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[Preprint]. 2023 Aug 28:rs.3.rs-3286696. [Version 1] doi: 10.21203/rs.3.rs-3286696/v1

The Role of Car Tyres in the Ecology of Aedes aegypti Mosquitoes in Ghana

Anisa Abdulai 1, Christopher Mfum Owusu-Asenso 2, Christodea Haizel 3, Sebastian Kow Egyin Mensah 4, Isaac Kwame Sraku 5, Abdul Rahim Mohammed 6, Yaw Akuamoah-Boateng 7, Akua Obeng Forson 8, Yaw A Afrane 9
PMCID: PMC10491337  PMID: 37693506

Abstract

Background

The Aedes aegyptimosquito is an important vector of arboviral diseases including dengue and yellow fever. Despite the wide distribution of the Aedes aegypti mosquito, there is limited data on the ecology of Aedes aegypti mosquitoes in Ghana. In this study, we report on the oviposition preference and the larval life table of Aedes aegypti mosquitoes in Accra, Ghana.

Methods

The oviposition preference of Aedesmosquitoes to three habitat types (tyres, drums and bowls) was measured by setting up ovitraps. Ovitraps were checked for the presence of Aedes larvae every 3 days. The presence and number of larvae were recorded for each habitat type. Two-hour-old Aedes aegypti larvae were introduced into and raised in these three habitat types to undertake larval life tables. The number of surviving larvae at each developmental stage was recorded daily until they emerge as adults.

Results

Car tyres showed a high abundance of Aedeslarvae (52.33%) than drums (32.49%) and bowls (15.18%) (ANOVA, F _ 18.79, df _ 2, 159, P < 0.001). The mean development time of Ae. aegypti larvae was significantly lower in car tyres (7 ± 1 days) compared to that of bowls (9 ± 0.0 days) and drums (12.6 ± 1.5 days) (H (2) = 7.448, P = 0.024). The differences in pupation rates and emergence rates were not significant across the habitat types, however, the highest pupation rate was observed in bowls (0.92) and the emergence rate was highest in tyres (0.84). The proportion of first-instar larvae that survived to adults was significantly higher in tyres with a shorter survival time (0.84; 9 days) compared to that of bowls (0.72; 10 days) and drums (0.62 ± 0.2; 13 days) (H (2) = 2.822, P= 0.009).

Conclusion

The results confirm that discarded car tyres were the preferred habitat choice for the oviposition of gravid female Aedes aegypti mosquitoes and provide the best habitat condition for larval development and survival. These findings are necessary for understanding the ecology of Aedes mosquitoes to develop appropriate strategies for their control in Ghana.

Introduction

Yellow Fever and Dengue fever outbreaks have become more frequent in West Africa in the last 5 years [16]. Aedes aegypti mosquitoes transmit arboviruses that cause diseases such as Yellow fever, Dengue fever, Zika, Chikungunya and Rift Valley Fever. Aedes aegypti is highly anthropophilic and mainly adapted to urban settings [7]. Domestic forms of African Ae. aegypti is more adapted to breeding in artificial containers close to human settlements [8,9]. However, the sylvatic forms of Ae. aegypti breed in natural breeding habitats such as rock pools, tree holes and fruit husks in forested areas [7]. The main vector control strategies for Aedes control are chemical interventions using insecticides and larval source management [10].

The World Health Organization (WHO) recommends using larval source management (LSM) to control the immature stages of Aedes mosquitoes [11]. This will help in reducing the densities of Aedes vectors within communities. Currently, evidence of insecticide resistance to the four main insecticides in adult Aedes mosquitoes has been detected in Ghana and across West Africa [1216]. Controlling the immature stages of Aedes mosquitoes using LSM helps reduce the dependence on the main insecticides by combining Larviciding and habitat modifications and manipulation [17,18].

To control the immature stages of Aedes mosquitoes, it is critical to understand the behaviour of these vectors such as their preferred habitat for oviposition and their life history traits. Female Aedes aegypti in urban and suburban areas prefer to breed in artificial, man-made containers such as tyres, discarded containers, flower pots or drums [19]. Aedes aegypti from different areas have been found to have different oviposition preferences [2023]. Several studies in West Africa including Ghana have found Aedes aegypti mosquitoes breeding predominately in car tyres [15,2427]. Tyres are especially useful for mosquito reproduction because they are mostly stored outdoors and can collect and maintain rainwater for a long period. Moreover, car tyres serve as an excellent breeding habitat for Aedes mosquitoes because decaying leaves from neighbouring trees provide chemical conditions which are similar to tree holes [28]. However, other studies have also found Aedes larvae to breed predominately in other habitat types such as large water barrels, animal troughs, plastic containers and septic tanks [2830].

A female mosquito’s choice of habitat type and oviposition may be influenced by several factors such as the season, habitat size and nutritional availability [19,31]. Female mosquitoes increase the survival and development of their offspring by selecting breeding habitats that reduce the risks of predators and competition [32,33]. For instance, Aedes mosquitoes mostly rests and feeds outdoors, so they can explore a wider range of habitat types that are far from human settlements [33]. Several studies in Ghana found Aedes mosquito abundance to be significantly higher outdoors than indoors [15,34]. Understanding the oviposition choices of female Aedes mosquitoes will help in designing targeted LSM interventions for these vectors.

Mosquito larval development and survivorship are important determinants of vector densities within an area [35]. Several studies have found that there are variations in life history traits such as larval development and survival in Ae. aegypti mosquitoes in different areas [36,37]. This is because different areas may have diverse environmental conditions which may affect larval development, survival and adult emergence [38,39]. Understanding the life history traits of Ghanaian Aedes aegypti mosquitoes is very important for the development of appropriate vector control measures for the immature stages of these vectors. This study aims to investigate the oviposition preference and the larval life history traits of Aedes mosquitoes in Accra, Ghana. This information will greatly improve vector control strategies especially larval source management for arboviral disease vectors in Ghana.

Material and Methods

Study Site

Aedes larvae were sampled from different breeding spots within Korle-bu (5° 33’ N 0° 12’ W), Accra, Ghana. Korle-bu is a suburb located in the coastal savannah zone of the Greater Accra Region. This area has the largest teaching and referral hospital in Ghana, thus has an influx of people from different regions across Ghana. This is a populous cosmopolitan area in Accra with numerous vulcanizing spots within the area. The inhabitants also tend to store water in storage containers due to the irregular low of pipe-borne water. There is an abundance of Aedes breeding habitats ranging mostly from used car tyres, small containers and water storage drums due to their inadequate water and drainage systems.

Aedes Oviposition in Three Habitat Types

An oviposition experiment was set up to investigate the preferred habitat type for Aedes mosquitoes using three habitat types, i.e., car tyres, bowls and drums. Car tyre ovitraps were made by cutting a car tyre into three parts that can hold water. Each car tyres ovitrap was approximately 56 cm in length and 15cm in height with an aperture of 5cm. Bowls were plastic, black and had a capacity of 5 litres water capacity. Drums had a water capacity of 50 litres and were made of plastic. At a particular spot, all three different habit types were set up to determine, which type was preferred for oviposition by gravid female Aedes mosquitoes.

Each container type was filled with 2 to 5 litres of rainwater and was placed in the natural environment close to where other habitats have been found in the past. For the reproducibility of the experiment, three replicates of each habitat type were set up in different areas. Larval abundance was used as a proxy for oviposition preference because of the difficulty in identifying and counting Aedes eggs that were laid in the different habitats especially tyres because of their dark surface. The replicates were checked for the presence of larvae every three days. The number of larvae were recorded for each habitat type. Larvae were removed and the water was replaced after every recording.

Larval life table in three habitat types

A life table experiments were performed to determine the life history traits of Aedes aegypti mosquitoes in different habitat types. The life-table components investigated were larval development time, pupation rates, emergence rate and sex ratio. Experiments were set up in three replicates each, for three different habitat types, i.e., car tyres, drums and bowls. For each replicate, thirty 2-hour-old larvae were introduced into each habitat type, containing 2 to 5 litres of rainwater and covered with a muslin net. Each habitat type was placed in its natural environment. The replicates were observed daily and the volume of water was replenished daily due to evaporation.

Developmental stages of surviving Ae. aegypti mosquito larvae were assessed daily; alive and dead larvae were recorded. Pupae collected from the habitat types were held in pre-labelled individual paper cups with water of a depth of 25 ml for adult emergence. The paper cups containing one pupa per cup were covered with muslin netting and observed daily for adult emergence. Pupae mortality, adult mosquitoes that emerged (emergence rate), and the sexes were recorded daily. When pupation started, habitats were visited twice a day, at 8 am and 5 pm daily for pupae collections.

Data Analysis

Larval abundance was calculated as the percentage of number of larvae obtained per each habitat type over the total number of larvae collected. This was used to measure the oviposition preference of Aedes mosquitoes to the three habitat types. For the larval life table experiment, the larval development time was recorded in days as the duration from the first instar larval stage to the pupal stage. Mean larval development time was defined as the average duration, in days, of first-instar larvae to develop into pupae. The pupation rate was calculated as the sum of the total number of pupae per the sum of the total number of 1st Instar larvae. The emergence rate was calculated as the sum of the number of adults that emerged per the total number of pupae.

Survivorship of Ae. aegypti larvae was calculated as the proportion of first-instar larvae that survived to adults. The ratio of females to males was determined by counting and recording the number of males and females that emerge per day over the total number of adults that emerged. The ANOVA test and Kruskal-Wallis ranked sum test was used to test the statistical significance of the different habitat types on larval survivorship and larval development time wherever appropriate. Dunn’s test was used to compare the significance of the means. Pearson Chi-square test was used to test for significance in survivorship. All data analyses were performed using R version 3.6.3.

Results

Aedes immature abundance in three different habitat types

A total of 4,059 immature Aedes mosquitoes were collected during the entire sampling period. The highest numbers of Aedes immatures were found in used tyres (2124/ 4059; 52.33%) as compared to that of drums (1319/4059; 32.49%). Bowls recorded the least abundance of Aedes immatures (616/4059; 15.18%) (Fig 1). There was a significant difference in the abundance of immature in the three habitat types (ANOVA, F _ 18.79, df _ 2, 159, P < 0.001).

Figure 1.

Figure 1

Abundance of immature Aedes mosquitoes collected from different habitat types (tyres, bowls and drums). Error bars represent the 95% confidence interval of the mean.

Development Time and Survival of Immature Stages of Aedes aegypti

The mean larval to pupae development time for immature Aedes aegypti mosquitoes was lower in tyres, 7 days as compared to bowls (9 days) and drums (12.7 days) (H (2) = 7.448, P = 0.024). A pairwise post-hoc Dunn test with Bonferroni adjustments showed that there was a significant difference in the mean larval to pupae development time between tyres and drums (P = 0.009) but no significant difference between tyres and bowls (P = 0.258). Furthermore, there was no significant difference in the mean larval to adult development time in males from the three habitat types (H (2) = 5.728, P= 0.06). However, there was a significant difference in the mean larval to adult development time of female Ae. aegypti mosquitoes (H (2) = 6.054, P= 0.048).

Pupation rate, emergence and survivorship of Immature Aedes aegypti in the different habitat types

A higher proportion of larvae pupated in bowls, (0.92) compared to that of tyres (0.88) and drums (0.75) but the observed differences were not significant (H (2) = 2.667, df = 2, P= 0.263). Out of the proportion of larvae that pupated, those that emerged as adults were 0.84 in tyres, 0.8 in drums and 0.77 in bowls (ANOVA, F _ 0.38, df _ 2, 6, P < 0.697). The proportion of first-instar larvae that survived to adults was greater in tyres (0.84 ± 0.1) than that in bowls, 0.72 ± 0.2 and drums, 0.62 ± 0.2. However, the differences in survivorship were not significant across the three habitat types (H (2) =2.822, P= 0.238). This is shown in Table 2.

Table 2:

Pupation rate and emergence rate of immature Aedes aegypti mosquitoes in different habitat types

Habitat Type Pupation (x ± SD) Emergence (x ± SD) Survivorship (x ± SD)
Tyres 0.88 ± 0.02 0.84 ± 0.1 0.84 ± 0.1a
Bowls 0.92 ± 0.17 0.77 ± 0.7 0.72 ± 0.2a
Drums 0.75 ± 0.22 0.8 ± 0.12 0.62 ± 0.2b

Values are means ± standard deviations. The differences in the proportion of larvae that pupated and emerged between the three habitat types, tyres, bowls and drums were not statistically significant (P>0.05).

Ae. aegypti larvae from car tyres showed a significantly shorter survival length of 9 days compared to that of drums (13 days) (H (2) = 2.822, P= 0.009). Larval survivorship reached 0% (all larvae became pupa) after 10 days in bowls (Figure 2).

Figure 2.

Figure 2

Aedes aegypti larval survivorship curve across the different habitat types

Sex Ratio of immature Aedes aegypti mosquitoes in different habitat types

The proportion of males that emerged was higher in tyres (65.79%) and bowls (60%) compared to that of males that emerged from drums (37.5%). The proportion of emerged females was higher in drums (62.5%) compared to that of bowls (40%) and drums (34.21%). There was a significant association between habitat type and the sex of emerged adults, (χ2 = 11.0601, df = 2, P= 0.004) (Table 3).

Table 3:

The number of males and females that emerged from the different habitat types

Habitat type Sample Size Male % Female % Sex Ratio (Female: Male)
Tyres 76 65.79 34.21 1:1.8a
Bowls 55 60 40 1:1.9a
Drums 56 37.5 62.5 1:0.6b

Values are means percentages. The letters symbol following the numerical values indicate the results of multiple comparison tests, and values with the same letter in each column were not statistically significant at P<0.05 and those with different letters in each column were statistically significant at P<0.05.

Discussion

Understanding the ecology and biology of Aedes mosquitoes is crucial for the control of Aedes-borne diseases. Development times and survivorship of various stages of mosquitoes under different environments are of particular importance, as they affect the vectorial capacity, which is tightly linked to mosquito-borne disease transmission [40]. This study provides evidence of the oviposition preferences and larval life history traits of Aedes aegypti mosquitoes in different habitat types in Accra, Ghana. Findings from our study showed high Aedes larval abundance in tyres compared to that of the other habitat types. Aedes aegypti larvae from tyres showed a significantly shorter development time and high survivorship compared to the other habitat types.

Aedes immature abundance was used as a proxy for oviposition preference in three different habitat types. The highest larval abundance was observed in tyres, suggesting that Ghanaian Aedes mosquitoes prefer to breed in tyres compared to other habitat types. This finding is in line with that of Owusu-Asenso et al (2022) where car tyres produced the highest densities of Aedes larvae [15]. Car tyres are among the most productive aquatic habitats across West Africa [20, 26, 41]. This may be because discarded car tyres are less prone to disturbance as compared to other habitat types such as containers, tin cans or coconut shells. Also, the internal condition in car tyres such as reduced light and low humidity attract gravid female Aedes mosquitoes [42]. Car tyres have a narrow opening thus providing some level of shade to the immature larvae and reducing the amount of light entering the habitat [20]. High mosquito densities have been associated with habitats that have some level of shading [43].

Thus, car tyres may be targeted for larval source management in the control of Aedes mosquitoes. Although car tyres are the most productive habitat type, discarded containers are also a common source of aquatic habitats. Drums were the second most abundant habitat in our study [20]. A risk factor for the presence of Aedes mosquitoes is the storage of water in drums for drinking or domestic use. A study from Cape Coast, Ghana found more storage containers to be infested with Aedes larvae in areas with water storage compared to areas with adequate access to piped water [25].

This study observed that the mean development time was significantly longer in the Aedes aegypti larvae from drums compared to Aedes larvae in tyres. The mean development time was similar between tyres and bowls and shorter as compared to that of drums. The short mean development time of Aedes mosquito larvae has important epidemiological implications. Rapid larval development favors higher vector densities, which may increase disease transmission. This is because the longer development time will expose the larvae to predation and loss of habitat through desiccation [20]. This negatively impacts the vectorial capacity of the vectors [44].

There were no significant differences in the emergence of Ae. aegypti mosquitoes across the three habitat types. However, the proportion of emerged adults was higher in car tyres and drums compared to bowls. Larval survivorship was higher in car tyres coupled by high pupation and emergence rates. Compared to other habitat types, Ae. Aegypti larvae from car tyres showed a significantly short survival length. These findings suggest that car tyres may be responsible for the high densities of adult Aedes mosquitoes, which may facilitate arboviral transmission in Accra, Ghana. The experiments were conducted in controlled environment thus this study did not take into account potential biological factors such as predators and competition, which may affect may survivorship. Furthermore, temperature and relative humidity was not measured, thus, its effect on the abundance of Aedes larvae was not determined.

Conclusion

This study showed that car tyres are the preferred choice for oviposition for gravid female Aedes mosquitoes. Furthermore, this study provides the first report on the life history parameters of Aedes aegypti mosquitoes from Korle-Bu, Accra, Ghana. Ae. aegypti larvae from car tyres showed a shorter larval development time and higher survivorship compared to other habitat types. This suggests that tyres may be playing a significant role in the ecology of Aedes mosquitoes, thus facilitating arboviral transmission. This study provides baseline information that is essential for wider studies towards a better understanding of the ecology of Aedes mosquitoes to develop appropriate strategies for their control in Ghana.

Table 1:

Larval development time of immature Aedes aegypti mosquitoes in different habitat types

Habitat Type Mean larval-pupae development time Mean development time of males (days) Mean development time of females (days)
Tyres 7 ± 1a 8 ± 1a 8.6 ± 0.5a
Bowls 9 ± 0.0a 8.3 ± 0.5a 8.3 ± 0.5a
Drums 12.6 ± 1.5b 12 ± 1b 14.3 ± 1.1b

Values are means ± standard deviations. The letter symbol following the numerical values indicates the results of multiple comparison tests, and values with the same letter in each column were not statistically significant at P<0.05 and those with different letters in each column were statistically significant at P<0.05.

Acknowledgements

We thank the residents of the study sites for their support during our study. Our sincere gratitude goes to all the staff of the animal house unit of the Department of Medical Microbiology, University of Ghana for their field assistance

Funding

This study was supported by grants from the National Institute of Health (D43 TW 011513).

Footnotes

Competing interests

The authors declare that they have no competing interests

Ethics Approval

Not applicable.

Consent for publication

Not applicable.

Contributor Information

Anisa Abdulai, University of Ghana.

Christopher Mfum Owusu-Asenso, University of Ghana.

Christodea Haizel, University of Ghana.

Sebastian Kow Egyin Mensah, University of Ghana.

Isaac Kwame Sraku, University of Ghana.

Abdul Rahim Mohammed, University of Ghana.

Yaw Akuamoah-Boateng, University of Ghana.

Akua Obeng Forson, University of Ghana.

Yaw A. Afrane, University of Ghana

Availability of data and materials

All datasets generated and/or analysed during this study are available on request.

References

  • 1.Amoako N, Duodu S, Dennis FE, Bonney JHK, Asante KP, Ameh J, et al. Detection of Dengue Virus among Children with Suspected Malaria, Accra, Ghana. Emerg Infect Dis [Internet]. Centers for Disease Control and Prevention; 2018;24:1544–7. Available from: https://pubmed.ncbi.nlm.nih.gov/30015610 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 2.Adogo LY, Ogoh MO. Yellow fever in Nigeria: A review of the current situation. African J Clin Exp Microbiol. 2020;21:1–13. [Google Scholar]
  • 3.Suzuki T, Kutsuna S, Taniguchi S, Tajima S, Maeki T, Kato F, et al. Dengue virus exported from Cote d’Ivoire to Japan, June 2017. Emerg Infect Dis. Centers for Disease Control and Prevention; 2017;23:1758. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 4.Tarnagda Z, Cissé A, Bicaba BW, Diagbouga S, Sagna T, Ilboudo AK, et al. Dengue fever in Burkina faso, 2016. Emerg Infect Dis. Centers for Disease Control and Prevention; 2018;24:170. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 5.Weetman D, Kamgang B, Badolo A, Moyes CL, Shearer FM, Coulibaly M, et al. Aedes Mosquitoes and Aedes-Borne Arboviruses in Africa: Current and Future Threats. Int J Environ Res Public Health [Internet]. MDPI; 2018;15:220. Available from: https://pubmed.ncbi.nlm.nih.gov/29382107 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 6.World Health Organization. Yellow Fever - West and Central Africa [Internet]. 2021. [cited 2022 Mar 9]. Available from: https://www.who.int/emergencies/disease-outbreak-news/item/yellow-fever---west-and-central-africa
  • 7.Powell JR, Tabachnick WJ. History of domestication and spread of Aedes aegypti–a review. Mem Inst Oswaldo Cruz [Internet]. Instituto Oswaldo Cruz, Ministério da Saúde; 2013;108 Suppl:11–7. Available from: https://pubmed.ncbi.nlm.nih.gov/24473798 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 8.Brown JE, McBride CS, Johnson P, Ritchie S, Paupy C, Bossin H, et al. Worldwide patterns of genetic differentiation imply multiple ‘domestications’ of Aedes aegypti, a major vector of human diseases. Proc R Soc B Biol Sci. The Royal Society; 2011;278:2446–54. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 9.Crawford JE, Alves JM, Palmer WJ, Day JP, Sylla M, Ramasamy R, et al. Population genomics reveals that an anthropophilic population of Aedes aegypti mosquitoes in West Africa recently gave rise to American and Asian populations of this major disease vector. BMC Biol. BioMed Central; 2017;15:1–16. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 10.Weeratunga P, Rodrigo C, Fernando SD, Rajapakse S. Control methods for Aedes albopictus and Aedes aegypti. Cochrane Database Syst Rev. John Wiley and Sons, Inc. and the Cochrane Library; 2017;2017. [Google Scholar]
  • 11.World Health Organization. Treatment, prevention and control global strategy for dengue prevention and control 2. WHO Press. 2017;43. [Google Scholar]
  • 12.Kwame Amlalo G, Akorli J, Etornam Akyea-Bobi N, Sowa Akporh S, Aqua-Baidoo D, Opoku M, et al. Evidence of High Frequencies of Insecticide Resistance Mutations in Aedes aegypti (Culicidae) Mosquitoes in Urban Accra, Ghana: Implications for Insecticide-based Vector Control of Aedes-borne Arboviral Diseases. J Med Entomol [Internet]. 2022;tjac120. Available from: 10.1093/jme/tjac120 [DOI] [PubMed] [Google Scholar]
  • 13.Badolo A, Sombié A, Pignatelli PM, Sanon A, Yaméogo F, Wangrawa DW, et al. Insecticide resistance levels and mechanisms in Aedes aegypti populations in and around Ouagadougou, Burkina Faso. PLoS Negl Trop Dis [Internet]. Public Library of Science; 2019;13:e0007439–e0007439. Available from: https://pubmed.ncbi.nlm.nih.gov/31120874 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 14.Konan LY, Oumbouke WA, Silué UG, Coulibaly IZ, Ziogba J-CT, N’Guessan RK, et al. Insecticide Resistance Patterns and Mechanisms in Aedes aegypti (Diptera: Culicidae) Populations Across Abidjan, Côte d’Ivoire Reveal Emergent Pyrethroid Resistance. J Med Entomol [Internet]. 2021;58:1808–16. Available from: 10.1093/jme/tjab045 [DOI] [PubMed] [Google Scholar]
  • 15.Owusu-Asenso CM, Mingle JAA, Weetman D, Afrane YA. Spatiotemporal distribution and insecticide resistance status of Aedes aegypti in Ghana. Parasit Vectors [Internet]. 2022;15:61. Available from: 10.1186/s13071-022-05179-w [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 16.Toé HK, Zongo S, Guelbeogo MW, Kamgang B, Viana M, Tapsoba M, et al. Multiple insecticide resistance and first evidence of V410L kdr mutation in Aedes (Stegomyia) aegypti (Linnaeus) from Burkina Faso. Med Vet Entomol [Internet]. John Wiley & Sons, Ltd; 2022;36:309–19. Available from: 10.1111/mve.12602 [DOI] [PubMed] [Google Scholar]
  • 17.Adetoro FA, Anikwe JC, Makanjuola WA, Omotayo AI, Awolola ST. Comparative Evaluation of Larvicides for Larval Source Management of Mosquitoes in Lagos, Nigeria. Egypt Acad J Biol Sci A, Entomol [Internet]. Department of Zoology, University of Lagos, Akoka, Yaba, Lagos, Nigeria.; 2022;15:33–46. Available from: https://eajbsa.journals.ekb.eg/article_221971.html [Google Scholar]
  • 18.Tusting LS. Larval source management: A supplementary measure for malaria control. Outlooks Pest Manag. 2014;25:41–3. [Google Scholar]
  • 19.Maciel-de-Freitas R, CODEÇO CT, LOURENÇO-DE-OLIVEIRA R. Body size-associated survival and dispersal rates of Aedes aegypti in Rio de Janeiro. Med Vet Entomol [Internet]. John Wiley & Sons, Ltd; 2007;21:284–92. Available from: 10.1111/j.1365-2915.2007.00694.x [DOI] [PubMed] [Google Scholar]
  • 20.Egid BR, Coulibaly M, Dadzie SK, Kamgang B, McCall PJ, Sedda L, et al. Review of the ecology and behaviour of Aedes aegypti and Aedes albopictus in Western Africa and implications for vector control. Curr Res Parasitol Vector-Borne Dis [Internet]. 2022;2:100074. Available from: https://www.sciencedirect.com/science/article/pii/S2667114X21000686 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 21.Zahouli JBZ, Utzinger J, Adja MA, Müller P, Malone D, Tano Y, et al. Oviposition ecology and species composition of Aedes spp. and Aedes aegypti dynamics in variously urbanized settings in arbovirus foci in southeastern Côte d’Ivoire. Parasit Vectors [Internet]. 2016;9:523. Available from: 10.1186/s13071-016-1778-9 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 22.Zuharah WF, Fadzly N, Wei WOK, Hashim ZH. Oviposition habitat selection of Dengue vectors, Aedes aegypti and Aedes albopictus in response to fish predator. Trop Life Sci Res. School of Medical Sciences, Universiti Sains Malaysia; 2016;27:117. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 23.Simard F, Nchoutpouen E, Toto JC, Fontenille D. Geographic distribution and breeding site preference of Aedes albopictus and Aedes aegypti (Diptera: Culicidae) in Cameroon, Central Africa. J Med Entomol. Oxford University Press Oxford, UK; 2005;42:726–31. [DOI] [PubMed] [Google Scholar]
  • 24.Kamgang B, Ngoagouni C, Manirakiza A, Nakouné E, Paupy C, Kazanji M. Temporal Patterns of Abundance of Aedes aegypti and Aedes albopictus (Diptera: Culicidae) and Mitochondrial DNA Analysis of Ae. albopictus in the Central African Republic. PLoS Negl Trop Dis [Internet]. Public Library of Science; 2013;7:e2590. Available from: 10.1371/journal.pntd.0002590 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 25.Kudom AA. Entomological surveillance to assess potential outbreak of Aedes-borne arboviruses and insecticide resistance status of Aedes aegypti from Cape Coast, Ghana. Acta Trop [Internet]. 2020;202:105257. Available from: https://www.sciencedirect.com/science/article/pii/S0001706X18313342 [DOI] [PubMed] [Google Scholar]
  • 26.Tedjou AN, Kamgang B, Yougang AP, Wilson-Bahun TA, Njiokou F, Wondji CS. Patterns of Ecological Adaptation of Aedes aegypti and Aedes albopictus and Stegomyia Indices Highlight the Potential Risk of Arbovirus Transmission in Yaoundé, the Capital City of Cameroon. Pathog (Basel, Switzerland) [Internet]. MDPI; 2020;9:491. Available from: https://pubmed.ncbi.nlm.nih.gov/32575721 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 27.Wat’senga Tezzo F, Fasine S, Manzambi Zola E, Marquetti MDC, Binene Mbuka G, Ilombe G, et al. High Aedes spp. larval indices in Kinshasa, Democratic Republic of Congo. Parasit Vectors [Internet]. England; 2021;14:92. Available from: https://pubmed.ncbi.nlm.nih.gov/33522947 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 28.Kweka E, Mathias L, John Mwang’onde B, Baraka G, Mahande MJ, Baraka V. Ecology of Aedes Mosquitoes, the Major Vectors of Arboviruses in Human Population. 2018. [Google Scholar]
  • 29.Badolo A, Sombié A, Yaméogo F, Wangrawa DW, Sanon A, Pignatelli PM, et al. First comprehensive analysis of Aedes aegypti bionomics during an arbovirus outbreak in west Africa: Dengue in Ouagadougou, Burkina Faso, 2016–2017. PLoS Negl Trop Dis [Internet]. Public Library of Science; 2022;16:e0010059–e0010059. Available from: https://pubmed.ncbi.nlm.nih.gov/35793379 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 30.Kampango A, Furu P, Sarath DL, Haji KA, Konradsen F, Schiøler KL, et al. Risk factors for occurrence and abundance of Aedes aegypti and Aedes bromeliae at hotel compounds in Zanzibar. Parasit Vectors [Internet]. England; 2021;14:544. Available from: https://pubmed.ncbi.nlm.nih.gov/34686195 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 31.Spencer CY, Pendergast TH, Harrington LC. Fructose Variation In The Dengue Vector, <Span Class=“Genus-Species”>Aedes aegypti</Span>, During High And Low Transmission Seasons In The Mae Sot Region Of Thailand. J Am Mosq Control Assoc [Internet]. 2005;21:177–81. Available from: 10.2987/8756-971X(2005)21[177:FVITDV]2.0.CO [DOI] [PubMed] [Google Scholar]
  • 32.Blaustein L, Kiflawi M, Eitam A, Mangel M, Cohen JE. Oviposition Habitat Selection in Response to Risk of Predation in Temporary Pools: Mode of Detection and Consistency across Experimental Venue. Oecologia [Internet]. Springer; 2004;138:300–5. Available from: http://www.jstor.org/stable/40005649 [DOI] [PubMed] [Google Scholar]
  • 33.Wong J, Stoddard ST, Astete H, Morrison AC, Scott TW. Oviposition Site Selection by the Dengue Vector Aedes aegypti and Its Implications for Dengue Control. PLoS Negl Trop Dis [Internet]. Public Library of Science; 2011;5:e1015. Available from: 10.1371/journal.pntd.0001015 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 34.Captain-Esoah M, Kweku Baidoo P, Frempong KK, Adabie-Gomez D, Chabi J, Obuobi D, et al. Biting behavior and molecular identification of Aedes aegypti (Diptera: Culicidae) subspecies in some selected recent yellow fever outbreak communities in Northern Ghana. J Med Entomol. Oxford University Press US; 2020;57:1239–45. [DOI] [PubMed] [Google Scholar]
  • 35.Li Y, Kamara F, Zhou G, Puthiyakunnon S, Li C, Liu Y, et al. Urbanization Increases Aedes albopictus Larval Habitats and Accelerates Mosquito Development and Survivorship. PLoS Negl Trop Dis [Internet]. Public Library of Science; 2014;8:e3301. Available from: 10.1371/journal.pntd.0003301 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 36.Bong L-J, Tu W-C, Neoh K-B. Interpopulation variations in life history traits and reproductive tactics in Aedes aegypti: A test on populations 50 km apart. Acta Trop [Internet]. 2021;213:105750. Available from: https://www.sciencedirect.com/science/article/pii/S0001706X20316636 [DOI] [PubMed] [Google Scholar]
  • 37.Cui G, Zhong S, Zheng T, Li Z, Zhang X, Li C, et al. Aedes albopictus life table: environment, food, and age dependence survivorship and reproduction in a tropical area. Parasit Vectors [Internet]. 2021;14:568. Available from: 10.1186/s13071-021-05081-x [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 38.Afrane YA, Little TJ, Lawson BW, Githeko AK, Yan G. Deforestation and vectorial capacity of Anopheles gambiae Giles mosquitoes in malaria transmission, Kenya. Emerg Infect Dis [Internet]. Centers for Disease Control and Prevention; 2008;14:1533–8. Available from: https://pubmed.ncbi.nlm.nih.gov/18826815 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 39.Yang D, He Y, Ni W, Lai Q, Yang Y, Xie J, et al. Semi-field life-table studies of Aedes albopictus (Diptera: Culicidae) in Guangzhou, China. PLoS One [Internet]. Public Library of Science; 2020;15:e0229829. Available from: 10.1371/journal.pone.0229829 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 40.David MR, Garcia GA, Valle D, Maciel-de-Freitas R. Insecticide Resistance and Fitness: The Case of Four Aedes aegypti Populations from Different Brazilian Regions. Remoue F, editor. Biomed Res Int [Internet]. Hindawi; 2018;2018:6257860. Available from: 10.1155/2018/6257860 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 41.Ouattara LPE, Sangaré I, Namountougou M, Hien A, Ouari A, Soma DD, et al. Surveys of Arboviruses Vectors in Four Cities Stretching Along a Railway Transect of Burkina Faso: Risk Transmission and Insecticide Susceptibility Status of Potential Vectors. Front Vet Sci [Internet]. Frontiers Media S.A.; 2019;6:140. Available from: https://pubmed.ncbi.nlm.nih.gov/31192232 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 42.Dom NC, Ahmad AH, Ismail R. Habitat characterization of Aedes sp. breeding in urban hotspot area. Procedia-Social Behav Sci. Elsevier; 2013;85:100–9. [Google Scholar]
  • 43.Yee DA, Allgood D, Kneitel JM, Kuehn KA. Constitutive Differences Between Natural and Artificial Container Mosquito Habitats: Vector Communities, Resources, Microorganisms, and Habitat Parameters. J Med Entomol [Internet]. 2012;49:482–91. Available from: 10.1603/ME11227 [DOI] [PubMed] [Google Scholar]
  • 44.Rivero A, Vezilier J, Weill M, Read AF, Gandon S. Insecticide control of vector-borne diseases: when is insecticide resistance a problem? PLoS Pathog. Public Library of Science San Francisco, USA; 2010;6:e1001000. [DOI] [PMC free article] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Data Availability Statement

All datasets generated and/or analysed during this study are available on request.


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