Six decades of malaria vector control in southern Africa: a review of the entomological evidence-base
Malaria Journal volume 21, Article number: 279 (2022)
Countries in the southern Africa region have set targets for malaria elimination between 2020 and 2030. Malaria vector control is among the key strategies being implemented to achieve this goal. This paper critically reviews published entomological research over the past six decades in three frontline malaria elimination countries namely, Botswana Eswatini and Namibia, and three second-line malaria elimination countries including Mozambique, Zambia, and Zimbabwe. The objective of the review is to assess the current knowledge and highlight gaps that need further research attention to strengthen evidence-based decision-making toward malaria elimination.
Publications were searched on the PubMed engine using search terms: “(malaria vector control OR vector control OR malaria vector*) AND (Botswana OR Swaziland OR Eswatini OR Zambia OR Zimbabwe OR Mozambique)”. Opinions, perspectives, reports, commentaries, retrospective analysis on secondary data protocols, policy briefs, and reviews were excluded.
The search resulted in 718 publications with 145 eligible and included in this review for the six countries generated over six decades. The majority (139) were from three countries, namely Zambia (59) and Mozambique (48), and Zimbabwe (32) whilst scientific publications were relatively scanty from front-line malaria elimination countries, such as Namibia (2), Botswana (10) and Eswatini (4). Most of the research reported in the publications focused on vector bionomics generated mostly from Mozambique and Zambia, while information on insecticide resistance was mostly available from Mozambique. Extreme gaps were identified in reporting the impact of vector control interventions, both on vectors and disease outcomes. The literature is particularly scanty on important issues such as change of vector ecology over time and space, intervention costs, and uptake of control interventions as well as insecticide resistance.
The review reveals a dearth of information about malaria vectors and their control, most noticeable among the frontline elimination countries: Namibia, Eswatini and Botswana. It is of paramount importance that malaria vector research capacity and routine entomological monitoring and evaluation are strengthened to enhance decision-making, considering changing vector bionomics and insecticide resistance, among other determinants of malaria vector control.
The World Health Organization (WHO) together with the Roll Back Malaria (RBM) partnership have set targets for malaria elimination which are highlighted in the Global Technical Strategy for Malaria 2016–2030 . In the southern Africa region (SAR) the elimination agenda is being pursued through initiatives such as Elimination 8 (E-8), launched in 2009 by the Southern African Development Community (SADC) . The E-8 goal was to enable and accelerate the achievement of zero local transmission in the four frontline countries, Namibia, South Africa, Eswatini and Botswana, by 2020, and the second line countries, Angola, Zambia, Mozambique, and Zimbabwe, by 2030 through the provision of a joint platform for collaboration and joint strategic programming . The goal of elimination in the SAR was premised on the documented reduction of malaria cases over the past 2000 to 2010 decade, attributed to improved case management and vector control, primarily indoor residual spraying (IRS) . IRS with dichlorodiphenyltrichloroethane (DDT) played a significant role in the drastic reduction of morbidity and mortality in the region, going as far back as the 1940s in South Africa, Zimbabwe and Eswatini (formerly Swaziland) . Before the introduction of IRS, malaria was hyper-endemic with intense seasonal transmission in endemic areas within the SAR [6,7,8,9,10,11]. The introduction of IRS was guided by surveys published between 1931 and 1957, reporting the wide spread of malaria vectors of the Anopheles gambiae complex and Anopheles funestus [6, 10, 12,13,14,15]. The commencement of IRS in the SAR dates to 1931 in South Africa when pyrethrum was tested on an experimental basis. From the mid-1940s DDT was used operationally targeting all malarious areas .
Successful implementation of IRS requires well-structured programmes, and countries like Eswatini and South Africa have National Malaria Control Programs (NMCP) dating back for almost seven decades [4, 16]. The upscaling of IRS with DDT was gradual [13, 17]. In Zimbabwe, DDT was introduced as a pilot in 1945 and evolved into a large-scale ‘barrier’ spraying programme to prevent epidemics and limit the spread of the disease to malaria-free areas . After 1980 IRS applications expanded to reduce morbidity and mortality rather than only preventing epidemics . In Botswana, even though the NMCP was established in 1974, IRS had been reported as far back as the mid-1940s , and by the 1950s, IRS with DDT became the main vector control method in the country . The National Vector-Borne Diseases Control Programme (NVBDCP) of Namibia was established in 1991, however, malaria control efforts using IRS with DDT had been implemented since 1965 in selected areas and upscaled to full coverage in the 1970s . Zambia established a comprehensive National Malaria Control Centre (NMCC) in the 1990s (1997) [20, 21] though the malaria control efforts started with the Mosquito Extermination Act of 1944 which mandated household management of outdoor water containers to eliminate mosquito breeding sites . In the late 1950s, Zambia introduced IRS with DDT whereby municipal councils and the ministry of health sprayed urban areas, and mining companies administered and financed the program in mining districts . Unlike the other SAR countries, Mozambique’s malaria control efforts collapsed due to the civil war in the late 1970s , after the country had been implementing IRS with DDT in selected southern parts of the country between 1960 and 1969 , as an upscale from the first round of implementation in 1946 [15, 24].
From the late 1980s onwards, countries started to shift at varying degrees from DDT to other insecticides belonging to the pyrethroid and carbamate groups in part due to the international lobby against persistent organic pollutants . One of the notable successes in malaria control in the SAR was the Lubombo Spatial Development Initiative (LSDI) a tri-country project between South Africa, Eswatini (Swaziland) and Mozambique established in 2000, with one of its aims to decrease the transmission of malaria in the region largely using IRS in the at-risk regions and border areas [26, 27]. The success of the LSDI was evidenced in the substantial decreases in disease burden observed over 12 years across the three participating countries . Control of malaria vector mosquitoes through insecticide-based IRS with insecticides, is still the primary malaria prevention tool in all malarious regions of SAR, nearly 80 years after its first use. Despite rigorous efforts, the ambitious control and elimination plans for the SAR countries [2, 3] have not been achieved [28, 29], with indigenous malaria cases increasing in several countries in recent years [3, 28].
A multitude of entomological studies from other (non-SAR) malaria-endemic regions in sub-Saharan Africa highlight the changing environmental conditions over the past decades, including land use and climate changes, changing vector dynamics and behaviours, and increasing insecticide resistance and more mobile human populations [30,31,32]. These studies highlight the importance of rigorous vector monitoring programs going hand in hand with vector control efforts to tailor evidence-based interventions. Here we review the literature for the six SAR countries over the past six decades with the aim to summarize the current knowledge base generated from entomological research and highlight gaps requiring attention for a more informed malaria elimination strategy.
Materials and methods
Articles for this review were identified through a search on PubMed on 17th March 2021. The following search terms were used: “(malaria vector control OR vector control OR malaria vector*) AND (Botswana OR Swaziland OR Eswatini OR Zambia OR Zimbabwe OR Mozambique)”. The following inclusion criteria were applied for the review: (i) articles reporting data from Botswana, Eswatini (Swaziland), Zambia, Zimbabwe, and Mozambique; (ii) articles that included data on the following outcomes of interest: vector ecology, vector biology, vector control, long-lasting insecticidal nets, indoor residual spraying, insecticide-treated bed nets, larvicides, larval source management, habitat modification, habitat manipulation, biological control, house screening, house modification and mosquito repellents, the impact of vector control interventions, evaluation of vector control interventions, insecticide resistance and susceptibility, knowledge on malaria disease and malaria vectors; and (iii) articles reporting retrospective data that has not been published before. This review excluded studies that were opinions, perspectives, commentaries, retrospective analysis on secondary data already published in the original study, protocols, policy briefs, reports, and reviews.
This review excluded South Africa within the SAR region, as the country has well-established health research organizations and significant entomological expertise and training programs in stark contrast to the reviewed countries. To illustrate this, the same search terms were applied for South Africa only and the overall number of publications contrasted in the result section.
Data from the selected articles were extracted onto a data extraction form created in Microsoft Excel for descriptive analysis of information on key study aspects matching our inclusion criteria such as design, intervention, aim and outcome. Studies conducted in laboratory settings using laboratory colonized malaria vectors, or vectors originating from the field but with the most analysis done in the laboratory, were classified as “laboratory studies” whereas those conducted under simulated field conditions (experimental huts) with field-collected or laboratory-reared mosquitoes were categorized as “semi-field studies”. “Field studies” included research activities that took place in the natural setting, or data used in the study originated from natural settings (field-collected mosquitoes that were analysed or tested in the laboratory).
The initial search yielded 719 articles. After screening titles and abstracts, we excluded 508 articles because they did not fulfil the inclusion criteria. Following a full-text review of 211 articles, a further 66 articles were excluded because they either reported on secondary data, were reviews, perspectives, or did not report on malaria vectors or control. This left only 145 articles published between 1963 and March 2021 for inclusion in this review, where in some cases one publication reported data from more than one of the target countries (Fig. 1).
Publications by country
Of the 145 eligible studies generated over six decades, the vast majority (139) were implemented in three countries, namely Zambia (59) and Mozambique (48), Zimbabwe (32) whilst scientific publications from front-line countries for elimination, such as Namibia (2), Botswana (11) and Eswatini (4), were scant (Fig. 2). Furthermore, the research studies were aggregated by year and by country (Fig. 3). To put these findings in perspective, the same PubMed search with the same search terms were applied to South Africa over the same time frame from 1963 to 2021. This yielded 2134 results without applying any eligibility criteria, over three times more publications, compared to the 718 publications for the six SAR countries of interest in this review. For malaria-endemic countries in East Africa (Tanzania, Kenya, Uganda, Burundi, and Rwanda) the same search yielded 3085 publications with Tanzania accounting for over a third of them (1081).
To review the publications in the context of the malaria control efforts at the time, publications were aggregated into blocks as follows: malaria-endemic phase (1963–1999), scaling up of malaria control interventions (2000–2006), malaria decline phase (2007–2012), malaria plateau phase (2013–2015) and malaria resurgence phase (2016–2021)  (Table 1). Furthermore, the published research was grouped into two main thematic areas: malaria vector ecology and malaria vector control.
Vector biology and ecology
This review explored the published evidence for vector incrimination, which is a prerequisite for understanding the role of anophelines in malaria transmission and has been used to determine which species are the most important vectors [176, 177]. There was no entomological evidence from Namibia or Eswatini. The incrimination of the primary malaria vector Anopheles arabiensis in Botswana is based on a small number of publications with limited spatial scale [35, 39, 42, 43]. Anopheles gambiae s.s. and Anopheles funestus have been identified as primary vectors in Mozambique [27, 51, 54, 66, 68, 70, 71, 81], Zimbabwe [121, 150, 151, 164, 171], and Zambia [102, 111, 113, 121, 126, 134, 140] (Table 2). The understanding of the local vector system is an essential step toward implementing effective vector control. The available studies on species composition in the SAR countries are limited in space and time, as there is inadequate routine malaria vector surveillance. Longitudinal changes in vector composition are inevitable as highlighted by recent reports of the re-emergence of An. funestus populations  and the discovery of a relatively diverse Anopheles fauna in Botswana . This calls for caution and underscores the need for routine entomological surveillance to better understand the local vector ecology. Changes in the composition of local malaria vectors were also observed in Mozambique, where in the 1990s, both An. funestus and An. arabiensis were equally important vectors [50, 51] while in recent years An. funestus [54, 66, 68, 71, 81] seem to dominate, accounting for over 70% of all collected mosquitoes [54, 66].
Numerous factors can contribute to vector population change such as vector control interventions (LLINs, IRS), human behaviour and climate change [176,177,178]. The effect of vector control intervention on species composition was observed in Mozambique after scaling up of IRS and LLINs [72, 74] and in Zimbabwe where suppression of An. gambiae s.s. by indoor spraying  was observed which could be explained based on the vector’s endophilic tendency of feeding and resting indoors  which is the main target of IRS. On the other hand, it has been shown that the selected sampling strategy can significantly affect what vector species are collected and reported, hence routine entomological surveillance must choose the sampling strategies such that all vectors can be identified. The literature for the reviewed countries is highly diverse with sampling in Mozambique done with CDC light traps, resting catches, exit collections, man baited double net, and knockdown collections [54, 70, 81] while in Zimbabwe the primary collection methods were man-baited nets both indoors and outdoors, complemented by pit traps [150, 171, 172]. The importance of the sampling methods on specie composition is also highlighted by a study from Zambia, where window exit trap collections were dominated by An. arabiensis despite a strong presence of An. funestus and An. gambiae s.s. in the study area .
Few larval ecology studies of these vectors in Botswana [33, 42], Zambia [105, 112], and Eswatini  are limited in scope and cannot inform potential intervention strategies such as larval source management (Table 2). A novel approach to mapping larval breeding sites has been used in Eswatini  which might have the potential to predict larval habitats in remote areas and inform interventions if more thoroughly supported by on-the-ground entomological surveys. The remotely sensed data seems to suggest that permanent habitats associated with farming play a major role in malaria vector production in Eswatini. A similar remote sensing approach was used in a small study area in southern Zambia which is characterized by seasonal streams . Again, permanent to semi-permanent habitats were signified as the major breeding sites of the local vectors. However, there is a need to expand such surveys in space and time in the target countries to be able to arrive at more generalizable results across different eco-epidemiological settings for example to inform the suitability of larval source management in a selected hotspot or elimination areas. The An. funestus larval ecology is generally not well studied in sub-Saharan Africa due to its affiliation with swampy, permanent, and difficult to access water bodies  and hence, it is not surprising that no information is available from the reviewed countries that have identified this species as the main malaria vector.
Adult vector ecology
Knowledge of vector resting behaviour, host-seeking, biting, host preference and vector competence is essential for the strategic implementation of vector control. For instance, knowledge of vector resting behaviour is essential if that behaviour is the target for control, such as the use of IRS. LLINs aim to control vectors that feed indoors when people are asleep. House entry and indoor resting habits of vectors are hence essential for this tool to be effective [181, 182]. Investigating host-seeking behaviour, host preferences and the presence of sporozoites in Anopheles mosquitoes help gauge their role as vectors of malaria . Mosquito biting behaviour includes biting seasonality, diel biting activity (i.e., peak biting in a 24-h cycle) and preferred biting location relative to a house (indoor vs outdoor) . IRS, which is the core intervention in the frontline countries for malaria elimination requires vectors to rest indoors either before or after biting a human. Yet there is a lack of published data on vector resting behaviour from Eswatini and Namibia, and only two small studies from Botswana, [35, 43].
Host preferences and times of biting of local malaria vectors have an impact on the disease transmission and vector control tools need to be aligned with the vector’s behaviour to interrupt man-vector contact . For instance, LLINs and IRS that target mostly indoor feeding and resting mosquitoes are not efficient to control vectors that feed and rest outdoors leading to residual malaria transmission . An. arabiensis has been reported to contribute to residual malaria transmission due to its tendency to feed outdoors , however, in the reviewed countries, three studies from Botswana, Mozambique and Zambia exclusively reported this specie to feed and rest indoors [39, 51, 113]. These observations could be explained by the fact that most mosquitoes were collected indoors. However, this differs from other studies reported elsewhere in sub-Saharan Africa, where An. arabiensis tends to feed and exit domiciles [186, 187]. Further studies are needed to establish this vector’s feeding and resting behaviour in the SAR, to determine its role in the residual transmission and its ability to avoid IRS, which can impact the elimination goal.
LLINs target to interrupt contact between humans and vectors as they form a physical and chemical barrier against mosquitoes. When mosquitoes try to bite, they are not only blocked by the netting but also killed by the insecticide coating. LLINs protect humans while sleeping and the peak feeding time will inform the impact of the intervention. Data from the reviewed countries are largely out of date, dating back a decade or longer. These available reports show clear late-night indoor biting peaks. An. funestus had varying peak hours of feeding between 2100 and 2400 h in Mozambique  and 2200–2300 h and 0200–0400 in Zimbabwe  and in Zambia between 2400 and 0600 h . However, biting peaks for An. funestus have been shown to differ elsewhere in Africa [188,189,190,191]. These observations of indoor resting after feeding for An. gambiae s.s. and An. funestus s.s. seems to confer with the known resting behaviour of these species [181, 182]. There is a need for updated information given that high vector control pressure selects for avoidance behaviours.
Studies on vector parameters such as seasonality and vector competence are scarce in these reviewed countries. An. funestus was reported to be abundant during all seasons in Mozambique . In Zimbabwe, vector peak populations were observed in March and An. funestus densities were higher in the wet than the dry season . Expectedly, the vector peak density is aligned with the rainy seasons in these countries as demonstrated elsewhere [192,193,194]. In Zimbabwe, it was observed that in unfed An. funestus group preferred seeking a human host . The Human Blood Index (HBI) represents the proportion of blood meals derived from humans by mosquito vectors, whereas in Zimbabwe, 64% of collected An. funestus fed on humans and had a Plasmodium falciparum infection rate of 1.8% . The few studies on vector competence from SAR observed the man survival rate for An. funestus and An. arabiensis was 79% with varying sporozoite rates, in Mozambique . A commonly used measure of malaria transmission intensity is the entomological inoculation rate (EIR), defined as the product of the human biting rate (HBR) and sporozoite infection rate (SIR). This review noted a dearth of information on this parameter, with reports from Zambia on EIRs of An. funestus s.s. 39.6 and An. gambiae s.s. of 5.9 .
More recent studies highlight the role of secondary malaria vectors such as Anopheles merus from Mozambique , Anopheles coustani s.l. and Anopheles squamosus from Zambia , as potential local malaria vectors. Although generally believed to be of negligible importance, P. falciparum sporozoites were detected in numerous An. squamosus specimens, in Botswana and Anopheles parensis were found to have human blood . These findings suggest that indoor vector control strategies might not be sufficient for the elimination of malaria in this region. As more studies are implemented in recent times, the complexity of malaria transmission becomes apparent. Implementing vector control independent from entomological evidence might in part be responsible for the persistence of malaria in this region.
Vector control has a long history in the reviewed countries with IRS and to a lower extent LLINs yet there is surprisingly little research data available on the feasibility and impact of interventions.
Indoor residual spraying (IRS) and long-lasting insecticide-treated nets (LLINs)
Despite extensive use, the effectiveness, efficacy, cost, and acceptance of IRS have not been assessed in the frontline countries for malaria elimination. Publications from second-line countries for elimination Zambia [96, 104, 114, 116, 117, 119, 124, 132, 138, 141, 145, 148], Mozambique [27, 53, 56, 59, 62, 63, 85, 89, 90] and Zimbabwe [151, 152, 157, 159, 175] are more abundant, though still comparatively few. The evaluation of different classes of insecticides for IRS has shown that pyrethroids, organochlorides, carbamates and organophosphates have different degrees of effectiveness and efficiency . The organochloride DDT significantly contributed to controlling the spread of malaria in the SAR, but in part due to the environmental concern of this chemical [196, 197], other insecticides were introduced for malaria control.
While the impact of bed nets has been extensively tested and proven in sub-Sahara Africa few reports on effectiveness, efficacy, cost, accessibility, and ownership of bed nets exist from the reviewed countries. As observed with other topics, second-line elimination countries such as Mozambique [57, 61, 75, 79, 80, 89], Zambia [97, 100, 107, 114, 119, 120, 124, 132, 133, 139] and Zimbabwe [139, 162, 166, 168, 175] have more data than elimination countries which do not place a strong emphasis on LLINs in their national malaria control programs. Current LLINs are manufactured for durability. However, research should periodically confirm the field performance of bed nets and barriers to use. Very few studies from Zambia  and Mozambique [77, 78, 88] have observed the durability and integrity of LLINs.
The combined benefits of IRS and LLINs on malaria are of high interest to policy. In Mozambique, no substantial difference was detected in the overall reduction of malaria cases between districts implementing IRS and LLINs . However, this trend is not uniform in the SAR, as Zambia has reported a continuous high burden of malaria after 7 years of implementation of IRS and LLINs in Luapula province . Evidence that incremental impact is achieved when combining IRS and LLINs remains limited and inconsistent. In Zambia, in fourteen population clusters of approximately 1000 residents each in Luangwa and Nyimba districts, where universal coverage targets for LLIN utilization have been achieved, supplementing LLINs with IRS using pyrethroids reduces malaria transmission below levels achieved by LLIN use alone . Concerning insecticide resistance that may occur from selection pressure in such a combination, the authors further recommended supplementing LLINs with IRS using non-pyrethroid insecticide classes, and in addition, attaining far greater transmission reduction .
Larval source management
Larval source management refers to the targeted management of mosquito larval habitats, to suppress mosquito larval and pupal abundance. Techniques used in LSM include environmental management and manipulation, larviciding, biological control or combinations of these methods . In SAR, the use of LSM has not been widely studied nor used. However, there is some documented evidence of the success of LSM in reducing malaria incidence in the pre-era of IRS with DDT, such as seen in the Zambian copper mines, whereby environment management was used to destroy the larval stages of mosquitoes . Two experimental studies in Botswana demonstrated a reduction of larval densities when the biological larvicide Bacillus thuringiensis serovar israelensis (Bti) was applied, however, these were not trials assessing the impact of the tool on malaria transmission [34, 37].
The effectiveness and efficacy of LSM using biological larviciding have been demonstrated elsewhere in Africa [200,201,202,203,204,205,206,207], however, more data is needed to demonstrate the impact of this tool in the SAR in the context of malaria elimination.
Repellents may provide a personal protection solution during outdoor activities . In SAR, there is a paucity of research studies on repellents for personal or space protection. The very few studies available are spaced over time and are of small scale within controlled conditions ranging from mosquito coils to spatial repellents [95, 136, 166]. In the recent decade, spatial repellents are being assessed for integrated vector management, but limitations exist in the residual effect of the repellent and the need for external power or heat for the diffusion of the volatiles .
Intervention acceptance and uptake
Community acceptance, ownership, and perceived effectiveness of vector control tools have been rarely conducted in the reviewed countries (Mozambique [59, 85], Zambia [57, 97]) In Zambia, despite the members of the community knowing that bed nets are useful in reducing the frequency of getting malaria, very few of those questioned owned a bed net . Thus, such studies could be a starting point for the further expansion of an integrated approach to vector control in these countries.
Insecticides and resistance
Insecticides used or tested for malaria control in SAR include pyrethroids, carbamates and organochlorides. These insecticides have been used for IRS and in LLINs. Despite a high reliance on insecticides for the control of malaria vectors for decades, insecticide resistance is not well documented, with few reports from Mozambique [55, 56, 60, 62, 64, 65, 74, 83, 90, 208], Zimbabwe [121, 165, 169, 170] and Zambia [110, 111, 121, 122, 143], one from Botswana . Information from Eswatini and Namibia is lacking altogether. For effective management and control of insecticide resistance in malaria vectors, frequent detection and monitoring of vector susceptibility and associated resistance mechanisms are crucial . An. funestus has been reported to be resistant to pyrethroids [60, 62, 64, 111, 121, 143, 208], and the carbamate bendiocarb . Low-level resistance to the carbamate propoxur in An. arabiensis has been reported in Mozambique , while resistance to DDT and the pyrethroids was detected in An. gambiae s.s. [111, 122]. Resistance mechanisms are largely unknown, with one report on the genotypic presence of target site mutation (knockdown resistance)  and a few on metabolic resistance associated with elevated p450 monooxygenase activity and acetylcholinesterase levels [60, 143, 208].
This review chronicles the vector research and control activities in six countries of the SAR for almost six decades starting from 1963 to 2021. Much of the literature was generated during the past two decades (2000–2021). There has been very little entomological research in the reviewed SAR countries before 2000, with just one publication per year in Mozambique, Zimbabwe, or Zambia. As the SAR had set goals for malaria elimination and in some countries such as Eswatini, Botswana and Namibia failing to meet their elimination targets of 2020, it will be necessary for these countries to update the knowledgebase of vector research and control by conducting routine entomological (vector) surveillance and evaluation. The historical literature generated may not hold as environmental landscapes continue to change.
Within the context of malaria elimination, the value of understanding the distribution and ecology of local malaria vectors and their ability to sustain malaria transmission cannot be understated. This review found that literature on malaria vector behaviour and control in the reviewed regions is limited, out of date or non-existing at all as for Namibia and Eswatini. However, the studies identified and reviewed herein provide a useful starting point for identifying the gaps and setting goals for future research areas.
SAR is large in a geographical context and extremely heterogeneous and fragmented with countries having distinct environments with a highly marked relief. The geographic landscape and topology differ from one country to the next and some even differ from one micro-district to the next within a country. Furthermore, the climate includes a range from semi-arid savanna to tropic with extreme differences in rainfall. For instance, the characterization of breeding sites differed for the vector An. arabiensis in Botswana [42, 43] and Zambia , thus highlighting the importance of local knowledge for proper planning of vector control activities such as larval source management. The human environment is equally varied, from the housing structures, human movement across borders, economic activities, traditions, and socio-demographics. This heterogeneity complicates the control and elimination of malaria in the region, especially where cross-border transmission is important.
The scarcity of ecological vector research data hampers the potential exploration of novel intervention strategies, such as genetic control tools. The few studies investigating vector bionomics in the region, seem to suggest that there are more vectors involved in malaria transmission, than the primary malaria vectors An. funestus, An. arabiensis and An. gambiae. The absence of data from Namibia and Eswatini in this context is therefore even more surprising. Overall, publications were found to be very limited in scale, usually associated with the presence of research institutions in a few selected areas. This eco-epidemiological bias poses the question of whether the local vector profile is representative of the country. While it is generally thought that An. arabiensis tends toward exophilic and exophagic , results reported in this review demonstrated a regional difference in behaviour. These results suggest entomological efforts to reduce transmission could benefit from different vector control approaches appropriate for the local situation.
A major challenge for improved vector control in the region is the selection and combination of appropriate strategies that will efficiently provide the maximum impact for malaria elimination. In the reviewed countries, the impact of IRS to reduce malaria transmission has not been meticulously monitored, so it is difficult to unequivocally state the extent of the impact and the potential gaps. The current evidence is limited to a few localities [96, 114], however, more robust studies are needed. It is important to note that acceptance and coverage of IRS achieved during earlier vector control campaigns may not be reproducible due to community fatigue and change to other social demographics like an increase in income leading to the building of more modern houses thus refusing IRS. However, national coverage may not be required for the elimination and focal application of IRS to malaria-endemic areas or reporting epidemics may be achievable. It is however likely, that impact would benefit from combinations of tools and the addition of strategies that are less dependent on the currently used insecticides.
The impact and effectiveness of LLINs have been demonstrated in sub-Sahara Africa . There is potentially room to increase coverage of LLINs as IRS is only used for targeted hotspots. Like IRS, to achieve malaria elimination in SAR, focal use of LLINs may be a good approach. New insecticides are being introduced to be used in IRS, such as neonicotinoid Clothianidin, however, they have not been evaluated in the SAR, thus the need to explore these new molecules in the context of tackling insecticide resistance and achieving malaria elimination.
The lack or rather scarcity of entomological information in the SAR stems from a lack of resources, both human and infrastructure. There is a need to improve SAR entomological surveillance capacity within countries and across the border as this region is interconnected via many aspects. The paucity of data in Eswatini, Namibia and Botswana could be a result of the absence of local capacity in both human and infrastructure to conduct entomological surveys. The need to build entomological capacity at the national level requires significant financial and technical investment. However, vector control interventions will have the greatest impact when implemented based on real-time data. As SAR makes progress in eliminating malaria, it will be challenging to measure the impact as fewer cases will be detected. Serological approaches that measure malaria and mosquito exposure might be useful additional surveillance methods.
Whether widespread or focal insecticide-based interventions are used, malaria vector populations will have to be monitored for insecticide resistance. The existing data is insufficient for some of the reviewed countries. There is an urgent need to establish national insecticide resistance detection and monitoring plans, which are crucial for maintaining the efficacy of the current tool.
For sustainability of the currently implemented strategies (IRS and LLINs), there is a need to assess the cost-effectiveness as well as the timely deployment. One of the setbacks in IRS implementation in the SAR is logistics involving delays in shipments thus receiving insecticides when the spraying season is over or when the insecticides have expired [195, 212]. The financial and technical cost needs a thorough assessment to drive malaria transmission down to zero while these approaches should be judiciously considered and supported by both government and donors to achieve the goal of malaria elimination.
New vector control approaches  and new strategies  are gaining more interest; therefore, consideration should be made for these interventions. Some activities that may have an immediate impact on SAR include (1) house screening to prevent mosquito entry into homes [214, 215]; (2) LSM using biological larvicide targeting immature stages of mosquitoes ; and (3) the re-emerging strategy The Global vector control response 2017–2030 (GVCR) emphasises increased capacity, improved surveillance, better coordination and integrated action across sectors and diseases .
This review had some limitations. The review focused on peer-reviewed publications in the PubMed search engine, thus most of the entomological surveillance reports that are on national malaria programmes of these countries were excluded because they were not published. The exclusion of these reports was on the scientific merits of data in peer-reviewed publications. Whilst not peer-reviewed these documents such as annual reports and strategic documents could have provided information on routine surveillance or operational research in entomology if any available, that could support some of the programmatic decisions such as their choice of insecticide for their IRS campaigns.
The review aimed to assess the current knowledge and highlight gaps that need further research attention to strengthen evidence-based decision-making toward malaria elimination. The reviewed data was derived from peer-reviewed publications mostly from the second-line countries for malaria elimination as opposed to the first-line countries for malaria elimination. The review reveals a dearth of information about malaria vectors and their control, most noticeable among the frontline elimination countries: Namibia, Eswatini and Botswana. It is of paramount importance that malaria vector research capacity and routine entomological monitoring and evaluation are strengthened to enhance decision-making, considering changing vector bionomics and insecticide resistance, among other determinants of malaria vector control. The paucity of data for Namibia and Eswatini calls for exploration of contributing factors thus calling for further reviews on local capacity in both human and infrastructure. Entomological surveillance provides the foundation necessary to optimize vector control strategies and is crucial for the malaria elimination success in SAR.
Availability of data and materials
Information was searched and obtained from published data in the PubMed search engine. The datasets used and/or analysed during this study can be obtained from the corresponding author on reasonable request.
Indoor residual spraying
Integrated vector management
Long-lasting Insecticidal Nets
Larval source management
Southern African Development Community
Southern Africa Region
World Health Organization
World Health Organization (WHO). A global malaria control strategy. Geneva: World Health Organization; 1993.
SADC. Strategic plan to fight against malaria in the region Southern African Development Community Ministers of Health. 2007.
SADC. Windhoek declaration on eliminating malaria in the SADC region—2018. Windhoek; 2018.
Mabaso MLH, Sharp B, Lengeler C. Historical review of malarial control in southern African with emphasis on the use of indoor residual house-spraying. Trop Med Int Health. 2004. https://doi.org/10.1111/j.1365-3156.2004.01263.x.
Kouznetsov RL. Malaria control by application of indoor spraying of residual insecticides in tropical Africa and its impact on community health. Trop Dr. 1977. https://doi.org/10.1177/004947557700700216.
Alves W, Blair DM. Malaria control in southern Rhodesia. J Trop Med Hyg. 1955;58:12.
Alves W, Blair DM. An experiment in the control of malaria and bilharziasis. Trans R Soc Trop Med Hyg. 1953. https://doi.org/10.1016/0035-9203(53)90052-2.
Packard RM. Maize, cattle and mosquitoes: the political economy of malaria epidemics in colonial Swaziland. J Afr Hist. 1984;25:189–212.
Taylor P, Mutambu SL. A review of the malaria situation in Zimbabwe with special reference to the period 1972–1981. Trans R Soc Trop Med Hyg. 1986. https://doi.org/10.1016/0035-9203(86)90185-9.
de Meillon B. Malaria survey of South-West Africa. Bull World Health Organ. 1951;4:3.
Wilson DB, Garnham PC, Swellengrebel NH. A review of hyperendemic malaria. Trop Dis Bull. 1950;47:8.
Swellengrebel NH, Annecke S, De Meillon B. Malaria investigations in some parts of the Transvaal and Zululand. J Am Med Assoc. 1931;97:25.
Mastbaum O. Past and present position of malaria in Swaziland. J Trop Med Hyg. 1957;60:5.
Mastbaum O. Clinical and on entomological surveys in Botswana: report by the Chief Medical Officer. 1944.
Soeiro A. Malaria in Mozambique with a special reference to its control in a mainly urban region (Lorenzo Marcus) and in a mainly rural region (Lumpompo valley). 1956.
Sharp BL, le Sueur D. Malaria in South Africa—the past, the present and selected implications for the future. S Afr Med J. 1996;86:83–9.
Caccone A, Marcondes CB, Sallum MAM, Forattini OP, Russello MA, Costa J, et al. Historical analysis of a near disaster: Anopheles gambiae in Brazil. Am J Trop Med Hyg. 2018;78:176–8.
Freedman ML. Malaria control. Gaborone: The Botswana National Archives and Records Services; 1953.
Hansford CF. Malaria control in Namibia. 1990.
Redditt V, ole-MoiYoi K, Rodriguez W, Rosenberg J, Weintraub R. Case in global health delivery: malaria control in Zambia. Boston: Harvard Business Publication; 2012.
National Malaria Elimination Programme. Republic of Zambia Ministry of Health. 2018.
Bouma A. Malaria in Mozambique—what had been done to control epidemics. 1996.
Schwalbach JFL, De La Maza MC. A malaria em Mozambique (1937–1973). 1985.
Ferreira MJ. Report on malaria in Mozambique: analysis of the epidemiology, feasibility and planning of a malaria eradication campaign. Geneva: World Health Organization; 1958. (Unpublished document).
Flint MES, Harrison MJS. DDT impact assessment project, Zimbabwe. 1998. https://www.gov.uk/government/publications/ddt-impact-assessment-project-zimbabwe-ev621s. Accessed 1 June 2021.
Maharaj R, Moonasar D, Baltazar C, Kunene S, Morris N. Sustaining control: lessons from the Lubombo spatial development initiative in southern Africa. Malar J. 2016. https://doi.org/10.1186/s12936-021-03699-x.
Durrheim DN, Ridl FC, Morris N, Seocharan I, Kunene S, Grange JJPLA, et al. Seven years of regional malaria control collaboration—Mozambique, South Africa, and Swaziland. Am J Trop Med Hyg. 2007;76:42–7.
Nkya TE, Fillinger U, Dlamini M, Sangoro OP, Marubu R, Zulu Z, et al. Malaria in Eswatini, 2012–2019: a case study of the elimination effort. Malar J. 2021. https://doi.org/10.1186/s12936-021-03699-x.
Kgoroebutswe TK, Makate N, Fillinger U, Mpho M, Segoea G, Sangoro PO, Mutero CM, Chanda E, Ntebela D, Mogopa M, Mosweunyane T, Nkya TE. Vector control for malaria elimination in Botswana: progress, gaps and opportunities. Malar J. 2020. https://doi.org/10.1186/s12936-020-03375-6.
Antonio-Nkondjio C, Sonhafouo-Chiana N, Ngadjeu CS, Doumbe-Belisse P, Talipouo A, Djamouko-Djonkam L, et al. Review of the evolution of insecticide resistance in main malaria vectors in Cameroon from 1990 to 2017. Parasites Vectors. 2017. https://doi.org/10.1186/s13071-017-2417-9.
WHO. Global vector control response 2017–2030. Geneva: World Health Organization; 2017.
Snow RW, Amratia P, Kabaria CW, Noor AM, Marsh K. The changing limits and incidence of malaria in Africa 1939–2009. Adv Parasitol. 2012. https://doi.org/10.1016/B978-0-12-394303-3.00010-4.
Chirebvu E, Chimbari MJ. Characteristics of Anopheles arabiensis larval habitats in Tubu village, Botswana. J Vector Ecol. 2015. https://doi.org/10.1111/jvec.12141.
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. https://doi.org/10.1186/s12936-016-1642-6.
Tawe L, Ramatlho P, Waniwa K, Muthoga CW, Makate N, Ntebela DS, et al. Preliminary survey on Anopheles species distribution in Botswana shows the presence of Anopheles gambiae and Anopheles funestus complexes. Malar J. 2017. https://doi.org/10.1186/s12936-017-1756-5.
Cornel AJ, Lee Y, Almeida APG, Johnson T, Mouatcho J, Venter M, et al. Mosquito community composition in South Africa and some neighboring countries. Parasites Vectors. 2018. https://doi.org/10.1186/s13071-018-2824-6.
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? Public Health Action. 2018. https://doi.org/10.5588/pha.17.0012.
Erlank E, Koekemoer LL, Coetzee M. The importance of morphological identification of African anopheline mosquitoes (Diptera: Culicidae) for malaria control programmes. Malar J. 2018. https://doi.org/10.1186/s12936-018-2189-5.
Kgoroebutswe TK, Ramatlho P, Reeder S, Makate N, Paganotti GM. Distribution of Anopheles mosquito species, their vectorial role and profiling of knock-down resistance mutations in Botswana. Parasitol Res. 2020. https://doi.org/10.1007/s00436-020-06614-6.
Buxton M, Wasserman RJ, Nyamukondiwa C. Spatial Anopheles arabiensis (Diptera: Culicidae) insecticide resistance patterns across malaria-endemic regions of Botswana. Malar J. 2020. https://doi.org/10.1186/s12936-020-03487-z.
Buxton M, Machekano H, Gotcha N, Nyamukondiwa C, Wasserman RJ. Are vulnerable communities thoroughly informed on mosquito bio-ecology and burden? Int J Environ Res Public Health. 2020. https://doi.org/10.3390/ijerph17218196.
Buxton M, Wasserman RJ, Nyamukondiwa C. Disease vector relative spatio-temporal abundances to water bodies and thermal fitness across Malaria endemic Semi-Arid areas. J Med Entomol. 2021. https://doi.org/10.1093/jme/tjaa221.
Chirebvu E, Chimbari MJ. Characterization of an indoor-resting population of Anopheles arabiensis (Diptera: Culicidae) and the implications on malaria transmission in Tubu village in Okavango Subdistrict, Botswana. J Med Entomol. 2016. https://doi.org/10.1093/jme/tjw024.
Hlongwana KW, Mabaso MLH, Kunene S, Govender D, Maharaj R. Community knowledge, attitudes and practices (KAP) on malaria in Swaziland: a country earmarked for malaria elimination. Malar J. 2009. https://doi.org/10.1186/1475-2875-8-29.
Dlamini SN, Franke J, Vounatsou P. Assessing the relationship between environmental factors and malaria vector breeding sites in Swaziland using multi-scale remotely sensed data. Geospat Health. 2015. https://doi.org/10.4081/gh.2015.302.
Dlamini SV, Liao CW, Dlamini ZH, Siphepho JS, Cheng PC, Chuang TW, et al. Knowledge of human social and behavioral factors essential for the success of community malaria control intervention programs: the case of Lomahasha in Swaziland. J Microbiol Immunol Infect. 2017. https://doi.org/10.4081/gh.2015.302.
Chanda E, Arshad M, Khaloua A, Zhang W, Namboze J, Uusiku P, et al. An investigation of the Plasmodium falciparum malaria epidemic in Kavango and Zambezi regions of Namibia in 2016. Trans R Soc Trop Med Hyg. 2018. https://doi.org/10.1093/trstmh/try097.
Zharov AA. Observations on malaria vectors in Mozambique. I. The status of Anopheles populations before the start of mosquito control. Meditsinskaya Parazitologiya i Parazitarnye Bolezni. 1992;3:23–8.
Crook SE, Baptista A. The effect of permethrin-impregnated wall-curtains on malaria transmission and morbidity in the suburbs of Maputo, Mozambique. Trop Geogr Med. 1995;47:64–7.
Thompson R, Begtrup K, Cuamba N, Dgedge M, Mendis C, Gamage-Mendis A, et al. The Matola malaria project: a temporal and spatial study of malaria transmission and disease in a suburban area of Maputo, Mozambique. Am J Trop Med Hyg. 1997. https://doi.org/10.4269/ajtmh.1997.57.550.
Mendis C, Jacobsen JL, Gamage-Mendis A, Bule E, Dgedge M, Thompson R, et al. Anopheles arabiensis and An. funestus are equally important vectors of malaria in Matola coastal suburb of Maputo, southern Mozambique. Med Vet Entomol. 2000. https://doi.org/10.1046/j.1365-2915.2000.00228.x.
Charlwood JD, Thompson R, Madsen H. Observations on the swarming and mating behaviour of Anopheles funestus from southern Mozambique. Malar J. 2003. https://doi.org/10.1186/1475-2875-2-2.
Maharaj R, Casimiro S, Mthembu SD, Sharp BL. The residual life of bendiocarb: a field-based evaluation from Mozambique. J Med Entomol. 2004. https://doi.org/10.1603/0022-2585-41.1.130.
Aranda C, Aponte JJ, Saute F, Casimiro S, Pinto J, Sousa C, et al. Entomological characteristics of malaria transmission in Manhiça, a rural area in southern Mozambique. J Med Entomol. 2005. https://doi.org/10.1093/jmedent/42.2.180.
Casimiro S, Coleman M, Hemingway J, Sharp B. Insecticide resistance in Anopheles arabiensis and Anopheles gambiae from Mozambique. J Med Entomol. 2006. https://doi.org/10.1093/jmedent/43.2.276.
Casimiro SLR, Hemingway J, Sharp BL, Coleman M. Monitoring the operational impact of insecticide usage for malaria control on Anopheles funestus from Mozambique. Malar J. 2007. https://doi.org/10.1186/1475-2875-6-142.
Chase C, Sicuri E, Sacoor C, Nhalungo D, Nhacolo A, Alonso PL, et al. Determinants of household demand for bed nets in a rural area of southern Mozambique. Malar J. 2009. https://doi.org/10.1186/1475-2875-8-132.
Cuamba Nelson MC. The role of Anopheles merus in malaria transmission in an area of southern Mozambique. Mozamb J Vector Borne Dis. 2009. https://doi.org/10.1016/j.socscimed.2010.01.020.
Montgomery CM, Munguambe K, Pool R. Group-based citizenship in the acceptance of indoor residual spraying (IRS) for malaria control in Mozambique. Soc Sci Med. 2010. https://doi.org/10.1371/journal.pone.0011010.
Cuamba N, Morgan JC, Irving H, Steven A, Wondji CS. High level of pyrethroid resistance in an Anopheles funestus population of the Chokwe district in Mozambique. PLoS ONE. 2010. https://doi.org/10.1371/journal.pone.0011010.
MacEdo De Oliveira A, Wolkon A, Krishnamurthy R, Erskine M, Roberts J, Sate F. Ownership and usage of insecticide-treated bed nets after free distribution via a voucher system in two provinces of Mozambique. Malar J. 2010. https://doi.org/10.1186/1475-2875-9-222.
Coleman M, Abilio AP, Kleinschmidt I, Rehman AM, Cuamba N, Ramdeen V, et al. The emergence of insecticide resistance in central Mozambique and potential threat to the successful indoor residual spraying malaria control programme. Malar J. 2011. https://doi.org/10.1186/1475-2875-10-110.
Munguambe K, Pool R, Montgomery C, Bavo C, Nhacolo A, Fiosse L, et al. What drives community adherence to indoor residual spraying (IRS) against malaria in Manhiça district, rural Mozambique: a qualitative study. Malar J. 2011. https://doi.org/10.1186/1475-2875-10-344.
Kloke RG, Nhamahanga E, Hunt RH, Coetzee M. Vectorial status and insecticide resistance of Anopheles funestus from a sugar estate in southern Mozambique. Parasites Vectors. 2011. https://doi.org/10.1186/1756-3305-4-16.
Wondji CS, Dabire RK, Tukur Z, Irving H, Djouaka R, Morgan JC. Identification and distribution of a GABA receptor mutation conferring dieldrin resistance in the malaria vector Anopheles funestus in Africa. Insect Biochem Mol Biol. 2011. https://doi.org/10.1016/j.ibmb.2011.03.012.
Kampango A, Cuamba N, Charlwood JD. Does moonlight influence the biting behaviour of Anopheles funestus? Med Vet Entomol. 2011. https://doi.org/10.1111/j.1365-2915.2010.00917.x.
Charlwood JD, Tomás EVE. Do developing malaria parasites manipulate their mosquito host? Evidence from infected Anopheles funestus (Giles) from Mozambique. Trans R Soc Trop Med Hyg. 2011. https://doi.org/10.1016/j.trstmh.2011.02.006.
Charlwood JD. Studies on the bionomics of male Anopheles gambiae Giles and male Anopheles funestus Giles from southern Mozambique. J Vector Ecol. 2011. https://doi.org/10.1111/j.1948-7134.2011.00179.x.
Kampango A, Bragança M, de Sousa B, Charlwood JD. Netting barriers to prevent mosquito entry into houses in southern Mozambique: a pilot study. Malar J. 2013. https://doi.org/10.1186/1475-2875-12-99.
Charlwood JD, Macia GA, Manhaca M, Sousa B, Cuamba N, Bragança M. Population dynamics and spatial structure of human-biting mosquitoes, inside and outside of houses, in the Chockwe irrigation scheme, southern Mozambique. Geospat Health. 2013. https://doi.org/10.4081/gh.2013.89.
Charlwood JD, Cuamba N, Tomás EV, Briët OJ. Living on the edge: a longitudinal study of Anopheles funestus in an isolated area of Mozambique. Malar J. 2013. https://doi.org/10.1186/1475-2875-12-208.
Plucinski MM, Chicuecue S, Macete E, Colborn J, Yoon SS, Patrick Kachur S, et al. Evaluation of a universal coverage bed net distribution campaign in four districts in Sofala Province, Mozambique. Malar J. 2014. https://doi.org/10.1186/1475-2875-13-427.
Abílio AP, Marrune P, de Deus N, Mbofana F, Muianga P, Kampango A. Bio-efficacy of new long-lasting insecticide-treated bed nets against Anopheles funestus and Anopheles gambiae from central and northern Mozambique. Malar J. 2015. https://doi.org/10.1186/s12936-015-0885-y.
Glunt KD, Abílio AP, Bassat Q, Bulo H, Gilbert AE, Huijben S, et al. Long-lasting insecticidal nets no longer effectively kill the highly resistant Anopheles funestus of southern Mozambique. Malar J. 2015. https://doi.org/10.1186/s12936-015-0807-z.
Plucinski MM, Chicuecue S, Macete E, Chambe GA, Muguande O, Matsinhe G, et al. Sleeping arrangements and mass distribution of bed nets in six districts in central and northern Mozambique. TM & IH. 2015. https://doi.org/10.1111/tmi.12596.
Quive IM, Candrinho B, Geelhoed D. Household survey of availability of long-lasting insecticide-treated nets and its determinants in rural Mozambique. Malar J. 2015. https://doi.org/10.1186/s12936-015-0811-3.
Morgan J, Abílio AP, do Rosario Pondja M, Marrenjo D, Luciano J, Fernandes G, et al. Physical durability of two types of long-lasting insecticidal nets (LLINs) three years after a mass LLIN distribution campaign in Mozambique, 2008–2011. Am J Trop Med. 2015. https://doi.org/10.4269/ajtmh.14-0023.
Vanden Eng JL, Chan A, Abílio AP, Wolkon A, Ponce De Leon G, Gimnig J, et al. Bed net durability assessments: exploring a composite measure of net damage. PLoS ONE. 2015. https://doi.org/10.1371/journal.pone.0128499.
Arroz JAH, Chirrute F, Mendis C, Chande MH, Kollhoff V. Assessment on the ownership and use of mosquito nets in Mozambique. Rev Saude Publica. 2016. https://doi.org/10.1590/S1518-8787.2016050006335.
Moon TD, Hayes CB, Blevins M, Lopez ML, Green AF, González-Calvo L, et al. Factors associated with the use of mosquito bed nets: results from two cross-sectional household surveys in Zambézia Province, Mozambique. Malar J. 2016. https://doi.org/10.1186/s12936-016-1250-5.
Charlwood JD. Some like it hot: a differential response to changing temperatures by the malaria vectors Anopheles funestus and An. gambiae s.l. PeerJ. 2017. https://doi.org/10.7717/peerj.3099.
Arroz JAH, Mendis C, Pinto L, Candrinho B, Pinto J, Martins MDRO. Implementation strategies to increase access and demand of long-lasting insecticidal nets: a before-and-after study and scale-up process in Mozambique. Malar J. 2017. https://doi.org/10.1186/s12936-017-2086-3.
Riveron JM, Huijben S, Tchapga W, Tchouakui M, Wondji MJ, Tchoupo M, et al. Escalation of pyrethroid resistance in the malaria vector Anopheles funestus induces a loss of efficacy of piperonyl butoxide-based insecticide-treated nets in Mozambique. J Infect Dis. 2019. https://doi.org/10.1093/infdis/jiz139.
Oxborough RM, Seyoum A, Yihdego Y, Dabire R, Gnanguenon V, Wat’Senga F, et al. Susceptibility testing of Anopheles malaria vectors with the neonicotinoid insecticide clothianidin; results from 16 African countries, in preparation for indoor residual spraying with new insecticide formulations. Malar J. 2019. https://doi.org/10.1186/s12936-019-2888-6.
Magaço A, Botão C, Nhassengo P, Saide M, Ubisse A, Chicumbe S, et al. Community knowledge and acceptance of indoor residual spraying for malaria prevention in Mozambique: a qualitative study. Malar J. 2019. https://doi.org/10.1186/s12936-019-2653-x.
Arroz JAH, Candrinho B, Mendis C, Lopez M, Martins MDRO. Cost-effectiveness of two long-lasting insecticidal nets delivery models in mass campaign in rural Mozambique. BMC Res Notes. 2019. https://doi.org/10.1186/s13104-019-4620-6.
Kaddumukasa MA, Wright J, Muleba M, Stevenson JC, Norris DE, Coetzee M. Genetic differentiation and population structure of Anopheles funestus from Uganda and the southern African countries of Malawi, Mozambique, Zambia and Zimbabwe. Parasites Vectors. 2020. https://doi.org/10.1186/s13071-020-3962-1.
Abílio AP, Obi E, Koenker H, Babalola S, Saifodine A, Zulliger R, et al. Monitoring the durability of the long-lasting insecticidal nets MAGNet and Royal Sentry in three ecological zones of Mozambique. Malar J. 2020. https://doi.org/10.1186/s12936-020-03282-w.
Galatas B, Saúte F, Martí-Soler H, Guinovart C, Nhamussua L, Simone W, et al. A multiphase program for malaria elimination in southern Mozambique (the Magude project): a before-after study. PLoS Med. 2020. https://doi.org/10.1371/journal.pmed.1003227.
Wagman JM, Varela K, Zulliger R, Saifodine A, Muthoni R, Magesa S, et al. Reduced exposure to malaria vectors following indoor residual spraying of pirimiphos-methyl in a high-burden district of rural Mozambique with high ownership of long-lasting insecticidal nets: entomological surveillance results from a cluster-randomized trial. Malar J. 2021. https://doi.org/10.1186/s12936-021-03583-8.
Chaccour C, Zulliger R, Wagman J, Casellas A, Nacima A, Elobolobo E, et al. Incremental impact on malaria incidence following indoor residual spraying in a highly endemic area with high standard ITN access in Mozambique: results from a cluster-randomized study. Malar J. 2021. https://doi.org/10.1186/s12936-021-03611-7.
Muspratt J. Destruction of the larvae of Anopheles gambiae giles by a Coelomomyces fungus. Bull World Health Organ. 1963;29:81–6.
Bransby-Williams WR. House catches of adult Anopheles gambiae species B in two areas of Zambia. East Afr Med J. 1979;56:557–61.
Ziba MM. Preliminary laboratory trial of Neem on Anopheles and Culex larvae in Zambia. Cent Afr J Med. 1995;41:137–8.
Lukwa N, Chandiwana SK. Efficacy of mosquito coils containing 0.3% and 0.4% pyrethrins against An. gambiae sensu lato mosquitoes. Cent Afr J. 1998;44:104–7.
Sharp B, van Wyk P, Sikasote JB, Banda P, Kleinschmidt I. Malaria control by residual insecticide spraying in Chingola and Chililabombwe, Copperbelt Province, Zambia. TM & IH. 2002. https://doi.org/10.1046/j.1365-3156.2002.00928.x.
Elphick H, Elphick D. Factors that contribute to the low use of bed nets in a malaria endemic zone of sub-Saharan Africa: a questionnaire survey in a rural population in Zambia. Cent Afr J Med. 2003;49:87–9.
Kent RJ, Coetzee M, Mharakurwa S, Norris DE. Feeding and indoor resting behaviour of the mosquito Anopheles longipalpis in an area of hyperendemic malaria transmission in southern Zambia. Med Vet Entomol. 2006. https://doi.org/10.1111/j.1365-2915.2006.00646.x.
Lehmann T, Licht M, Elissa N, Maega BTA, Chimumbwa JM, Watsenga FT, et al. Population structure of Anopheles gambiae in Africa. J Hered. 2003. https://doi.org/10.1093/jhered/esg024.
Baume CA, Marin MC. Intra-household mosquito net use in Ethiopia, Ghana, Mali, Nigeria, Senegal, and Zambia: are nets being used? Who in the household uses them? Am J Trop Med Hyg. 2007;77:963–71.
Kent RJ, Mharakurwa S, Norris DE. Spatial and temporal genetic structure of Anopheles arabiensis in southern Zambia over consecutive wet and drought years. Am J Trop Med Hyg. 2007;77:316.
Kent RJ, Thuma PE, Mharakurwa S, Norris DE. Seasonality, blood feeding behavior, and transmission of Plasmodium falciparum by Anopheles arabiensis after an extended drought in southern Zambia. Am J Trop Med Hyg. 2007;76:267–74.
Baume CA, Marin MC. Gains in awareness, ownership and use of insecticide-treated nets in Nigeria, Senegal, Uganda and Zambia. Malar J. 2008;7:1–10.
Fornadel CM, Norris LC, Glass GE, Norris DE. Analysis of Anopheles arabiensis blood feeding behavior in southern Zambia during the two years after introduction of insecticide-treated bed nets. Am J Trop Med Hyg. 2010. https://doi.org/10.1186/1475-2875-7-153.
Clennon JA, Kamanga A, Musapa M, Shiff C, Glass GE. Identifying malaria vector breeding habitats with remote sensing data and terrain-based landscape indices in Zambia. Int J Health Geogr. 2010. https://doi.org/10.1186/1476-072X-9-58.
Fornadel CM, Norris LC, Norris DE. Centers for disease control light traps for monitoring Anopheles arabiensis human biting rates in an area with low vector density and high insecticide-treated bed net use. Am J Trop Med Hyg. 2010. https://doi.org/10.4269/ajtmh.2010.10-0088.
Tuba M, Sandoy IF, Bloch P, Byskov J. Fairness and legitimacy of decisions during delivery of malaria services and ITN interventions in Zambia. Malar J. 2010. https://doi.org/10.1186/1475-2875-9-309.
Norris LC, Fornadel CM, Hung WC, Pineda FJ, Norris DE. Frequency of multiple blood meals taken in a single gonotrophic cycle by Anopheles arabiensis mosquitoes in Macha, Zambia. Am J Trop Med Hyg. 2010. https://doi.org/10.4269/ajtmh.2010.09-0296.
Fornadel CM, Norris LC, Franco V, Norris DE. Unexpected anthropophily in the potential secondary malaria vectors Anopheles coustani s.l. and Anopheles squamosus in Macha, Zambia. Vector Borne Zoonotic Dis. 2011. https://doi.org/10.1089/vbz.2010.0082.
Norris LC, Norris DE. Efficacy of long-lasting insecticidal nets in use in Macha, Zambia, against the local Anopheles arabiensis population. Malar J. 2011. https://doi.org/10.1186/1475-2875-10-254.
Chanda E, Hemingway J, Kleinschmidt I, Rehman AM, Ramdeen V, Phiri FN, et al. Insecticide resistance and the future of malaria control in Zambia. PLoS ONE. 2011. https://doi.org/10.1371/journal.pone.0024336.
Chanda E, Baboo KS, Shinondo CJ. Transmission attributes of periurban malaria in Lusaka, Zambia, precedent to the integrated vector management strategy: an entomological input. J Trop Med. 2012. https://doi.org/10.1155/2012/873852.
Seyoum A, Sikaala CH, Chanda J, Chinula D, Ntamatungiro AJ, Hawela M, et al. Human exposure to anopheline mosquitoes occurs primarily indoors, even for users of insecticide-treated nets in Luangwa Valley, South-east Zambia. Parasites Vectors. 2012. https://doi.org/10.1186/1756-3305-5-101.
Chanda E, Coleman M, Kleinschmidt I, Hemingway J, Hamainza B, Masaninga F, et al. Impact assessment of malaria vector control using routine surveillance data in Zambia: implications for monitoring and evaluation. Malar J. 2012. https://doi.org/10.1186/1475-2875-11-437.
Mharakurwa S, Sialumano M, Liu K, Scott A, Thuma P. Selection for chloroquine-sensitive Plasmodium falciparum by wild Anopheles arabiensis in southern Zambia. Malar J. 2013. https://doi.org/10.1186/1475-2875-12-453.
Chanda E, Kandyata A, Chanda J, Phiri FN, Muzia L, Kamuliwo M. The efficacy of vectron 20 WP, etofenprox, for indoor residual spraying in areas of high vector resistance to pyrethroids and organochlorines in Zambia. Prev Med. 2013. https://doi.org/10.5402/2013/371934.
Chanda E, Chanda J, Kandyata A, Phiri FN, Muzia L, Haque U, et al. Efficacy of ACTELLIC 300 CS, pirimiphos methyl, for indoor residual spraying in areas of high vector resistance to pyrethroids and carbamates in Zambia. J Med Entomol. 2013. https://doi.org/10.1603/ME13041.
Sikaala CH, Killeen GF, Chanda J, Chinula D, Miller JM, Russell TL, et al. Evaluation of alternative mosquito sampling methods for malaria vectors in Lowland South–East Zambia. Parasites Vectors. 2013. https://doi.org/10.1186/1756-3305-6-91.
Kamuliwo M, Chanda E, Haque U, Mwanza-Ingwe M, Sikaala C, Katebe-Sakala C, et al. The changing burden of malaria and association with vector control interventions in Zambia using district-level surveillance data, 2006–2011. Malar J. 2013. https://doi.org/10.1186/1475-2875-12-437.
Norris LC, Norris DE. Heterogeneity and changes in inequality of malaria risk after introduction of insecticide-treated bed nets in Macha, Zambia. Am J Trop Med Hyg. 2013. https://doi.org/10.4269/ajtmh.11-0595.
Choi KS, Christian R, Nardini L, Wood OR, Agubuzo E, Muleba M, et al. Insecticide resistance and role in malaria transmission of Anopheles funestus populations from Zambia and Zimbabwe. Parasites Vectors. 2014. https://doi.org/10.1186/s13071-014-0464-z.
Thomsen EK, Strode C, Hemmings K, Hughes AJ, Chanda E, Musapa M, et al. Underpinning sustainable vector control through informed insecticide resistance management. PLoS ONE. 2014. https://doi.org/10.1371/journal.pone.0099822.
Fornadel CM, Norris DE. Increased endophily by the malaria vector Anopheles arabiensis in southern Zambia and identification of digested blood meals. Am J Trop Med Hyg. 2008;79:876–80.
Mukonka VM, Chanda E, Haque U, Kamuliwo M, Mushinge G, Chileshe J, et al. High burden of malaria following scale-up of control interventions in Nchelenge District, Luapula Province, Zambia. Malar J. 2014. https://doi.org/10.1186/1475-2875-13-153.
Sikaala CH, Chinula D, Chanda J, Hamainza B, Mwenda M, Mukali I, et al. A cost-effective, community-based, mosquito-trapping scheme that captures spatial and temporal heterogeneities of malaria transmission in rural Zambia. Malar J. 2014. https://doi.org/10.1186/1475-2875-13-225.
Lobo NF, St. Laurent B, Sikaala CH, Hamainza B, Chanda J, Chinula D, et al. Unexpected diversity of Anopheles species in Eastern Zambia: implications for evaluating vector behavior and interventions using molecular tools. Sci Rep. 2015. https://doi.org/10.1038/srep17952.
Das S, Henning TC, Simubali L, Hamapumbu H, Nzira L, Mamini E, et al. Underestimation of foraging behaviour by standard field methods in malaria vector mosquitoes in southern Africa. Malar J. 2015. https://doi.org/10.1186/s12936-014-0527-9.
Craig AS, Muleba M, Smith SC, Katebe-Sakala C, Chongwe G, Hamainza B, et al. Long-lasting insecticidal nets in Zambia: a cross-sectional analysis of net integrity and insecticide content. Malar J. 2015. https://doi.org/10.1186/s12936-015-0754-8.
Stevenson JC, Pinchoff J, Muleba M, Lupiya J, Chilusu H, Mwelwa I, et al. Spatio-temporal heterogeneity of malaria vectors in northern Zambia: implications for vector control. Parasites Vectors. 2016. https://doi.org/10.1186/s13071-016-1786-9.
Das S, Muleba M, Stevenson JC, Norris DE. Habitat partitioning of malaria vectors in Nchelenge district, Zambia. Am J Trop Med Hyg. 2016. https://doi.org/10.4269/ajtmh.15-0735.
Stevenson JC, Simubali L, Mbambara S, Musonda M, Mweetwa S, Mudenda T, et al. Detection of Plasmodium falciparum infection in Anopheles squamosus (Diptera: Culicidae) in an area targeted for malaria elimination, Southern Zambia. J Med Entomol. 2016. https://doi.org/10.1093/jme/tjw091.
Hamainza B, Sikaala CH, Moonga HB, Chanda J, Chinula D, Mwenda M, et al. Incremental impact upon malaria transmission of supplementing pyrethroid-impregnated long-lasting insecticidal nets with indoor residual spraying using pyrethroids or the organophosphate, pirimiphos methyl. Malar J. 2016. https://doi.org/10.1186/s12936-016-1143-7.
Wang P, Connor AL, Joudeh AS, Steinberg J, Ndhlovu K, Siyolwe M, et al. Community point distribution of insecticide-treated bed nets and community health worker hang-up visits in rural Zambia: a decision-focused evaluation. Malar J. 2016. https://doi.org/10.1186/s12936-016-1165-1.
Das S, Muleba M, Stevenson JC, Pringle JC, Norris DE. Beyond the entomological inoculation rate: characterizing multiple blood feeding behavior and Plasmodium falciparum multiplicity of infection in Anopheles mosquitoes in northern Zambia. Parasites Vectors. 2017. https://doi.org/10.1186/s13071-017-1993-z.
Chinula D, Sikaala CH, Chanda-Kapata P, Hamainza B, Zulu R, Reimer L, et al. Wash-resistance of pirimiphos-methyl insecticide treatments of window screens and eave baffles for killing indoor-feeding malaria vector mosquitoes: an experimental hut trial, South East of Zambia. Malar J. 2018. https://doi.org/10.1186/s12936-018-2309-2.
Stevenson JC, Simubali L, Mudenda T, Cardol E, Bernier UR, Vazquez AA, et al. Controlled release spatial repellent devices (CRDs) as novel tools against malaria transmission: a semi-field study in Macha, Zambia. Malar J. 2018. https://doi.org/10.1186/s12936-018-2558-0.
Jones CM, Lee Y, Kitchen A, Collier T, Pringle JC, Muleba M, et al. Complete Anopheles funestus mitogenomes reveal an ancient history of mitochondrial lineages and their distribution in southern and central Africa. Sci Rep. 2018. https://doi.org/10.1038/s41598-018-27092-y.
Dengela D, Seyoum A, Lucas B, Johns B, George K, Belemvire A, et al. Multi-country assessment of residual bio-efficacy of insecticides used for indoor residual spraying in malaria control on different surface types: results from program monitoring in 17 PMI/USAID-supported IRS countries. Parasites Vectors. 2018. https://doi.org/10.1186/s13071-017-2608-4.
Kanyangarara M, Hamapumbu H, Mamini E, Lupiya J, Stevenson JC, Mharakurwa S, et al. Malaria knowledge and bed net use in three transmission settings in southern Africa. Malar J. 2018. https://doi.org/10.1186/s12936-018-2178-8.
Hast MA, Stevenson JC, Muleba M, Chaponda M, Kabuya JB, Mulenga M, et al. Risk factors for household vector abundance using indoor CDC light traps in a high malaria transmission area of northern Zambia. Am J Trop Med Hyg. 2019. https://doi.org/10.4269/ajtmh.18-0875.
Hast MA, Chaponda M, Muleba M, Kabuya JB, Lupiya J, Kobayashi T, et al. The impact of 3 years of targeted indoor residual spraying with pirimiphos-methyl on malaria parasite prevalence in a high-transmission area of northern Zambia. Am J Epidemiol. 2019. https://doi.org/10.1093/aje/kwz107.
Ciubotariu II, Jones CM, Kobayashi T, Bobanga T, Muleba M, Pringle JC, et al. Genetic diversity of Anopheles coustani (Diptera: Culicidae) in malaria transmission foci in southern and central Africa. J Med Entomol. 2020. https://doi.org/10.1093/jme/tjaa132.
Chanda J, Saili K, Phiri F, Stevenson JC, Mwenda M, Chishimba S, et al. Pyrethroid and carbamate resistance in Anopheles funestus Giles along Lake Kariba in southern Zambia. Am J Trop Med Hyg. 2020. https://doi.org/10.4269/ajtmh.19-0664.
Jumbam DT, Stevenson JC, Matoba J, Grieco JP, Ahern LN, Hamainza B, et al. Knowledge, attitudes and practices assessment of malaria interventions in rural Zambia. BMC Public Health. 2020. https://doi.org/10.1186/s12889-020-8235-6.
Larsen DA, Martin A, Pollard D, Nielsen CF, Hamainza B, Burns M, et al. Leveraging risk maps of malaria vector abundance to guide control efforts reduces malaria incidence in Eastern Province, Zambia. Sci Rep. 2020. https://doi.org/10.1038/s41598-020-66968-w.
Cross DE, Thomas C, McKeown N, Siaziyu V, Healey A, Willis T, et al. Geographically extensive larval surveys reveal an unexpected scarcity of primary vector mosquitoes in a region of persistent malaria transmission in western Zambia. Parasites Vectors. 2021. https://doi.org/10.1186/s13071-020-04540-1.
Hoffman JE, Ciubotariu II, Simubali L, Mudenda T, Moss WJ, Carpi G, et al. Phylogenetic complexity of morphologically identified anopheles squamosus in southern Zambia. Insects. 2021. https://doi.org/10.3390/insects12020146.
Hast MA, Stevenson JC, Muleba M, Chaponda M, Kabuya JB, Mulenga M, et al. The impact of three years of targeted indoor residual spraying with pirimiphos-methyl on household vector abundance in a high malaria transmission area of northern Zambia. Am J Trop Med Hyg. 2021. https://doi.org/10.4269/ajtmh.20-0537.
Green CA. Identifications of member species of the Anopheles gambiae complex in the Zambesi valley. Cent Afr J Med. 1970;16:207–9.
Mpofu SM. Seasonal vector density and disease incidence patterns of malaria in an area of Zimbabwe. Trans R Soc Trop Med Hyg. 1985;79:169–75.
Taylor P, Govere J, Crees MJ. A field trial of microencapsulated deltamethrin, a synthetic pyrethroid, for malaria control. Trans R Soc Trop Med Hyg. 1986;80:537–45.
Mpofu SM, Kanyimo KH, Masendu H. Potential use of bendiocarb (Ficam VC) for malaria control in an area of Zimbabwe. J Am Mosq Control Assoc. 1991;7:536–42.
Murahwa FC, Lukwa N, Govere JM, Masedza C. Do mosquito coils and killer sticks work against Anopheles gambiae sensu lato mosquitoes in Zimbabwe? Cent Afr J Med. 1994;40:122–6.
Lukwa N. Do traditional mosquito repellent plants work as mosquito larvicides? Cent Afr J Med. 1994;40:306–9.
van Geldermalsen AA, Munochiveyi R. Knowledge, attitude and practice (KAP) relating to malaria in Mashonaland Central, Zimbabwe. Cent Afr J Med. 1995;41:10–4.
Vundule C, Mharakurwa S. Knowledge, practices, and perceptions about malaria in rural communities of Zimbabwe: relevance to malaria control. Bull World Health Organ. 1996;74:55–60.
Mpofu SM, Taylor P, Govere J. An evaluation of the residual lifespan of DDT in malaria control. J Am Mosq Control Assoc. 1988;4:529–35.
Lukwa N, Nyazema NZ, Curtis CF, Mwaiko GL, Chandiwana SK. People’s perceptions about malaria transmission and control using mosquito repellent plants in a locality in Zimbabwe. Cent Afr J Med. 1999. https://doi.org/10.4314/cajm.v45i3.8456.
Manokore V, Murahwa FC, Chirebvu E. Absence of insecticide resistance in Anopheles gambiae s.l. (Diptera: Culicidae) after four decades of residual house spraying in Gokwe District, Zimbabwe. J Med Entomol. 2000. https://doi.org/10.1603/0022-2585-37.2.286.
Masendu HT, McClean D, Mushavave ST, Chinyowa D, Simbanegavi P, Chawarika C, et al. Urban malaria transmission in Mutare City; an unlikely phenomenon. Cent Afr J Med. 2000. https://doi.org/10.1603/0022-2585-37.2.286.
Chirebvu E, Nzira L. The efficacy and residual life span of two alphacypermethrin insecticide formulations (fendona 6% suspension concentrate and fendona dry 15%) treated on mosquito bed nets. Cent Afr J Med. 2000. https://doi.org/10.4314/cajm.v46i7.8555.
Tsuyuoka R, Midzi SM, Dziva P, Makunike B. The acceptability of insecticide treated mosquito nets among community members in Zimbabwe. Cent Afr J Med. 2002. https://doi.org/10.4314/cajm.v48i7.8435.
Masendu HT, Nziramasanga N, Muchechemera C. Low insecticide deposit rates detected during routine indoor residual spraying for malaria vector control in two districts of Gokwe, Zimbabwe. J Am Mosq Control Assoc. 2002. https://doi.org/10.4314/cajm.v48i7.8435.
Masendu HT, Hunt RH, Govere J, Brooke BD, Awolola TS, Coetzee M. The sympatric occurrence of two molecular forms of the malaria vector Anopheles gambiae Giles sensu stricto in Kanyemba, in the Zambezi Valley, Zimbabwe. Trans R Soc Trop Med Hyg. 2004. https://doi.org/10.1016/j.trstmh.2003.10.006.
Munhenga G, Masendu HT, Brooke BD, Hunt RH, Koekemoer LK. Pyrethroid resistance in the major malaria vector Anopheles arabiensis from Gwave, a malaria-endemic area in Zimbabwe. Malar J. 2008. https://doi.org/10.1186/1475-2875-7-247.
Lukwa N, Chiwade T. Lack of insecticidal effect of mosquito coils containing either metofluthrin or esbiothrin on Anopheles gambiae sensu lato mosquitoes. Trop Biomed. 2008;25:191–5.
Torr SJ, della Torre A, Calzetta M, Costantini C, Vale GA. Towards a fuller understanding of mosquito behaviour: use of electrocuting grids to compare the odour-orientated responses of Anopheles arabiensis and An. quadriannulatus in the field. Med Vet Entomol. 2008. https://doi.org/10.1111/j.1365-2915.2008.00723.x.
Sande S, Jagals P, Mupeta B, Chadambuka A. An investigation of the use of rectangular insecticide-treated nets for malaria control in Chipinge district, Zimbabwe: a descriptive study. Pan Afr Med J. 2012;13:5.
Lukwa N, Sande S, Makuwaza A, Chiwade T, Netsa M, Asamoa K, et al. Nationwide assessment of insecticide susceptibility in Anopheles gambiae populations from Zimbabwe. Malar J. 2014. https://doi.org/10.1186/1475-2875-13-408.
Sande S, Zimba M, Chinwada P, Masendu HT, Mazando S, Makuwaza A. The emergence of insecticide resistance in the major malaria vector Anopheles funestus (Diptera: Culicidae) from sentinel sites in Mutare and Mutasa Districts, Zimbabwe. Malar J. 2015. https://doi.org/10.1186/s12936-015-0993-8.
Sande S, Zimba M, Chinwada P, Masendu HT, Makuwaza A. Biting behaviour of Anopheles funestus populations in Mutare and Mutasa districts, Manicaland province, Zimbabwe: implications for the malaria control programme. J Vector Borne Dis. 2016;53:789–96.
Sande S, Zimba M, Chinwada P, Masendu HT, Makuwaza A. Insights into resting behavior of malaria vector mosquitoes in Mutare and Mutasa Districts of Manicaland Province, Zimbabwe. J Med Entomol. 2016;53:866–72.
Kanyangarara M, Mamini E, Mharakurwa S, Munyati S, Gwanzura L, Kobayashi T, et al. Reduction in malaria incidence following indoor residual spraying with actellic 300 CS in a setting with pyrethroid resistance: Mutasa District, Zimbabwe. PLoS ONE. 2016. https://doi.org/10.1371/journal.pone.0151971.
Tapera O. Determinants of long-lasting insecticidal net ownership and utilization in malaria transmission regions: evidence from Zimbabwe demographic and health surveys. Malar J. 2019. https://doi.org/10.1186/s12936-019-2912-x.
Dube B, Mberikunashe J, Dhliwayo P, Tangwena A, Shambira G, Chimusoro A, et al. How far is the journey before malaria is knocked out malaria in Zimbabwe: results of the malaria indicator survey 2016. Malar J. 2019. https://doi.org/10.1186/s12936-019-2801-3.
Higgs S, Beaty BJ. Natural cycles of vector-borne pathogens. The biology of disease vectors. Colorado: University Press of Colorado; 2005.
Beier JC. Vector incrimination and entomological inoculation rates. Methods Mol Med. 2002.
Gimmg JE, Ombok M, Kamau L, Hawley WA. Characteristics of larval anopheline (Diptera: Culicidae) habitats in western Kenya. J Med Entomol. 2001. https://doi.org/10.1603/0022-2585-38.2.282.
Li L, Bian L, Yan G. A study of the distribution and abundance of the adult malaria vector in western Kenya highlands. Int J Health Geogr. 2008. https://doi.org/10.1186/1476-072X-7-50.
Nambunga IH, Ngowo HS, Mapua SA, Hape EE, Msugupakulya BJ, Msaky DS, et al. Aquatic habitats of the malaria vector Anopheles funestus in rural south-eastern Tanzania. Malar J. 2020. https://doi.org/10.1186/s12936-020-03295-5.
Mburu MM. Indoor and outdoor biting behaviour of malaria vectors and the potential risk factors that enhance malaria in southern Malawi. Thesis. Wageningen University & Research. 2019.
Rozendaal JA. Mosquitos and other biting Diptera. Vector control: methods for use by individuals and communities. World Health Organization; 1997. https://apps.who.int/iris/handle/10665/41968.
Wilson AL, Courtenay O, Kelly-Hope LA, Scott TW, Takken W, Torr SJ, et al. The importance of vector control for the control and elimination of vector-borne diseases. PLoS Negl Trop Dis. 2020. https://doi.org/10.1371/journal.pntd.0007831.
Killeen GF. Characterizing, controlling and eliminating residual malaria transmission. Malar J. 2014. https://doi.org/10.1186/1475-2875-13-330.
Burke A, Dahan-Moss Y, Duncan F, Qwabe B, Coetzee M, Koekemoer L, et al. Anopheles parensis contributes to residual malaria transmission in South Africa. Malar J. 2019. https://doi.org/10.1186/s12936-019-2889-5.
Perugini E, Guelbeogo WM, Calzetta M, Manzi S, Virgillito C, Caputo B, et al. Behavioural plasticity of Anopheles coluzzii and Anopheles arabiensis undermines LLIN community protective effect in a Sudanese-savannah village in Burkina Faso. Parasites Vectors. 2020. https://doi.org/10.1186/s13071-020-04142-x.
Gordicho V, Vicente JL, Sousa CA, Caputo B, Pombi M, Dinis J, et al. First report of an exophilic Anopheles arabiensis population in Bissau City, Guinea-Bissau: recent introduction or sampling bias? Malar J. 2014. https://doi.org/10.1186/1475-2875-13-423.
Moiroux N, Gomez MB, Pennetier C, Elanga E, Djènontin A, Chandre F, et al. Changes in Anopheles funestus biting behavior following universal coverage of long-lasting insecticidal nets in Benin. J Infect Dis. 2012. https://doi.org/10.1093/infdis/jis565.
Ojuka P, Boum Y, Denoeud-Ndam L, Nabasumba C, Muller Y, Okia M, et al. Early biting and insecticide resistance in the malaria vector Anopheles might compromise the effectiveness of vector control intervention in Southwestern Uganda. Malar J. 2015. https://doi.org/10.1186/s12936-015-0653-z.
Kabbale FG, Akol AM, Kaddu JB, Onapa AW. Biting patterns and seasonality of Anopheles gambiae sensu lato and Anopheles funestus mosquitoes in Kamuli District, Uganda. Parasites Vectors. 2013. https://doi.org/10.1186/1756-3305-6-340.
Dambach P, Schleicher M, Korir P, Ouedraogo S, Dambach J, Sié A, et al. Nightly biting cycles of Anopheles species in rural northwestern Burkina Faso. J Med Entomol. 2018. https://doi.org/10.1093/jme/tjy043.
Kipruto EK, Ochieng AO, Anyona DN, Mbalanya M, Mutua EN, Onguru D, et al. Effect of climatic variability on malaria trends in Baringo County, Kenya. Malar J. 2017. https://doi.org/10.1186/s12936-017-1848-2.
Shililu J, Ghebremeskel T, Seulu F, Mengistu S, Fekadu H, Zerom M, et al. Seasonal abundance, vector behavior, and malaria parasite transmission in Eritrea. J Am Mosq Control Assoc. 2004;20:155–60.
Mawejje HD, Kilama M, Kigozi SP, Musiime AK, Kamya M, Lines J, et al. Impact of seasonality and malaria control interventions on Anopheles density and species composition from three areas of Uganda with differing malaria endemicity. Malar J. 2021. https://doi.org/10.1186/s12936-021-03675-5.
Tangena JAA, Hendriks CMJ, Devine M, Tammaro M, Trett AE, Williams I, et al. Indoor residual spraying for malaria control in sub-Saharan Africa 1997 to 2017: an adjusted retrospective analysis. Malar J. 2020. https://doi.org/10.1186/s12936-020-03216-6.
Fitzgerald L, Wikoff DS. Persistent organic pollutants. In: Encyclopedia of toxicology. 3rd ed. London: Academic Press; 2014.
vandenBilcke C. The Stockholm convention on persistent organic pollutants. Rev Eur Community Int Environ Law. 2002. https://doi.org/10.1111/1467-9388.00331.
WHO. Larval source management: a supplementary measure for malaria vector control. An operational manual. Geneva: World Health Organization; 2013.
Utzinger J, Tozan Y, Singer BH. Efficacy and cost-effectiveness of environmental management for malaria control. Trop Med Int Health. 2001. https://doi.org/10.1046/j.1365-3156.2001.00769.x.
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. https://doi.org/10.1007/s00436-010-2029-1.
Diédhiou SM, Konaté L, Samb B, Niang EA, Sy O, Thiaw O, et al. Effectiveness of three biological larvicides and of an insect growth regulator against Anopheles arabiensis in Senegal. Bull Soc Pathol Exot. 2017. https://doi.org/10.1007/s13149-016-0531-4.
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. https://doi.org/10.1186/s12936-017-2046-y.
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.
Fillinger U, Knols BG, 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. https://doi.org/10.1046/j.1365-3156.2003.00979.x.
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;93:325–9.
Dambach P, Louis VR, Kaiser A, Ouedraogo S, Sié A, Sauerborn R, et al. Efficacy of Bacillus thuringiensis var. israelensis against malaria mosquitoes in northwestern Burkina Faso. Parasites Vectors. 2014. https://doi.org/10.1186/1756-3305-7-371.
Barbazan P, Baldet T, Darriet F, Escaffre H, Djoda DH, Hougard JM. 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.
Casimiro S, Coleman M, Mohloai P, Hemingway J, Sharp B. Insecticide resistance in Anopheles funestus (Diptera: Culicidae) from Mozambique. J Med Entomol. 2006;43:267–75.
Mnzava AP, Knox TB, Temu EA, Trett A, Fornadel C, Hemingway J, et al. Implementation of the global plan for insecticide resistance management in malaria vectors: progress, challenges and the way forward. Malar J. 2015. https://doi.org/10.1186/s12936-015-0693-4.
Mahande A, Mosha F, Mahande J, Kweka E. Feeding and resting behaviour of malaria vector, Anopheles arabiensis with reference to zooprophylaxis. Malar J. 2007. https://doi.org/10.1186/1475-2875-6-100.
Lengeler C. Insecticide-treated bed nets and curtains for preventing malaria. Cochrane Database Syst Rev. 2004. https://doi.org/10.1002/14651858.CD000363.pub2.
Akogbéto MC, Dagnon F, Aïkpon R, Ossé R, Salako AS, Ahogni I, et al. Lessons learned, challenges and outlooks for decision-making after a decade of experience monitoring the impact of indoor residual spraying in Benin, West Africa. Malar J. 2020. https://doi.org/10.1186/s12936-020-3131-1.
The Vector Control Advisory Group. Third meeting of the Vector Control Advisory Group. The Vector Control Advisory Group, Geneva, Switzerland 12–14 November 2014. 2015
Gimnig JE, Slutsker L. House screening for malaria control. Lancet. 2009. https://doi.org/10.1016/S0140-6736(09)61078-3.
Getawen SK, Ashine T, Massebo F, Woldeyes D, Lindtjørn B. Exploring the impact of house screening intervention on entomological indices and incidence of malaria in Arba Minch town, southwest Ethiopia: a randomized control trial. Acta Trop. 2018. https://doi.org/10.1016/j.actatropica.2018.02.009.
Ls T, Thwing J, Sinclair D, Fillinger U, Gimnig J, Ke B, et al. Mosquito larval source management for controlling malaria (Review). Cochrane Database Syst Rev. 2016. https://doi.org/10.1002/14651858.CD008923.pub2.
The authors thank AFRO II National Project Coordinators for Botswana, Namibia, Kingdom of Eswatini, Zambia, Mozambique, and Zimbabwe for their collaboration.
Funding support is acknowledged from the AFRO-II Project under the auspices of the Global Environment Facility/United Nations Environment Programme (GEF/UNEP) through the World Health Organization Regional Office for Africa (WHO-AFRO). We also gratefully acknowledge the financial support by icipe’s core donors, the Foreign, Commonwealth & Development Office (FCDO) of the UK Government; Swedish International Development Cooperation Agency (Sida); the Swiss Agency for Development and Cooperation (SDC); Federal Democratic Republic of Ethiopia; and the Kenyan Government. The views expressed herein do not necessarily reflect the official opinion of the donors.
Ethics approval and consent to participate
Consent for publication
No competing interest was reported by the authors.
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
About this article
Cite this article
Nkya, T.E., Fillinger, U., Sangoro, O.P. et al. Six decades of malaria vector control in southern Africa: a review of the entomological evidence-base. Malar J 21, 279 (2022). https://doi.org/10.1186/s12936-022-04292-6
- Malaria vectors
- Vector control
- Malaria elimination
- Southern African region