 0.018–1.807 mg/l, respectively. For An. funestus, LC50 and LC95 values after 48 h of exposure to Bs were 1.0 mg/l and 6.0 mg/l, respectively. For studies that reported the potency in spores per milliliter, LC50 and LC90 values after 24 h of exposure to Bti in different malaria vectors are presented in Table 4.

Table 4 Laboratory trials using Bacillus thuringiensis var. israelensis and Bacillus sphaericus against malaria vectors in sub-Saharan Africa

The activity of Bti and Bs in semi-field conditions

A total of 12 (21.4%) studies reported experiments with Bti and Bs conducted in semi-field conditions to establish their effectiveness and duration of control (Table 5). The larval habitats treated contained Anopheles gambiae (s.l.), a mixture of Anopheles and culicine species, An. arabiensis and An. gambiae (s.s.) in 5, 4, 2 and 1 of these studies, respectively. Larvicide application rates varied considerably among the studies with products based on Bti having relatively lower application rates compared to Bs. With respect to larvicide formulation, application rates for water-dispersible granules (WDG) were lower than corn granules (CG) or granules (G) due to their inherently high potency. The studies reported appreciable larval reductions in the treated larval habitats for 2 to 14 days post-treatment. Of the tested products, the highest larval reductions and the most prolonged effect was seen in studies that tested VectoMax® CG, with 98–100% reduction in late larval instars for 2 weeks. On the other hand, the pupal reductions in treated larval habitats varied between 64–100%, with residual effects ranging from 7 days to 3 months. A very high residual effect in pupal control was observed in a study that tested a slow release formulation of bacterial larvicide (FourStar®) that combined both Bti and Bs (Table 5).

Table 5 Semi-field trials using commercial products of Bacillus thuringiensis var. israelensis and Bacillus sphaericus against malaria vectors in sub-Saharan Africa

The activity of Bti and Bs on immature and adult mosquitoes in field conditions

A total of 39 (69.6%) reviewed studies evaluated the activity of Bti and/or Bs in field conditions (Table 2). Of these, seven commenced the evaluations of Bti and/or Bs from the laboratory and/or semi-field conditions. Five bacterial larvicide products evaluated in the semi-field trials were also tested in the field conditions (Table 6). WDG and CG formulations of Bti and Bs were the majority of the evaluated products, with VectoBac® WDG tested in 14 of the field studies. Reported larval reductions varied considerably with the test site, larvicide product applied and application rate. Overall, larval reductions ranging from 47 to 100% were recorded, with the residual effect lasting for 2 to 28 days following single or repeated applications of the larvicide. Substantial pupal reductions were also reported, with the most marked impact observed with FourStar®, a slow release bacterial larvicide formulation (Table 6). The least larval reductions were recorded with Bactimos® and VectoBac® wettable powder (WP) when applied once in rain pools. In the reviewed articles, it was not possible to analyze the difference in susceptibility between An. gambiae (s.l.) and An. funestus or variation in different ecological settings due to heterogeneity in testing conditions, products used and pooling of mosquito species data in some studies. However, the reviewed laboratory studies indicated that An. gambiae (s.l.) were more sensitive to Bti and Bs than An. funestus (Table 4). On the other hand, a total of 14 (35.9%) reviewed field studies reported the activity of Bti and/or Bs in adult mosquitoes and/or malaria transmission. Different levels of reductions in adult mosquitoes and/or malaria transmission were reported with single or repeated applications of Bti and/or Bs (Table 7).

Table 6 Field trials of commercial products of Bacillus thuringiensis var. israelensis and Bacillus sphaericus against immature stages of malaria vectors in sub-Saharan Africa
Table 7 Field trials of commercial products of Bacillus thuringiensis var. israelensis and Bacillus sphaericus against adult malaria vectors and the effect on malaria transmission in sub-Saharan Africa

Safety, cost effectiveness and acceptability

Five of the reviewed studies evaluated the safety of Bti and/or Bs to non-target organism co-habiting with mosquito larvae in natural larval habitats. Of these, 4 [23,24,25,26] reported that the products were fairly safe to the non-target organisms whereas the fifth [27] indicated that Bti caused mortalities in Psychodidae larvae. Six studies evaluated the economic costs of implementing bacterial larvicides interventions in the tropical conditions of SSA (Table 8). The costs varied greatly depending on the ecology of the vectors, the larvicide product deployed and the size of the human population covered by the intervention. The cost per person protected per year (PPPY) varied from USD 0.44 in Ouagadougou, Burkina Faso to USD 2.50 in Mbita, Kenya. The cost PPPY was relatively higher in the rural (range of USD 0.77–2.50) than in the urban settings (range of USD 0.44–0.94). Five of the reviewed studies monitored the acceptability of microbial larvicide interventions to the community members and concluded that they were highly accepted by the general community [23, 28,29,30,31]. However, challenges related to accessing larval habitats in people’s compounds were reported from the large-scale larviciding intervention conducted in Dar es Salaam, Tanzania [32]. In general, Bti and/or Bs larvicide products were perceived as relatively easy to use and suitable to apply with hand and/or conventional sprayers.

Table 8 Cost (in USD) of bacterial larvicide interventions for malaria control in sub-Saharan Africa


After several years of encouraging reports on global malaria decline [33], the 2018 world malaria report indicated that no further significant progress in reducing global malaria cases was made during the 2015–2017 time frame [34]. The persisting malaria transmission occurs despite implementation in time and space of widely effective malaria control interventions, mainly anti-malarial drugs and insecticide-based vector control methods [34]. With the observed resilience in malaria transmission, the current control interventions need to be complemented with other novel methods in an integrated manner to further reduce the malaria burden. Larval source management is an important strategy in malaria control and its potential to lower malaria transmission has been well documented [8, 11, 35,36,37]. When integrated with adult mosquito control interventions, such as LLINs or IRS, the strategy has been found to have a complementary role in lowering malaria transmission [10]. The present article reviews the available literature on implementation of bacterial larvicides for malaria vector control in sub-Saharan Africa (SSA) to provide an informed background for designing larval source management using these agents.

Reduction in malaria burden and intensity of parasite transmission [expressed as entomological inoculation rate (EIR), a measure of infectious bite per person per unit time] recorded over the past two decades is an important epidemiological juncture to intensify malaria control measures. It has been shown that once EIRs fall below one infectious bite per person per year, malaria burden becomes much more responsive to further reductions in transmission [38]. Thus, as malaria continues to decline, larviciding interventions may have a much greater epidemiological impact as a supplementary intervention, secondary to primary front-line options like LLINs/IRS. Moreover, larviciding becomes a more feasible intervention for IVM once malaria transmission has been reduced to low and moderate levels by LLINs/IRS or once these tools have reached their maximum practical effect [14]. Recognizing the limitations of the primary front-line vector control tools and reduced progress of malaria control recorded in recent years, call for accelerated development and adoption of diverse options available for malaria vector control [39].

The reviewed studies on bacterial larviciding conducted in field conditions were carried out in typical Anopheles breeding habitats found in SSA and targeted the main malaria vectors An. gambiae (s.l.) and An. funestus. The laboratory and semi-field studies targeted the same vector species. In this region, An. gambiae (s.l.) is known to breed in clear, temporary water bodies exposed to direct sunlight, whereas An. funestus prefers semi-permanent to permanent water bodies with some degree of shading [40]. To be effective, bacterial larvicide interventions require that the habitats that produce malaria vectors are targeted continuously and for indefinite basis. Due to the ephemeral nature of Anopheles larval habitats, identifying and targeting these numerous larval habitats have been considered important challenges of larviciding interventions [13]. However, the advancements in geographical information system (GIS) technology, satellite imagery and drone-based multispectral imagery, have made mapping and generation of high-resolution geo-referenced landscape images possible [41,42,43]. With these new technologies, larval habitats can be relatively easily identified, mapped and targeted for larviciding, thereby overcoming the constraints of the traditional laborious methods of identifying and mapping the habitats.

Various bacterial larvicide products were tested in the reviewed studies, including most of the products available in the market or developed for mosquito control [12, 17]. WDG and CG formulations were the most preferred and these were also used in the large-scale control programmes. While the CG were easily applied by hand and were suitable in larval habitats with dense vegetation, WDG had a lower application rate due to their high toxin content (measured in international toxic units per milligram, ITU/mg). These properties also had implications for transport and storage costs. The newly formulated bacterial larvicides based on granules, tablets and briquettes were designed to offer flexibility in the application in different larval habitat types which vary in their physical characteristics and larvae productivity [12]. The reviewed articles indicated that products based on Bti and/or Bs were fairly easy to apply by hand or with conventional sprayers depending on the formulation and habitat characteristics. Although the larvicidal activity of used products is known to vary with mosquito species, the reviewed studies indicated that they were generally effective in controlling An. gambiae (s.l.), An. funestus (s.l.) and culicine mosquitoes.

The findings of studies implemented in diverse ecological conditions across SSA indicated that at low application rates, bacterial larvicides based on Bti and/or Bs were effective in controlling malaria vectors. The reported effectiveness of these agents in mosquito control corroborates well with findings of other studies conducted elsewhere outside SSA [44,45,46]. It was found that Bti and/or Bs caused a reduction in larval density, vector density, vector biting and malaria transmission in most of the tested areas. However, due to their short duration of activity, repeated applications at weekly or bi-weekly intervals were required to sustain control. On the other hand, products based on sustained slow release formulations showed relatively high residual activity ranging from 3–6 months in selected larval habitats [47, 48]. Moreover, the reviewed studies showed that the efficacy and residual activity of Bti and/or Bs on malaria vectors varied considerably with the prevailing ecological settings of the study site, the test products, as well as the study design. The activity of Bti and Bs is known to be influenced by factors related to the target mosquito, larval habitat conditions and larvicide properties as reported elsewhere [17]. The inherent variation in their activity in different ecological settings needs to be taken into account when designing and scaling-up larvicide interventions.

Many typical larval habitats for malaria vector mosquitoes, particularly the all-important An. gambiae complex in SSA, are in nature transient and shifting [40]. Most of these habitats originate from a wide range of economic important human activities such as agriculture, construction and mining [49]. Although some of the habitats are relatively more permanent and may contain some water for the most of the year, their size and, more importantly, the location of water margin where most of mosquito breeding activities take place fluctuates from week to week depending on weather conditions (mainly rain and sun). In addition to natural forces of the weather, man-made habitats are constantly modified to serve the purpose of which were created for, during cultivation and resumption of construction or mining activities. These activities may end up creating more new habitats or eliminate some altogether. Thus, many active larval habitats for malaria mosquitoes are not always static, but sometimes dynamic and a moving target. For this reason, irrespective of the residuality of the product applied, treated sites must be visited on a regular basis to identify and treat new active larval habitats that may have arisen or to re-treat the existing ones which have been affected by human activities. For this case, residuality is less valuable than it would otherwise be because of the duration and nature of the habitats themselves. Although long-lasting, slow release formulations of larvicides are desirable, less persistent conventional products have wide application in tropical weather conditions and more appropriate for the transient An. gambiae complex larval habitats.

Although the reviewed studies demonstrated the effectiveness of the bacterial larvicides based on Bti and Bs in malaria vector control, the products were found to be less effective in riverine areas with extensive flooding in The Gambia [50], in rice fields and swamps in Zaire (now The Democratic Republic of the Congo) [51], in transient rain puddles in Burkina Faso [27] and in overgrown wetlands in Tanzania [23]. These findings support the view that manual application of bacterial larvicides Bti and/or Bs by ground teams is not a strategy for all larval habitat types [14]. However, as malaria prevalence continues to decline, high transmission areas are attaining low to focal transmission, creating more conducive conditions appropriate for larviciding intervention. If sustained, the decline in malaria parasite transmission intensity creates an important opportunity for adoption of larviciding as a supplementary measure, though the strategy may not be suitable as a stand-alone intervention in many transmission settings. Moreover, it was evident from the reviewed studies that effective control of mosquito larvae can be achieved with repeated treatment of breeding sites and that malaria vector control with bacterial larvicides demands much greater ecological information with regard to water quality and the nature of the mosquito breeding habitats. It was also evident that larvicide intervention was more cost-effective in urban than in rural areas. To be effective, larviciding intervention with Bti and Bs needs to be well adapted to the prevailing local malaria vectors and their ecology.

High implementation costs have been considered as the main factor that prevents broader use of larvicide interventions particularly in SSA [13, 52]. Despite variation in the cost of these interventions reported in different areas of SSA, the cost compared favorably with those for LLINs and IRS interventions [53,54,55]. Some of the reviewed studies indicated that the interventions based on Bti and/or Bs were readily accepted by the general community in the intervention areas [23, 28,29,30,31]. In addition to participation in the larvicide applications, some community members indicated willingness to pay for the intervention [28,29,30,31]. Moreover, the safety of the tested products was found to be high [23,24,25,26], targeting only mosquito larvae and with no deleterious effect to non-target organisms, as also reported in other studies conducted outside SSA [56,57,58]. However, one of the reviewed articles reported that Bti treatment caused mortalities in Psychodidae larvae when applied at the recommended rate [27]. Species of the Psychodidae are among the dipterans that have been shown to be affected by Bti treatment as summarized elsewhere [59].

Larviciding intervention, particularly for control of mosquito with diverse breeding habitats like the major malaria vector in SSA, is labor-intensive undertaking. To be effective, larviciding teams must cover a large number of Anopheles larval habitats, some of which appear and disappear frequently in space and time with high-cost implications. In SSA, financial resources (for equipment, supplies and personnel costs) required to manage larviciding programmes remain intermittent and unreliable [60, 61]. Thus, mobilizing reliable sources of funding is crucial for the success of larvicide interventions. It was also found out that larvicides application by ground teams in rural areas with extensive larval habitats was inappropriate [50]. In areas with large flood plains, extensive wetland and rice cultivation which are largely inaccessible on foot, aerial application of larvicides is more appropriate. Further analysis of the reviewed field studies has shown that a wide range of larvicide products including non-WHOPES-recommended products [14] was evaluated in SSA (Tables 6, 7). This variation in product types tested coupled with heterogeneity in test conditions, did not permit unambiguous analysis of the efficacy of the interventions by geographical settings and/or malaria vector species. While more countries in SSA are adopting (larval source management, LSM) for control of malaria, it is crucial that a package of products for larviciding is streamlined based on WHOPES recommendations to allow for appropriate scale-up of the intervention in the future.

Apart from financial constraints, other major obstacles to delivering larviciding interventions to local communities in SSA include scarcity of trained personnel in the field of vector ecology/biology and lack of organizational structures for governance and management of vertical, decentralized LSM programmes [39, 62]. While it is crucial that these rare specialties are developed, a partnership between academic/research institutions and communities have been applied effectively to fill this technical gap in the implementation of larviciding or other vector control programmes in SSA [60, 62]. With the renewed interest in LSM in SSA, there is an urgent need to develop operational teams and robust organization structures for governance of these programmes in the near future [39, 60, 63]. Beside the outlined shortfalls, SSA is better positioned with adequate human resources to manage labor-intensive larval source management programmes. The availability of effective and yet safe microbial larvicides is making larviciding interventions feasible with such community-based staff with a minimal level of training.

Based on the effectiveness of larvicide products reported in the reviewed studies (Tables 6, 7), the historical success of larvicide interventions for malaria vector control [8, 11] and expert opinions [13, 37], larviciding remains a feasible option that can be included in the IVM programmes to supplement other vector control tools. Following decades of neglect of this strategy in SSA, research is still needed to improve quality of evidence and build skills especially in areas of malaria vector ecology, designing, monitoring and evaluation of larval source management programmes.


The findings from the reviewed studies indicated that, at low application rates, bacterial larvicide products based on Bti and Bs were effective against malaria vectors in SSA. Furthermore, the larvicide intervention was found to be feasible and safe to non-target organisms and its cost compared fairly well with those of other vector control measures practiced in SSA. However, interventions based on these agents require substantial knowledge of larval ecology due to the effect of environment and larval habitat characteristics on these agents. As malaria continues to decline in SSA, larviciding should gain more ground due to shrinking of transmission areas and creation of more appropriate conditions for the intervention, and in order to delay the evolution of insecticide resistance and behavioral adaptations by the vectors. Moreover, the advancement of technology for mapping landscapes could facilitate the identification and targeting the numerous larval habitats preferred by the African malaria vectors. To build sustainable anti-larval measures in SSA, there is a great need to build capacity in relevant specialties in vector control and develop organizational structures for governance and management of larval source management programmes.

Availability of data and materials

All relevant data supporting the conclusions of this article are included within the article.


Bti :

Bacillus thuringiensis var. israelensis

Bs :

Bacillus sphaericus


international toxic units


water-dispersible granules


corn granules




flowable concentrate


wettable powder


sustained-release granular


water-based suspension


primary powder


technical powder


liquid concentrate


aqueous suspension


long-lasting insecticide-treated nets


indoor residual spraying


sub-Saharan Africa


integrated vector management


geographical information system


entomological inoculation rate


person protected per year


World Health Organization Pesticides Evaluation Scheme


larval source management


  1. 1.

    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.

  2. 2.

    Kleinschmidt I, Bradley J, Knox TB, Mnzava AP, Kafy HT, Mbogo C, et al. Implications of insecticide resistance for malaria vector control with long-lasting insecticidal nets: a WHO-coordinated, prospective, international, observational cohort study. Lancet Infect Dis. 2018;18:640–9.

  3. 3.

    Hancock PA, Wiebe A, Gleave KA, Bhatt S, Cameron E, Trett A, et al. Associated patterns of insecticide resistance in field populations of malaria vectors across Africa. Proc Natl Acad Sci USA. 2018;115:5938–43.

  4. 4.

    Protopopoff N, Mosha JF, Lukole E, Charlwood JD, Wright A, Mwalimu CD, et al. Effectiveness of a long-lasting piperonyl butoxide-treated insecticidal net and indoor residual spray interventions, separately and together, against malaria transmitted by pyrethroid-resistant mosquitoes: a cluster, randomised controlled, two-by-two factorial design trial. Lancet. 2018;391:1577–88.

  5. 5.

    Sougoufara S, Doucouré S, Sembéne PMB, Harry M, Sokhna C. Challenges for malaria vector control in sub-Saharan Africa: resistance and behavioral adaptations in Anopheles populations. J Vector Borne Dis. 2017;54:4–15.

  6. 6.

    Kamdem C, Fouet C, Gamez S, White BJ. Pollutants and insecticides drive local adaptation in African malaria mosquitoes. Mol Biol Evol. 2017;34:1261–75.

  7. 7.

    Killeen GF, Ranson H. Insecticide-resistant malaria vectors must be tackled. Lancet. 2018;391:1551–2.

  8. 8.

    Killeen GF, Fillinger U, Kiche I, Gouagna LC, Knols BGJ. Eradication of Anopheles gambiae from Brazil: lessons for malaria control in Africa? Lancet Infect Dis. 2002;2:618–27.

  9. 9.

    Killeen GF, Fillinger U, Knols BGJ. Advantages of larval control for African malaria vectors: low mobility and behavioural responsiveness of immature mosquito stages allow high effective coverage. Malar J. 2002;1:8.

  10. 10.

    Fillinger U, Ndenga B, Githeko A, Lindsay SW. Integrated malaria vector control with microbial larvicides and insecticide-treated nets in western Kenya: a controlled trial. Bull World Health Organ. 2009;87:655–65.

  11. 11.

    Shousha AT. Species-eradication. The eradication of Anopheles gambiae from Upper Egypt 1942–1945. Bull World Health Organ. 1948;1:309–42.

  12. 12.

    Walker K, Lynch M. Contributions of Anopheles larval control to malaria suppression in tropical Africa: review of achievements and potential. Med Vet Entomol. 2007;21:2–21.

  13. 13.

    Fillinger U, Lindsay SW. Larval source management for malaria control in Africa: myths and reality. Malar J. 2011;10:353.

  14. 14.

    WHO. a supplementary measure for malaria control. An operational manual. Geneva: World Health Organization; 2013.

  15. 15.

    WHO. World Health Assembly Resolution 50.13: Promotion of chemical safety, with special attention to persistent organic pollutants. Geneva: World Health Organization; 1997. Accessed 1 Mar 2019.

  16. 16.

    Mittal PK. Biolarvicides in vector control: challenges and prospects. J Vector Borne Dis. 2003;40:20–32.

  17. 17.

    Lacey LA. Bacillus thuringiensis serovariety israelensis and Bacillus sphaericus for mosquito control. Am Mosq Control Assoc. 2007;23:133–63.

  18. 18.

    Barbazan P, Baldet T, Darrieit E, Escaffre H, Haman DD, Hougard J-M. Impact of treatments with Bacillus sphaericus on Anopheles populations and the transmission of malaria in Maroua, a large city in a Savannah Region of Cameroon. J Am Mosq Control Assoc. 1998;14:33–9.

  19. 19.

    Kandyata A, Mbata KJ, Shinondo CJ, Katongo C, Kamuliwo RM, Nyirenda F, et al. Impacts of Bacillus thuringiensis var. israelensis and Bacillus sphaericus insect larvicides on mosquito larval densities in Lusaka, Zambia. Med J Zambia. 2012;39:33–8.

  20. 20.

    Nicolas L, Darriet F, Hougard JM. Efficacy of Bacillus sphaericus 2362 against larvae of Anopheles gambiae under laboratory and field conditions in West Africa. Med Vet Entomol. 1987;1:157–62.

  21. 21.

    Derua YA, Kahindi SC, Mosha FW, Kweka EJ, Atieli HE, Zhou G, et al. Susceptibility of Anopheles gambiae complex mosquitoes to microbial larvicides in diverse ecological settings in western Kenya. Med Vet Entomol. 2019;33:220–7.

  22. 22.

    Kinde-Gazard D, Baglo T. Assessment of microbial larvicide spraying with Bacillus thuringiensis israelensis, for the prevention of malaria. Med Mal Infect. 2012;42:114–8.

  23. 23.

    Magesa SM, Athumani Y, Barongo V, Sambu EZ, Senkoro KP, Mboera LEG, et al. Efficacy of Bacillus thuringiensis var. israelensis (Bactivec®) and Bacillus sphaericus (Griselesf®) for control of mosquito larvae: a field trial in Mvomero and Bagamoyo districts. Dar es Salaam: National Institute for Medical Research; 2009.

  24. 24.

    Derua YA, Kahindi SC, Mosha FW, Kweka EJ, Atieli HE, Wang X, et al. Microbial larvicides for mosquito control: impact of long lasting formulations of Bacillus thuringiensis var. israelensis and Bacillus sphaericus on non-target organisms in western Kenya highlands. Ecol Evol. 2018;8:7563–73.

  25. 25.

    Ravoahangimalala O, Thiery I, Sinegre G. Rice field efficacy of deltamethrin and Bacillus thuringiensis israelensis formulations on Anopheles gambiae s.s. in the Anjiro Region of Madagascar. Bull Soc Vector Ecol. 1994;19:169–74.

  26. 26.

    Ragoonanansingh RN, Njunwa KJ, Curtis CF, Becker N. A field study of Bacillus sphaericus for the control of culicine and anopheline mosquito larvae in Tanzania. Bull Soc Vector Ecol. 1992;17:45–50.

  27. 27.

    Skovmand O, Sanogo E. Experimental formulations of Bacillus sphaericus and B. thuringiensis israelensis against Culex quinquefasciatus and Anopheles gambiae (Diptera: Culicidae) in Burkina Faso. J Med Entomol. 1999;36:62–7.

  28. 28.

    Mboera LEG, Kramer RA, Miranda ML, Kilima SP, Shayo EH, Lesser A. Community knowledge and acceptance of larviciding for malaria control in a rural district of east-central Tanzania. Int J Environ Res Public Health. 2014;11:5137–54.

  29. 29.

    Ingabire CM, Hakizimana E, Rulisa A, Kateera F, Van Den Borne B, Muvunyi CM, et al. Community-based biological control of malaria mosquitoes using Bacillus thuringiensis var. israelensis (Bti) in Rwanda: community awareness, acceptance and participation. Malar J. 2017;16:399.

  30. 30.

    Mazigo HD, Massawe IS, Rumisha SF, Kweka EJ, Mboera LEG. Rice farmers’ perceptions and acceptability in the use of a combination of biolarvicide (Bacillus thuringiensis var. israeliensis) and fertilizers application for malaria control and increase rice productivity in a rural district of central Tanzania. Malar J. 2019;18:71.

  31. 31.

    Dambach P, Jorge MM, Traoré I, Phalkey R, Sawadogo H, Zabré P, et al. A qualitative study of community perception and acceptance of biological larviciding for malaria mosquito control in rural Burkina Faso. BMC Public Health. 2018;18:399.

  32. 32.

    Geissbühler Y, Kannady K, Chaki PP, Emidi B, Govella NJ, Mayagaya V, et al. Microbial larvicide application by a large-scale, community-based program reduces malaria infection prevalence in urban Dar es Salaam, Tanzania. PLoS ONE. 2009;4:e5107.

  33. 33.

    WHO. World malaria report 2017. Geneva: World Health Organization; 2017.

  34. 34.

    WHO. World malaria report 2018. Geneva: World Health Organization; 2018.

  35. 35.

    Utzinger J, Tozan Y, Singer BH. Efficacy and cost-effectiveness of environmental management for malaria control. Trop Med Int Health. 2001;6:677–87.

  36. 36.

    Utzinger J, Tozan Y, Doumani F, Singer BH. The economic payoffs of integrated malaria control in the Zambian Copperbelt between 1930 and 1950. Trop Med Int Health. 2002;7:657–77.

  37. 37.

    Tusting LS, Thwing J, Sinclair D, Fillinger U, Gimnig J, Bonner KE, et al. Mosquito larval source management for controlling malaria. Cochrane Database Syst Rev. 2015;8:CD008923.

  38. 38.

    Beier JC, Killeen GF, Githure JI. Short report: entomologic inoculation rates and Plasmodium falciparum malaria prevalence in Africa. Am J Trop Med Hyg. 1999;61:109–13.

  39. 39.

    Killeen GF, Tatarsky A, Diabate A, Chaccour CJ, Marshall JM, Okumu FO, et al. Developing an expanded vector control toolbox for malaria elimination. BMJ Glob Health. 2017;2:e000211.

  40. 40.

    Gillies MT, Coetzee M. A supplement to the Anophelinae of Africa south of the Sahara (Afrotropical region). Johannesburg: South Africa Institute for Medical Research; 1987.

  41. 41.

    Mushinzimana E, Munga S, Minakawa N, Li L, Feng C-C, Bian L, et al. Landscape determinants and remote sensing of anopheline mosquito larval habitats in the western Kenya highlands. Malar J. 2006;5:13.

  42. 42.

    Carrasco-Escobar G, Manrique E, Ruiz-Cabrejos J, Saavedra M, Alava F, Bickersmith S, et al. High-accuracy detection of malaria vector larval habitats using drone-based multispectral imagery. PLoS Negl Trop Dis. 2019;13:e0007105.

  43. 43.

    Hardy A, Makame M, Cross D, Majambere S, Msellem M. Using low-cost drones to map malaria vector habitats. Parasit Vectors. 2017;10:29.

  44. 44.

    Kumar A, Sharma VP, Sumodan PK, Thavaselvam D. Field trials of biolarvicide Bacillus thuringiensis var. israelensis strain 164 and the larvivorous fish Aplocheilus blocki against Anopheles stephensi for malaria control in Goa, India. J Am Mosq Control Assoc. 1998;14:457–62.

  45. 45.

    Kroeger A, Horstick O, Riedl C, Kaiser A, Becker N. The potential for malaria control with the biological larvicide Bacillus thuringiensis israelensis (Bti) in Peru and Ecuador. Acta Trop. 1995;60:47–57.

  46. 46.

    Becker N. Microbial control of mosquitoes: management of the Upper Rhine mosquito population as a model programme. Parasitol Today. 1997;13:485–7.

  47. 47.

    Afrane YA, Mweresa NG, Wanjala CL, Gilbreath-III TM, Zhou G, Lee M-C, et al. Evaluation of long-lasting microbial larvicide for malaria vector control in Kenya. Malar J. 2016;15:577.

  48. 48.

    Kahindi SC, Muriu S, Derua YA, Wang X, Zhou G, Lee M-C, et al. Efficacy and persistence of long-lasting microbial larvicides against malaria vectors in western Kenya highlands. Parasit Vectors. 2018;11:438.

  49. 49.

    Fillinger U, Lindsay SW. Suppression of exposure to malaria vectors by an order of magnitude using microbial larvicides in rural Kenya. Trop Med Int Health. 2006;11:1629–42.

  50. 50.

    Majambere S, Pinder M, Fillinger U, Ameh D, Conway DJ, Green C, et al. Is mosquito larval source management appropriate for reducing malaria in areas of extensive flooding in the Gambia? A cross-over intervention trial. Am J Trop Med Hyg. 2010;82:176–84.

  51. 51.

    Karch S, Asid N, Manzambi M, Salaun JJ. Efficacy of Bacillus sphaericus against the malaria vector Anopheles gambiae and other mosquitoes in swamps and rice fields in Zaire. J Am Mosq Control Assoc. 1992;8:376–80.

  52. 52.

    Dambach P, Schleicher M, Stahl HC, Traoré I, Becker N, Kaiser A, et al. Routine implementation costs of larviciding with Bacillus thuringiensis israelensis against malaria vectors in a district in rural Burkina Faso. Malar J. 2016;15:380.

  53. 53.

    Yukich J, Tediosi F, Lengeler C. Operations, costs and cost-effectiveness of five insecticide-treated net programs (Eritrea, Malawi, Tanzania, Togo, Senegal) and two indoor residual spray programs (Kwa-Zulu-Natal, Mozambique). Washington: USAID; 2007.

  54. 54.

    Yukich JO, Lengeler C, Tediosi F, Brown N, Mulligan JA, Chavasse D, et al. Costs and consequences of large-scale vector control for malaria. Malar J. 2008;7:258.

  55. 55.

    Worrall E, Connor S, Thomson M. Improving the cost-effectiveness of IRS with climate informed health surveillance systems. Malar J. 2008;7:263.

  56. 56.

    Lacey LA, Merritt RW. The safety of bacterial microbial agents used for black fly and mosquito control in aquatic environments. In: Hokkanen HMT, Hajek AE, editors. Environmental impact of microbial insecticides: need and methods for risk assessment. Dordrecht: Kluwer Academic Publishers; 2003. p. 151–68.

  57. 57.

    Merritt RW, Lessard JL, Wessell KJ, Hernandez O, Berg MB, Wallace JR, et al. Lack of effects of Bacillus sphaericus (Vectolex) on nontarget organisms in a mosquito-control program in southeastern Wisconsin: a 3-year study. J Am Mosq Control Assoc. 2005;21:201–12.

  58. 58.

    Lagadic L, Roucaute M, Caquet T. Bti sprays do not adversely affect non-target aquatic invertebrates in French Atlantic coastal wetlands. J Appl Ecol. 2014;51:102–13.

  59. 59.

    Boisvert M, Boisvert J. Effects of Bacillus thuringiensis var. israelensis on target and nontarget organisms: a review of laboratory and field experiments. Biocontrol Sci Technol. 2000;10:517–61.

  60. 60.

    Fillinger U, Kannady K, William G, Vanek MJ, Dongus S, Nyika D, et al. A tool box for operational mosquito larval control: preliminary results and early lessons from the Urban Malaria Control Programme in Dar es Salaam, Tanzania. Malar J. 2008;7:20.

  61. 61.

    Dambach P, Traoré I, Kaiser A, Sié A, Sauerborn R, Becker N. Challenges of implementing a large scale larviciding campaign against malaria in rural Burkina Faso - lessons learned and recommendations derived from the EMIRA project. BMC Public Health. 2016;16:1023.

  62. 62.

    Mukabana WR, Kannady K, Kiama GM, Ijumba JN, Mathenge EM, Kiche I, et al. Ecologists can enable communities to implement malaria vector control in Africa. Malar J. 2006;5:9.

  63. 63.

    Chaki PP, Kannady K, Mtasiwa D, Tanner M, Mshinda H, Kelly AH, et al. Institutional evolution of a community-based programme for malaria control through larval source management in Dar es Salaam, United Republic of Tanzania. Malar J. 2014;13:245.

  64. 64.

    Ketseoglou I, Koekemoer LL, Coetzee M, Bouwer G. The larvicidal efficacy of Bacillus thuringiensis subsp. israelensis against five African Anopheles (Diptera: Culicidae) species. Afr Entomol. 2011;19:146–50.

  65. 65.

    Seyoum A, Abate D. Larvicidal efficacy of Bacillus thuringiensis var. israelensis and Bacillus sphaericus on Anopheles arabiensis in Ethiopia. World J Microbiol Biotechnol. 1997;13:21–4.

  66. 66.

    Baffour-awuah S, Owusu-Dabo E, Kruppa T, Annan A, Nartey R, Dogbe J, et al. Lysinibacillus sphaericus biolarvicide, an efficacious tool in the control of Anopheles gambiae in Kumasi, Ghana. East Afr J Public Health. 2014;11:851–61.

  67. 67.

    Fillinger U, Knols BGJ, Becker N. Efficacy and efficiency of new Bacillus thuringiensis var. israelensis and Bacillus sphaericus formulations against Afrotropical anophelines in western Kenya. Trop Med Int Health. 2003;8:37–47.

  68. 68.

    Nartey R, Owusu-Dabo E, Kruppa T, Baffour-Awuah S, Annan A, Oppong S, et al. Use of Bacillus thuringiensis var. israelensis as a viable option in an integrated malaria vector control programme in the Kumasi Metropolis, Ghana. Parasit Vectors. 2013;6:116.

  69. 69.

    Majambere S, Lindsay SW, Green C, Kandeh B, Fillinger U. Microbial larvicides for malaria control in The Gambia. Malar J. 2007;6:76.

  70. 70.

    Majori G, Ali A, Sabatinelli G. Laboratory and field efficacy of Bacillus thuringiensis var. israelensis and Bacillus sphaericus against Anopheles gambiae s.l. and Culex quinquefasciatus in Ouagadougou, Burkina Faso. J Am Mosq Control Assoc. 1987;3:20–5.

  71. 71.

    Dambach P, Louis VRV, Kaiser A, Ouedraogo S, Sie A, Sauerborn R, et al. Efficacy of Bacillus thuringiensis var. israelensis against malaria mosquitoes in northwestern Burkina Faso. Parasit Vectors. 2014;7:371.

  72. 72.

    Demissew A, Balkew M, Girma M. Larvicidal activities of chinaberry, neem and Bacillus thuringiensis israelensis (Bti) to an insecticide resistant population of Anopheles arabiensis from Tolay, Southwest Ethiopia. Asian Pac J Trop Biomed. 2016;6:554–61.

  73. 73.

    Zogo B, Tchiekoi BNC, Koffi AA, Dahounto A, Ahoua Alou LP, Dabiré RK, et al. Impact of sunlight exposure on the residual efficacy of biolarvicides Bacillus thuringiensis israelensis and Bacillus sphaericus against the main malaria vector, Anopheles gambiae. Malar J. 2019;18:55.

  74. 74.

    Diédhiou SM, Konaté L, Doucouré S, Samb B, Niang EA, Sy O, et al. Effectiveness of three biological larvicides and of an insect growth regulator against Anopheles arabiensis in Senegal. Bull Soc Pathol Exot. 2016;110:102–15.

  75. 75.

    Djènontin A, Pennetier C, Zogo B, Soukou KB, Ole-Sangba M, Akogbéto M, et al. Field efficacy of vectobac GR as a mosquito larvicide for the control of anopheline and culicine mosquitoes in natural habitats in Benin, West Africa. PLoS ONE. 2014;9:e87934.

  76. 76.

    Imbahale SS, Githeko A, Mukabana WR, Takken W. Integrated mosquito larval source management reduces larval numbers in two highland villages in western Kenya. BMC Public Health. 2012;12:362.

  77. 77.

    Kahindi SC, Midega JT, Mwangangi JM, Kibe LW, Nzovu J, Luethy P, et al. Efficacy of vectobac DT and Culinexcombi against mosquito larvae in unused swimming pools in Malindi, Kenya. J Am Mosq Control Assoc. 2008;24:538–42.

  78. 78.

    Karch S, Manzambi ZA, Salaun JJ. Field trials with Vectolex (Bacillus sphaericus) and Vectobac (Bacillus thuringiensis (H-14)) against Anopheles gambiae and Culex quinquefasciatus breeding in Zaire. J Am Mosq Control Assoc. 1991;7:176–9.

  79. 79.

    Mpofu M, Becker P, Mudambo K, De Jager C. Field effectiveness of microbial larvicides on mosquito larvae in malaria areas of Botswana and Zimbabwe. Malar J. 2016;15:586.

  80. 80.

    Mwangangi JM, Kahindi SC, Kibe LW, Nzovu JG, Luethy P, Githure JI, et al. Wide-scale application of Bti/Bs biolarvicide in different aquatic habitat types in urban and peri-urban Malindi, Kenya. Parasitol Res. 2011;108:1355–63.

  81. 81.

    Obopile M, Segoea G, Waniwa K, Ntebela DS, Moakofhi K, Motlaleng M, et al. Did microbial larviciding contribute to a reduction in malaria cases in eastern Botswana in 2012–2013? PHA. 2018;8(Suppl. 1):50–4.

  82. 82.

    Romi R, Ravoniharimelina B, Ramiakajato M, Majori G. Field trials of Bacillus thuringiensis H-14 and Bacillus sphaericus (strain 2362) formulations against Anopheles arabiensis in the central highlands of Madagascar. J Am Mosq Control Assoc. 1993;9:325–9.

  83. 83.

    Skovmand O, Bauduin S. Efficacy of a granular formulation of Bacillus sphaericus against Culex quinquefasciatus and Anopheles gambiae in West African countries. J Vector Ecol. 1997;22:43–51.

  84. 84.

    Skovmand O, Ouedraogo TDA, Sanogo E, Samuelsen H, Toé LP, Baldet T. Impact of slow-release Bacillus sphaericus granules on mosquito populations followed in a tropical urban environment. J Med Entomol. 2009;46:67–76.

  85. 85.

    Tchicaya ES, Koudou BG, Keiser J, Adja AM, Cisse G, Tanner M, et al. Effect of repeated application of microbial larvicides on malaria transmission in central Cote d’Ivoire. J Am Mosq Control Assoc. 2009;25:382–5.

  86. 86.

    Zhou G, Afrane YA, Dixit A, Atieli HE, Lee MC, Wanjala CL, et al. Modest additive effects of integrated vector control measures on malaria prevalence and transmission in western Kenya. Malar J. 2013;12:256.

  87. 87.

    Kramer RA, Mboera LEG, Senkoro K, Lesser A, Shayo EH, Paul CJ, Miranda ML. A randomized longitudinal factorial design to assess malaria vector control and disease management interventions in rural Tanzania. Int J Environ Res Public Health. 2014;11:5317–32.

  88. 88.

    Shililu JI, Tewolde GM, Brantly E, Githure JI, Mbogo CM, Beier JC, et al. Efficacy of Bacillus thuringiensis israelensis, Bacillus sphaericus and temephos for managing Anopheles larvae in Eritrea. J Am Mosq Control Assoc. 2003;19:251–8.

  89. 89.

    Shililu J, Mbogo C, Ghebremeskel T, Githure J, Novak R. Mosquito larval habitats in a semiarid ecosystem in Eritrea: impact of larval habitat management on Anopheles arabiensis population. Am J Trop Med Hyg. 2007;76:103–10.

  90. 90.

    Van Den Berg H, Van Vugt M, Kabaghe AN, Nkalapa M, Kaotcha R, Truwah Z, et al. Community-based malaria control in southern Malawi: a description of experimental interventions of community workshops, house improvement and larval source management. Malar J. 2018;17:266.

  91. 91.

    Msellemu D, Namango HI, Mwakalinga VM, Ntamatungiro AJ, Mlacha Y, Mtema ZJ, et al. The epidemiology of residual Plasmodium falciparum malaria transmission and infection burden in an African city with high coverage of multiple vector control measures. Malar J. 2016;15:288.

  92. 92.

    Maheu-Giroux M, Castro MC. Cost-effectiveness of larviciding for urban malaria control in Tanzania. Malar J. 2014;13:477.

  93. 93.

    Rahman R, Lesser A, Mboera L, Kramer R. Cost of microbial larviciding for malaria control in rural Tanzania. Trop Med Int Health. 2016;21:1468–75.

  94. 94.

    Worrall E, Fillinger U. Large-scale use of mosquito larval source management for malaria control in Africa: a cost analysis. Malar J. 2011;10:338.

  95. 95.

    Skovmand O, Ouedraogo TDA, Sanogo E, Samuelsen H, Toé LP, Bosselmann R, et al. Cost of integrated vector control with improved sanitation and road infrastructure coupled with the use of slow-release Bacillus sphaericus granules in a tropical urban setting. J Med Entomol. 2011;48:813–21.

Download references


We are grateful to Dr Paul Erik Simonsen from the University of Copenhagen, Denmark for constructive comments to the manuscript.


Not applicable.

Author information




YAD, FWM conceived and designed the review. YAD conducted literature search and drafted the manuscript with inputs from EJK, FWM, AKG and WNK. All authors read and approved the final manuscript.

Corresponding author

Correspondence to Yahya A. Derua.

Ethics declarations

Ethics approval and consent to participate

Not applicable.

Consent for publication

Not applicable.

Competing interests

The authors declare that they have no competing interests.

Additional information

Publisher's Note

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

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

Derua, Y.A., Kweka, E.J., Kisinza, W.N. et al. Bacterial larvicides used for malaria vector control in sub-Saharan Africa: review of their effectiveness and operational feasibility. Parasites Vectors 12, 426 (2019).

Download citation


  • Bacterial larvicides
  • Bacillus thuringiensis var. israelensis
  • Bacillus sphaericus
  • Anopheles gambiae (sensu lato)
  • Anopheles gambiae (sensu stricto)
  • Anopheles arabiensis
  • Anopheles funestus
  • Sub-Saharan Africa


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.