Figures
Abstract
House Index, Container Index, and Breteau Index are the most commonly used indices for dengue vector surveillance. However, these larval indices are a poor proxy for measuring the adult population—which is responsible for disease transmission. Information on the adult distribution and density are important for assessing transmission risk as well as for developing effective control strategies. This study introduces a new entomological index, Gravitrap aegypti index (GAI), which estimates the adult female Aedes aegypti population in the community and presents its association with dengue cases. Gravitraps were deployed across 34 treatment sites in Singapore from September 2013 to September 2016. The GAI, derived from the Gravitrap surveillance data, was analysed to investigate the spatio-temporal patterns of the Ae. aegypti population in Singapore. The index was further categorised into low, moderate, and high-risk groups and its association with dengue cases were examined. A Before-After Control Impact analysis was performed to evaluate the epidemiology impact of Gravitrap system on dengue transmission. The Ae. aegypti population exhibits a seasonal pattern, and spatial heterogeneity in Ae. aegypti abundance was observed among treatment sites. The Ae. aegypti population was also found to be unevenly distributed among floors of an apartment block, with low floors (floors 1–4) having a higher abundance of mosquitoes trapped than mid (floors 5–8) and high (floors ≥9) floors. Areas with high GAI were shown to have higher dengue case count. Gravitrap has also demonstrated to be a good dengue control tool. The contribution of cases by treatment sites to the national numbers was lower after Gravitraps deployment. The GAI, which is of better relevance to dengue transmission risk, could be recommended as an indicator for decision making in vector control efforts, and to monitor the spatio-temporal variability of the adult Aedes population in the country. In addition, findings from this study indicate that Gravitraps can be used as a dengue control tool to reduce dengue transmission.
Author summary
In the absence of an effective vaccine: vector surveillance and control remain the key strategy for dengue prevention and control. The collection of the adult female Aedes mosquito is thus important to understand disease transmission dynamics. Information on its distribution and density are also essential for assessing transmission risk as well as for devising an effective control strategy. Here, we described a new approach to dengue vector surveillance based on adult female Aedes trapping using Gravitraps. Using the Gravitrap surveillance data, we derived a new entomological index, Gravitrap aegypti index (GAI), which estimates the adult female Ae. aegypti population in the community and presents its association with dengue cases. When analysed, the index can provide useful information on the spatio-temporal distribution of the Ae. aegypti population in the country and hence, assist planning of vector control. The GAI, which is of better relevance to dengue transmission risk, could be used as an indicator for decision making in vector control efforts, and to monitor the spatio-temporal variability of the adult Aedes population. In addition, findings from this study indicate that Gravitraps can be used as a dengue control tool to reduce dengue transmission.
Citation: Ong J, Chong C-S, Yap G, Lee C, Abdul Razak MA, Chiang S, et al. (2020) Gravitrap deployment for adult Aedes aegypti surveillance and its impact on dengue cases. PLoS Negl Trop Dis 14(8): e0008528. https://doi.org/10.1371/journal.pntd.0008528
Editor: Robert L. Aldridge, USDA-ARS Center for Medical Agricultural and Veterinary Entomology, UNITED STATES
Received: December 8, 2019; Accepted: June 26, 2020; Published: August 7, 2020
Copyright: © 2020 Ong et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Data Availability: The data underlying the results presented in the study are owned by a third party. They are available upon reasonable request from the Environmental Public Health Operations Department of the National Environment Agency (email: Contact_NEA@nea.gov.sg).
Funding: The study was funded by Singapore's Ministry of Environment and Water Resources. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
Introduction
Dengue fever has become the most important mosquito-borne viral disease due to its increasing frequency and magnitude of dengue epidemics as well as its high morbidity and mortality [1,2]. It is estimated that 390 million dengue infections occur each year (95% credible interval 284–528 million), with more than 125 countries known to be dengue endemic [2,3]. Dengue poses a significant public health threat globally, especially throughout the tropical and subtropical regions [4].
Dengue fever is caused by infection with one of the four dengue virus serotypes and is transmitted to humans primarily by the mosquito Aedes aegypti and by Ae. albopictus as a secondary vector [5,6]. Both Ae. aegypti and Ae. albopictus are known to be widely distributed in the tropical and subtropical areas of the world [7]. However, these Aedes species have expanded all over the world in the past decades and expanded the geographical risk of dengue outbreaks [8,9]. The dengue outbreak in Nepal in 2006 and more recently on Madeira island in 2012, are examples of epidemic driven by Ae. aegypti invasion [10,11]. The occurrence of Ae. aegypti was not reported in Nepal until 2006 when entomological survey conducted after its first dengue outbreak revealed the presence of Ae. aegypti in five major urban areas [12,13]. The outbreak on Madeira island was the first dengue epidemic in Europe since the 1920s, and it occurred in a territory where Ae. aegypti was introduced less than a decade before the outbreak [14].
Located in the tropical region of Asia-Pacific, Singapore is endemic for dengue with all four dengue serotypes co-circulating in the country at all times [15]. There is a cyclical pattern of outbreaks that oscillates between DENV-1 and DENV-2 as the predominant serotype [16]. In 2013 and 2014, Singapore experienced the largest outbreaks known to date, reporting 22,170 and 18,318 laboratory confirmed dengue cases respectively [17]. These outbreaks were associated with a switch in the predominant serotype from DENV-2 to DENV-1. The population’s susceptibility to outbreaks may have been influenced by multiple factors; an increase in human population density, improved transportation that facilitated virus dissemination, and low herd immunity resulting from sustained period of low transmission; all of which facilitated dengue transmission [18–20].
In the absence of an effective vaccine: vector surveillance and control remain the key strategy for dengue prevention and control in Singapore. Although several vector surveillance and control techniques have been developed, their utilization is limited to the sampling of the immature stages of Aedes, such as the eggs, larvae, and pupae [21]. Entomological indices generated from these methods–Breteau Index, Container Index, and House Index, only estimate the frequency of infestation and not the actual number [22]. They are also a poor proxy for measuring the adult population, which is responsible for disease transmission. These indices may hence have limited use in assessing transmission risk [23].
In Singapore, the house index has been used to monitor the Ae. aegypti population in the community since the 1960s. However, the low house index of less than 1%, observed in the last few decades has rendered the house index insensitive for gauging trends in the Ae. aegypti population in Singapore [17]. As such, the house index is no longer relevant for dengue risk assessment, suggesting a need to develop new approaches to monitor the Ae. aegypti population. Expansion of surveillance tools and evaluation of populations based on adult collections were considered. As a result, a simple, hay infusion-filled cylindrical trap with a sticky lining on the inner surface was designed to lure and trap gravid female Aedes. The trap was named a Gravitrap to easily to define how it functions–trapping gravid mosquitoes [24]. A field trial was first conducted in a small site in 2010 to assess the effectiveness of the Gravitrap in trapping adult female Aedes. Subsequently, Gravitrap deployment was expanded to 34 treatment sites across the island in 2013. As part of the evolving dengue control programme in Singapore, Gravitraps have been used as a vector surveillance tool by the National Environment Agency (NEA), Singapore, to monitor the spatio-temporal variability of the adult Ae. aegypti population in Singapore [25].
In this study: we introduce a new entomological index, derived from the Gravitrap surveillance data, which provides an indication of the adult population of female Ae. aegypti in the community; the association of the index with dengue transmission risk; and the impact of large-scale deployment of such adult female traps on case counts.
Methods
Ethics statement
This study was granted approval by the Environmental Health Institute of the National Environment Agency, Singapore and the permission to use the dengue case data was approved by the Ministry of Health, Singapore.
Study area and period
A total of 3,000 Gravitraps were deployed at 34 treatment sites across Singapore from September 2013 to September 2016. These treatment sites were residential areas with high rise public housing apartments. Each treatment site comprised of 5 to 30 apartment blocks that were typically 150 meters apart, 12 to 14 floors high, and with the human population ranging between 3,700 and 16,000. These sites were selected due to the high risk of dengue transmission based on a previous study that mapped the spatial risk of dengue in Singapore [26]. Gravitraps (Fig 1) were placed along the common corridors of these apartments in the ratio of 1 trap for every 20 households, i.e. two to three traps on each of three floors per apartment block: lower floor (2nd), mid floor (5th or 6th floor) and high floor (10th or 11th floor). This corresponded to an average of six Gravitraps per apartment block. This trap-to-household ratio and deployment was based on logistic considerations for long term monitoring, and it provided an assessment of the density as well as vertical distribution of the mosquito population. Mosquito data was collected from all 3,000 Gravitraps on a weekly basis.
Entomological data
Gravitrap aegypti index.
The Gravitrap contained a hay infusion solution, which acts as a lure for gravid female Aedes mosquitoes. The hay infusion solution was prepared from a stock solution consisting of 100g of dried Bermuda hay (Cynodon dactylon), purchased from a local equine care product supplier, for every 10L of water. The stock solution was then left at ambient temperature to ferment for 7 days, after which it was filtered and diluted by five times using water. Bacillus thuringensis israelensis (VectorBac WG, Valent BioSciences) was added accordingly to label instruction to kill immatures. During each weekly maintenance of traps, field officers removed all mosquitoes caught on the sticky lining and placed them into vials. The Gravitraps were topped up to the overflow holes with fresh working solution and all debris was removed. Gravitraps were emptied and replaced with fresh solution every eight weeks. All mosquito samples were sent to the laboratory for species identification using mosquito identification keys [27]. Information on the mosquito species, counts and locations were recorded and updated into the study database.
Gravitrap aegypti index (GAI), derived from the Gravitrap surveillance data, was defined as the mean number of female adult Ae. aegypti caught per functional Gravitrap. It estimates the Ae. aegypti population by normalizing the total number of female adult Ae. aegypti caught with the total number of functional Gravitrap recovered.
A functional Gravitrap is defined as a fully-assembled Gravitrap where the inner lining remained sticky to capture mosquitoes and hay infusion solution was present. Traps that were empty, missing, overturned, or had lining removed were considered non-functional and excluded.
Breeding percentage.
Breeding Percentage (BP), derived from routine inspection data, is an index previously developed to estimate the proportion of Ae. aegypti positive breeding sites relative to that of total Aedes spp. positive breeding sites, which includes both Ae. aegypti and Ae. albopictus, the latter being ubiquitous in Singapore [28]. Larvae collected from breeding sites were sent to the laboratory for species identification using mosquito identification keys. BP is calculated from the number of Aedes mosquito breeding sites recorded during ground inspections carried out by NEA using the formula:
NEA carried out routine inspection surveillance across Singapore throughout the year. These inspections include those scheduled for regular preventive surveillance, and those conducted in response to dengue transmission in a location. The relationship between BP and GAI was assessed by Pearson’s correlation.
Dengue case data
Under the Infectious Diseases Act, it is mandatory for all medical practitioners and clinical laboratories to notify all clinically diagnosed and laboratory confirmed dengue cases to the Ministry of Health [29]. The residential address and onset date of each dengue case were recorded and shared with NEA for vector control. Geo-referenced data on dengue cases were extracted from NEA’s database and anonymized prior to analysis.
Statistical analysis
A Before-after control impact (BACI) statistical design was used to examine the impact of Gravitraps on dengue transmission. BACI designs are an effective method that is commonly used for environmental impact assessment [30,31]. The BACI approach is designed to compensate for spatial differences between the treatment and control sites, as well as temporal variance [32,33]. Two control sites were identified for each treatment site, after the selection of the treatment sites. The control sites were epidemiologically matched and randomly selected. They were of the same premise type (i.e. High-rise public housing apartments) and had the same risk of dengue transmission (i.e. High risk) as the treatment sites based on a spatial dengue risk map [26]. The absolute number of dengue cases reported is not a fair measurement of case burden in the treatment and control sites as it is often influenced by island wide dengue outbreak and thus, cannot be compared across time. Therefore, case ratio, a more robust measurement of case burden, was obtained by normalising the number of dengue cases in the treatment and control sites with the total national dengue cases. Monthly case ratios were computed for the treatment and control sites. The case ratios were analysed by fitting a linear mixed effects model using restricted maximum likelihood to estimate the effect of Gravitraps on dengue incidence. The model estimates the main effects and interaction between Site (Treatment vs. Control sites) and Period (Before vs. after Gravitrap deployment), with a random effect of Year. A statistically significant interaction between Site and Period is strong evidence for an effect of Gravitraps on dengue incidence. Data from January 2010 to December 2012 was taken as the before period (i.e. prior to Gravitrap deployment) and January 2014 to September 2016 as the after period (i.e. during Gravitrap deployment) in the BACI analysis.
All statistical analyses were performed using R software version 3.1.1 [34]. Significant differences between groups were determined by non-overlapping 95% confidence intervals. Dengue case data from January 2010 to September 2016 and Gravitrap surveillance data from January 2014 to September 2016 were used in this study.
Results
Temporal analysis
Fig 2A shows the temporal trend of the weekly GAI of the 34 treatment sites. The GAI ranged between 0.05 and 0.30 and averaging at 0.12. The time series data was further decomposed into trend and seasonality components. As illustrated in Fig 2B, there was a gradual increase in the index since 2014. The mean GAI in 2015 (0.13) and 2016 (0.15) was 30% and 50% higher than that of 2014 (0.10) respectively. This increase indicates higher Ae. aegypti activity within the community. The seasonality component suggests a seasonal pattern in the Ae. aegypti activity (Fig 2C). The lowest activities of Ae. aegypti occurred in March (E-week 11–14) and September (E-week 37–40), coinciding with the low rainfall seasons. Peak activity, which occurred in May/June (E-week 19–26) and in December (E-week 49–52), coincided with the high rainfall seasons (S1 Fig).
Temporal trend of the weekly Gravitrap aegypti Index (GAI) from 2014 to 2016 (A). Trend (B) and seasonal (C) decomposition of the GAI in Singapore.
Spatial analysis
Vertical distribution of the Ae. aegypti was examined, and the number of Ae. aegypti caught in the Gravitraps was found to be unevenly distributed among different floors in the apartment block, with low floors (floors 1–4) having a higher abundance of mosquitoes trapped than mid (floors 5–8) and high (floors ≥9) floors (Fig 3). The odds of detecting an Ae. aegypti positive Gravitrap at low floors were 2.05 (95% CI: 2.00,2.09) and 2.35 (95% CI: 2.27,2.43) times higher than the mid and high floors respectively. Spatial heterogeneity in Ae. aegypti abundance was observed when Gravitrap data were analysed separately for each treatment site (Fig 4). The Ae. aegypti population differs between the treatment sites, with some sites having a higher Ae. aegypti abundance than the others. Time series plot for each treatment site is shown in S2 Fig.
The mean Ae. aegypti caught per trap by aggregated floor (Low, Mid and High), and its 95% confidence intervals.
Distribution of the weekly GAI from January 2014 to September 2016 in each treatment site, arranged in descending median GAI.
Association of GAI with BP and dengue cases
The GAI was consistently positively associated with BP (Fig 5). The Pearson’s correlation coefficient ranged between 0.37 and 0.53. Areas with high GAI tended to have high BP, and areas with high BP were previously shown to be associated with high risk of dengue transmission [28]. Temporal relationship between GAI and dengue cases was examined using correlation analysis. As shown in Fig 6, there was no observed temporal relationship (ρ = -0.14, P = 0.09) between GAI and dengue cases. However, when the GAI and dengue case data were analysed spatially at the treatment site level, it was found that treatment sites with high GAI were associated with a higher risk of dengue transmission, as indicated by the higher mean number of dengue cases per week (Fig 7). The GAI were categorized into low, moderate, and high-risk groups based on terciles, and the mean number of dengue cases per week were 0.156 (95% CI: 0.143;0.168), 0.217 (95% CI: 0.201;0.232) and 0.253 (95% CI: 0.236;0.271) respectively.
BACI analysis
Fig 8 shows the locations of the treatment and control sites. The treatment and control sites are well distributed across the country and thus nationally representative. Comparison of the before and after case ratios in sites with Gravitraps showed an impact on dengue transmission. While case ratios in control sites remained unchanged over time, the treatment sites saw a reduction in case ratio, suggesting that contribution of cases by the treatment sites to the national numbers were lower after Gravitraps were deployed (Fig 9). Results from BACI analysis were summarized in Table 1. The main effect terms, Site and Period, were both non-significant. Case ratios in treatment and control sites were of no difference prior to Gravitrap deployment and there were no changes in control sites’ case ratios over time. The interaction term, on the other hand, suggested evidence of treatment effect of Gravitraps. There was a 0.017 reduction in treatment sites’ case ratio after Gravitraps deployment. This corresponds to a 36% reduction in case burden in the treatment sites when comparing to the control sites.
Map showing the spatial distribution of control (red) and treatment (green) sites. The grey borders indicate the residential areas in Singapore. The figure was created using R software with base layer obtained from https://www.onemap.sg/main/v2/.
Monthly case ratios in control (red) and treatment (green) sites, before (2010–2012) and during (2014–2016) Gravitrap deployment.
Outcome is the monthly case ratios.
Discussion
Dengue is transmitted by the adult female Aedes mosquito. The collection of the adult female Aedes mosquito is thus important to understand disease transmission dynamics. Information on its distribution and density are also essential for assessing transmission risk as well as for devising an effective control strategy [35]. Surveillance of the adult Aedes mosquito would therefore be more appropriate for risk assessment than larval indices, whose association with dengue transmission have yet to be proven satisfactory [36]. In recent years, several adult traps (e.g. BG-Sentinel, MosquiTrap, etc.) have been developed to address the increasing need for an efficient adult collection, for both surveillance and control. Even though their efficacy in trapping adult Aedes mosquitoes has been demonstrated in many studies, their utility is limited due to various setbacks such as cost, size, and dependence on electric power [37–40]. Most importantly, what is still lacking is the development of an accurate method of estimating the adult Aedes mosquito density based on the trapping data. Despite the limitations, these adult traps have been useful for entomological studies but are inadequate for epidemiological studies.
This paper described a new approach to dengue vector surveillance, introduced a new entomological index that estimates the adult population of Ae. aegypti in the environment and presented its association with dengue transmission risk. The GAI, provides a measure of the Ae. aegypti density by normalizing the total number of female adult Ae. aegypti caught with the total number of Gravitraps. Unlike traditional indices such as House Index, Container Index and Breteau Index, which are reported on a national level or a neighbourhood level, the main strength of the GAI is its higher resolution in time and space. This is largely due to the possibility of deploying large number of low-cost traps for longitudinal monitoring survey. Depending on operational needs, the index can be computed at different spatial scales. Data can be aggregated to estimate the Ae. aegypti population in the country or analysed separately to estimate the population within a predefined area.
Spatio-temporal patterns of the Ae. aegypti population can be examined to assist the planning of vector control. In our study, time series data of the GAI revealed an increased Ae. aegypti activities over the years. The Ae. aegypti population exhibits a seasonal pattern, characterized by two troughs and peaks. The first trough occurs in March but rises to a peak in May. The Ae. aegypti population decreases subsequently to form a second trough in September and rises again to a peak in December. A recent study on the seasonal fluctuations of Ae. aegypti larval and pupae in Singapore also revealed a bimodal seasonal pattern which peaks in April and November [41]. The consistent one-month lag in the peaks may be attributed to the development and longevity of the Ae. aegypti [42]. Spatially, Ae. aegypti is most abundant on the lower floors of high-rise housing apartments, consistent with those of previous studies that had found that Ae. aegypti prefer to oviposit near ground level [43,44]. This indicates that vector control efforts should be prioritized at lower floors given limited resources. Spatial heterogeneity in Ae. aegypti populations were observed among treatment sites, a possible contributing factor to the differential transmission risk between areas.
Unlike house inspection, Gravitraps which lure mosquitoes are not biased by the inaccessibility of premises or cryptic breeding sites. Since the implementation of Gravitraps in 2013, the GAI has been used as the national vector index for monitoring the spatio-temporal variability of the adult Ae. aegypti population in Singapore, replacing the previously used house index, which is no longer sensitive for dengue risk assessment. Our study showed that areas with high GAI were associated with higher dengue case count. Therefore, the GAI can be used as a risk factor and be incorporated into dengue forecast models as well as the spatial dengue risk map, that had been developed to predict dengue incidence and to guide the prioritization of resources respectively [26,45,46]. Besides being an efficient surveillance tool, Gravitrap appears to have an impact on dengue transmission, hypothetically due to the removal of infected mosquitoes. This is consistent with the recent study by Barrera et al., which shows that adult mosquito traps can protect humans from disease acquired from infected Ae. aegypti mosquitoes [47].
Under the islandwide Gravitrap surveillance programme, NEA has progressively deployed Gravitraps across all apartment blocks in Singapore since 2017, with more than 50,000 Gravitraps deployed across 9,000 apartment blocks currently. The GAI data has been used to alert stakeholders and community to proactively reduce mosquito breeding [48–50]. Areas with high GAI received more house inspections. Information on areas with high GAI is also made publicly available through NEA website and myENV app (an application by NEA), to nudge the community to conduct pre-emptive source reduction even before any report of dengue transmission [51,52].
The re-emergence of dengue fever in many countries, despite low immature indices, has warranted the need for a more effective index for dengue vector surveillance and control. The GAI, which is more relevant for dengue risk assessment, is recommended as an indicator for decision making in vector control efforts.
Supporting information
S1 Fig. Monthly rainfall (mm) in Singapore (2014–2016).
https://doi.org/10.1371/journal.pntd.0008528.s001
(TIF)
S2 Fig. Temporal trend of the weekly GAI of each treatment site (2014–2016).
https://doi.org/10.1371/journal.pntd.0008528.s002
(TIF)
Acknowledgments
The authors would like to thank the following people who have contributed to the project; Communicable Disease Division of Ministry of Health, Singapore, for providing the dengue case data, staff of Environmental Health Institute, the Applied Entomology team for Gravitrap surveillance and adult mosquito identification the Entomological Taxonomy team for identification of mosquito larval samples.
References
- 1. Xi Z, Ramirez JL, Dimopoulos G. The Aedes aegypti toll pathway controls dengue virus infection. PLoS Pathog. 2008;4 7:e1000098. pmid:18604274
- 2. Ferreira GL. Global dengue epidemiology trends. Rev Inst Med Trop Sao Paulo. 2012;54:5–6. pmid:22370747
- 3. Bhatt S, Gething PW, Brady OJ, Messina JP, Farlow AW, Moyes CL, et al. The global distribution and burden of dengue. Nature. 2013;496 7446:504. pmid:23563266
- 4. Gubler DJ. Epidemic dengue/dengue hemorrhagic fever as a public health, social and economic problem in the 21st century. Trends Microbiol. 2002;10 2:100–3. pmid:11827812
- 5. Gubler DJ. Dengue and dengue hemorrhagic fever. Clin Microbiol Rev. 1998;11 3:480–96. pmid:9665979
- 6. Rosen L, Shroyer DA, Tesh RB, Freier JE, Lien JC. Transovarial transmission of dengue viruses by mosquitoes: Aedes albopictus and Aedes aegypti. Am J Trop Med Hyg. 1983;32 5:1108–19. pmid:6625066
- 7.
World Health Organization. Dengue: guidelines for diagnosis, treatment, prevention and control. Geneva: WHO Library. 2009:10–2.
- 8. Benedict MQ, Levine RS, Hawley WA, Lounibos LP. Spread of the tiger: global risk of invasion by the mosquito Aedes albopictus. Vector Borne Zoonotic Dis. 2007;7 1:76–85. pmid:17417960
- 9. Akiner MM, Demirci B, Babuadze G, Robert V, Schaffner F. Spread of the invasive mosquitoes Aedes aegypti and Aedes albopictus in the Black Sea region increases risk of chikungunya, dengue, and Zika outbreaks in Europe. PLoS Negl Trop Dis. 2016;10 4:e0004664.
- 10. Pandey BD, Morita K, Santa Raj Khanal TT, Miyazaki I, Ogawa T, Inoue S, et al. Dengue virus, Nepal. Emerg Infect Dis. 2008;14 3:514. pmid:18325280
- 11. Sousa C, Clairouin M, Seixas G, Viveiros B, Novo M, Silva A, et al. Ongoing outbreak of dengue type 1 in the Autonomous Region of Madeira, Portugal: preliminary report. Euro Surveill. 2012;17 49:20333. pmid:23231893
- 12. Dhimal M, Gautam I, Kreß A, Müller R, Kuch U. Spatio-temporal distribution of dengue and lymphatic filariasis vectors along an altitudinal transect in Central Nepal. PLoS Negl Trop Dis. 2014;8 7:e3035. pmid:25078276
- 13. Gautam I, Dhimal MN, Shrestha SR, Tamrakar AS. First record of Aedes aegypti (L.) vector of dengue virus from Kathmandu, Nepal. J Nat Hist Mus. 2009;24 1:156–64.
- 14. Almeida AP, Gonçalves Y, Novo M, Sousa C, Melim M, Gracio AJ. Vector monitoring of Aedes aegypti in the Autonomous Region of Madeira, Portugal. Weekly releases (1997–2007). 2007;12 46:3311.
- 15. Lee K-S, Lo S, Tan SS-Y, Chua R, Tan L-K, Xu H, et al. Dengue virus surveillance in Singapore reveals high viral diversity through multiple introductions and in situ evolution. Infect Genet Evol. 2012;12 1:77–85. pmid:22036707
- 16. Rajarethinam J, Ang L-W, Ong J, Ycasas J, Hapuarachchi HC, Yap G, et al. Dengue in Singapore from 2004 to 2016: Cyclical epidemic patterns dominated by serotypes 1 and 2. Am J Trop Med Hyg. 2018;99 1:204–10. pmid:29848407
- 17. Hapuarachchi HC, Koo C, Rajarethinam J, Chong C-S, Lin C, Yap G, et al. Epidemic resurgence of dengue fever in Singapore in 2013–2014: a virological and entomological perspective. BMC Infect Dis. 2016;16 1:300.
- 18.
Singapore Department of Statistics [Internet]. Population trends 2019 [cited 09 Oct 2019]. Available from: https://www.singstat.gov.sg/find-data/search-by-theme/population/population-and-population-structure/publications-and-methodology
- 19. Low S-L, Lam S, Wong W-Y, Teo D, Ng L-C, Tan L-K. Dengue seroprevalence of healthy adults in Singapore: serosurvey among blood donors, 2009. Am J Trop Med Hyg. 2015;93 1:40–5. pmid:26013376
- 20. Yew YW, Ye T, Ang LW, Ng LC, Yap G, James L, et al. Seroepidemiology of dengue virus infection among adults in Singapore. Ann Acad Med Singapore. 2009;38 8:667–75. pmid:19736569
- 21. Paz-Soldan VA, Yukich J, Soonthorndhada A, Giron M, Apperson CS, Ponnusamy L, et al. Design and testing of novel lethal ovitrap to reduce populations of Aedes mosquitoes: Community-based participatory research between industry, academia and communities in Peru and Thailand. PLoS One. 2016;11 8:e0160386. pmid:27532497
- 22. Sivagnaname N, Gunasekaran K. Need for an efficient adult trap for the surveillance of dengue vectors. Indian J Med Res. 2012;136 5:739.
- 23. Lacroix R, Delatte H, Hue T, Dehecq J-S, Reiter P. Adaptation of the BG‐Sentinel trap to capture male and female Aedes albopictus mosquitoes. Med Vet Entomol. 2009;23 2:160–2. pmid:19493196
- 24. Lee C, Vythilingam I, Chong C-S, Razak MAA, Tan C-H, Liew C, et al. Gravitraps for management of dengue clusters in Singapore. Am J Trop Med Hyg. 2013;88 5:888–92. pmid:23478581
- 25. Ng L, Tan H, Tan L, Chong C, Ho D. Evolving dengue control programme in Singapore. Epidemiol News Bull. 2016;42:11–5.
- 26. Ong J, Liu X, Rajarethinam J, Kok SY, Liang S, Tang CS, et al. Mapping dengue risk in Singapore using Random Forest. PLoS Negl Trop Dis. 2018;12 6:e0006587. pmid:29912940
- 27. Rattanarithikul R, Harbach RE, Harrison BA, Panthusiri P, Coleman RE, Richardson JH. Illustrated keys to the mosquitoes of Thailand. VI. Tribe Aedini. Southeast Asian J Trop Med Public Health. 2010; 41:1–225.
- 28. Ong J, Liu X, Rajarethinam J, Yap G, Ho D, Ng LC. A novel entomological index, Aedes aegypti Breeding Percentage, reveals the geographical spread of the dengue vector in Singapore and serves as a spatial risk indicator for dengue. Parasit Vectors. 2019;12 1:17. pmid:30621762
- 29.
Ministry of Health of Singapore [Internet]. Infectious Diseases Act [cited 09 Oct 2019]. Available from: https://www.moh.gov.sg/policies-and-legislation/infectious-disease-act.
- 30. Smith EP. BACI design. Wiley StatsRef: Statistics Reference Online. 2014.
- 31. Conner MM, Saunders WC, Bouwes N, Jordan C. Evaluating impacts using a BACI design, ratios, and a Bayesian approach with a focus on restoration. Environ Monit Assess. 2016;188 10:555.
- 32. de Loma TL, Osenberg CW, Shima JS, Chancerelle Y, Davies N, Brooks AJ, et al. A Framework for Assessing Impacts of Marine Protected Areas in Moorea (French Polynesia) 1. Pac Sci. 2008;62 3:431–42.
- 33. Rumbold D, Davis P, Perretta C. Estimating the effect of beach nourishment on Caretta caretta (loggerhead sea turtle) nesting. Restor Ecol. 2001;9 3:304–10.
- 34. Team RC. R: A language and environment for statistical computing. 2013.
- 35. de Moura Rodrigues M, Marques GRAM, Serpa LLN, de Brito Arduino M, Voltolini JC, Barbosa GL, et al. Density of Aedes aegypti and Aedes albopictus and its association with number of residents and meteorological variables in the home environment of dengue endemic area, São Paulo, Brazil. Parasit Vectors. 2015;8 1:115.
- 36. Bowman LR, Runge-Ranzinger S, McCall P. Assessing the relationship between vector indices and dengue transmission: a systematic review of the evidence. PLoS Negl Trop Dis. 2014;8 5:e2848. pmid:24810901
- 37. Sivagnaname N, Gunasekaran K. Need for an efficient adult trap for the surveillance of dengue vectors. Indian J Med Res. 2012;136 5:739. pmid:23287120
- 38. Maciel-de-Freitas R, Eiras ÁE, Lourenço-de-Oliveira R. Field evaluation of effectiveness of the BG-Sentinel, a new trap for capturing adult Aedes aegypti (Diptera: Culicidae). Mem Inst Oswaldo Cruz. 2006;101 3:321–5. pmid:16862330
- 39. Bhalala H, Arias JR. The Zumba mosquito trap and BG-Sentinel trap: novel surveillance tools for host-seeking mosquitoes. J Am Mosq Control Assoc. 2009;25 2:134–40. pmid:19653494
- 40. Eiras ÁE, Resende MC. Preliminary evaluation of the" Dengue-MI" technology for Aedes aegyptimonitoring and control. Cad Saude Publica. 2009;25:S45–S58. pmid:19287866
- 41. Rajarethinam J, Ong J, Neo ZW, Ng LC, Aik J. Distribution and seasonal fluctuations of Ae. aegypti and Ae. albopictus larval and pupae in residential areas in an urban landscape. PLoS Negl Trop Dis. 2020;14 4:e0008209. pmid:32310960
- 42. Duncombe J, Clements A, Davis J, Hu W, Weinstein P, Ritchie S. Spatiotemporal patterns of Aedes aegypti populations in Cairns, Australia: assessing drivers of dengue transmission. Trop. Med. Int. Health. 2013;18 7:839–49. pmid:23617766
- 43. Obenauer P, Kaufman P, Allan S, Kline D. Infusion-baited ovitraps to survey ovipositional height preferences of container-inhabiting mosquitoes in two Florida habitats. J Med Entomol. 2009;46 6:1507–13. pmid:19960705
- 44. Williams CR, Long SA, Russell RC, Ritchie SA. Optimizing ovitrap use for Aedes aegypti in Cairns, Queensland, Australia: effects of some abiotic factors on field efficacy. J Am Mosq Control Assoc. 2006;22 4:635–41. pmid:17304930
- 45. Shi Y, Liu X, Kok S-Y, Rajarethinam J, Liang S, Yap G, et al. Three-month real-time dengue forecast models: an early warning system for outbreak alerts and policy decision support in Singapore. Environmental health perspectives. 2015;124 9:1369–75. pmid:26662617
- 46. Chen Y, Ong JHY, Rajarethinam J, Yap G, Ng LC, Cook AR. Neighbourhood level real-time forecasting of dengue cases in tropical urban Singapore. BMC medicine. 2018;16 1:129. pmid:30078378
- 47. Sharp TM, Lorenzi O, Torres-Velasquez B, Acevedo V, Perez-Padilla J, Rivera A, et al. Autocidal gravid ovitraps protect humans from chikungunya virus infection by reducing Aedes aegypti mosquito populations. PLoS Negl Trop Dis. 2019;13 7.
- 48.
National Environment Agency, Singapore. Community Called To Do ‘Mozzie Wipeout’ For 14 days to Break Breeding Cycle. NEA News. 28 Feb 2016 [Cited 2020 Mar 01]. Available from: https://www.nea.gov.sg/media/news/news/index/community-called-to-do-mozzie-wipeout-for-14-days-to-break-breeding-cycle
- 49.
National Environment Agency, Singapore. NEA Urges Continued Vigilance To Avoid Surge in Dengue Cases in 2017. NEA News. 19 Jan 2017 [Cited 2020 Mar 01]. Available from: https://www.nea.gov.sg/media/news/news/index/nea-urges-continued-vigilance-to-avoid-surge-in-dengue-cases-in-2017
- 50.
National Environment Agency, Singapore. NEA Urges Continued Vigilance In Fight Against Dengue. NEA News. 20 May 2018 [Cited 2020 Mar 01]. Available from: https://www.nea.gov.sg/media/news/news/index/nea-urges-continued-vigilance-in-fight-against-dengue
- 51.
National Environment Agency, Singapore. Information On Areas With Higher Mosquito Population Now Available on MyENV App. NEA News. 20 Dec 2019 [Cited 2020 Mar 01]. Available from: https://www.nea.gov.sg/media/news/news/index/information-on-areas-with-higher-mosquito-population-now-available-on-myenv-app
- 52.
National Environment Agency, Singapore [Internet]. Areas with Higher Aedes aegypti Mosquito Population [Cited 2020 Mar 01]. Available from: https://www.nea.gov.sg/dengue-zika/Aedes