Previous studies have demonstrated contact irritant and spatial repellent behaviors in Aedes aegypti following exposure to sublethal concentrations of chemicals. These sublethal actions are currently being evaluated in the development of a push-pull strategy for Ae. aegypti control. This study reports on mosquito escape responses after exposure to candidate chemicals for a contact irritant focused push-pull strategy using varying concentrations and focal application.
Contact irritancy (escape) behavior, knockdown and 24 hour mortality rates were quantified in populations of female Ae. aegypti under laboratory conditions and validated in the field (Thailand and Peru) using experimental huts. Evaluations were conducted using varying concentrations and treatment surface area coverage (SAC) of three pyrethroid insecticides: alphacypermethrin, lambacyhalothrin and deltamethrin.
Under laboratory conditions, exposure of Ae. aegypti to alphacypermethrin using the standard field application rate (FAR) resulted in escape responses at 25% and 50% SAC that were comparable with escape responses at 100% SAC. Significant escape responses were also observed at <100% SAC using ½FAR of all test compounds. In most trials, KD and 24 hour mortality rates were higher in mosquitoes that did not escape than in those that escaped. In Thailand, field validation studies indicated an early time of exit (by four hours) and 40% increase in escape using ½FAR of alphacypermethrin at 75% SAC compared to a matched chemical-free control. In Peru, however, the maximum increase in Ae. aegypti escape from alphacypermethrin-treated huts was 11%.
Results presented here suggest a potential role for sublethal and focal application of contact irritant chemicals in an Ae. aegypti push-pull strategy to reduce human–vector contact inside treated homes. However, the impact of an increase in escape response on dengue virus transmission is currently unknown and will depend on rate of biting on human hosts prior to house exiting.
Dengue virus is spread by Aedes aegypti, a mosquito that prefers to feed on humans. Chemicals used at toxic levels is currently the only confirmed effective strategy for dengue vector control, but insecticide resistance issues are threatening this approach. Other chemical actions that break vector-human contact exist: contact irritant effects, causing escape from homes and spatial repellent effects, preventing house entry. These actions are being evaluated in the development of a push-pull strategy to target indoor resting sites (using contact irritants) and/or portals of house entry (using spatial repellents) at sublethal concentrations to push the vector away from the treated structure and associated human hosts. When combined with an attractant trap placed outdoors to pull the irritated/repelled vectors from the peridomestic environment, the integrated stimuli form a push-pull system that can be used to further enhance disruption of human-vector contact. Here we report on the quantification of contact irritancy (escape) behavior, knockdown and 24 hour mortality rates in populations of Ae. aegypti under both laboratory and field conditions. Evaluations were carried out against three pyrethroid insecticides. Findings indicate an increase in escape response using sublethal concentrations and focal application suggesting a potential role for contact irritants in a push-pull strategy.
Citation: Manda H, Shah P, Polsomboon S, Chareonviriyaphap T, Castro-Llanos F, Morrison A, et al. (2013) Contact Irritant Responses of Aedes aegypti Using Sublethal Concentration and Focal Application of Pyrethroid Chemicals. PLoS Negl Trop Dis7(2): e2074. https://doi.org/10.1371/journal.pntd.0002074
Editor: Pattamaporn Kittayapong, Mahidol University, Thailand
Received: July 11, 2012; Accepted: January 8, 2013; Published: February 28, 2013
This is an open-access article, free of all copyright, and may be freely reproduced, distributed, transmitted, modified, built upon, or otherwise used by anyone for any lawful purpose. The work is made available under the Creative Commons CC0 public domain dedication.
Funding: Funding for this research was supported by the Bill & Melinda Gates Foundation (Grant #48513). 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.
Dengue, transmitted primarily by Aedes aegypti mosquitoes, is the most important mosquito-borne viral disease affecting humans worldwide . It is caused by four serotypes that produce a spectrum of clinical illness ranging from unapparent or mild disease, to an influenza-like illness, to a fatal shock syndrome.
Due to the current lack of a licensed vaccine, dengue prevention is limited to vector control. Aedes aegypti control programs are based on two main targets: (1) the immature stages (egg, larvae, and pupae) through environmental management (source reduction), larvicides and/or biological control; and (2) the adult stage using space or residual sprays of chemical insecticides and more recently insecticide treated materials . Aedes aegypti has strong associations with human habitations, living and breeding very near or inside human dwellings –. This extensive use of the human indoor environment poses challenges to traditional adult control methods and as well as in devising new or improved methods to sufficiently reduce disease transmission risk . Pyrethroids have commonly been employed in dengue endemic countries such as Thailand and Peru for peridomestic and/or indoor residual/space-spraying to reduce adult mosquito populations , . However, despite the fact that selective use of pyrethroids and other residual insecticides applied indoors have successfully controlled Ae. aegypti and dengue –, outdoor and peridomestic space-spraying alone has often failed to achieve any meaningful control of indoor adult Ae. aegypti populations. This is because the chemical fails to reach the preferred resting sites inside homes ,  and indoor residual or space-spraying can be resource limited and hampered by poor public perception that limits indoor access  therefore reducing treatment coverage. However, the high affinity of Ae. aegypti for the human indoor environment also provides unique opportunities for innovative approaches to control the adult vector .
During dengue outbreaks, the methods of choice for emergency interventions remain outdoor ultra-low-volume (ULV) application of insecticides and/or indoor thermal fogging , . While effective, these interventions usually follow onset of epidemics, are difficult to implement in urban environments where Ae. aegypti is most common, and more importantly very difficult to sustain . For these and other reasons such as insecticide resistance , , there is a need for proactive measures that have potential to prevent virus transmission and avert dengue epidemics as well as reduce selection pressure for insecticide resistance.
Research has shown that the impact of public health insecticides on vector populations is much more complex than simple toxic actions (i.e., direct mortality following exposure). There are other chemical actions that exist to break human-vector contact –. Such actions include among others, contact irritant effects, causing an escape response from homes, and initiating a spatial repellent or deterrent effect, thereby preventing house entry , , . Both contact irritant and spatial repellent behaviors have been demonstrated in vector populations using sublethal chemical concentrations under both laboratory and field environments , . The importance of these findings is accentuated as both organochlorine resistant and pyrethroid tolerant Ae. aegypti were included in the vector test populations, indicating that behavior-modifying actions exist even when mosquitoes are not susceptible to their toxic actions and as such, may play a role in insecticide resistance management. Current issues of insecticide resistance are creating a necessity for development of new strategies  and/or chemical products that act to prevent vector biting. Such approaches will require an understanding of the range of biological actions (independent from toxicity) elicited by vectors exposed to chemical tools to help drive such methods for disease control.
Both contact irritancy and spatial repellency are currently being evaluated in the development of a push-pull strategy for Ae. aegypti control. The goal of the push-pull strategy is to reduce the probability of human-vector contact and therefore dengue virus transmission. The approach is to target preferred indoor resting sites (using contact irritants) and house portals of entry (using spatial repellents) using minimum effective chemical concentration and treatment surface area coverage (SAC) to make these sites unsuitable, and thereby drive (push) the vector away from the treated structure and human hosts in a cost-effective manner. To further enhance the effect of a push response, an attractant trap is placed outdoors to pull the irritated/repelled vectors from the peridomestic environment thereby disrupting human-vector contact in the peridomestic environment. However, a component to system success based on a contact irritant push element is the quantification of a contact irritant response - movement of Ae. aegypti test populations away from a chemical source following tarsal contact–when less than 100% of a surface is treated (i.e. focal application). Target application could prove cost-effective; however, untreated sites inside homes may serve as refuge locations for exposed vectors thereby diminishing efficacy of the approach.
Our previous study quantified Ae. aegypti resting behavior under laboratory conditions following exposure to chemical-treated surfaces at various treatment coverage area (100%, 75%, 50% and 25%) to define the effects of “safe sites” (untreated surfaces) on irritancy behavior . Results indicated that when preferred Ae. aegypti resting sites were treated with irritant chemicals, even at a treatment coverage of 25%, test populations did not simply move to untreated areas but became agitated, using increased flight as a proxy indicator. It is this contact irritant response that may result in an escape behavior and could be exploited as one type of push component in a push-pull strategy.
The objectives of the current study were to quantify contact irritancy (escape) response, knockdown, and 24 hour mortality rates in populations of female Ae. aegypti. Evaluations were carried out at varying chemical concentrations and treatment surface area coverage using three standard pyrethroid insecticides: alphacypermethrin, lambdacyhalothrin and deltamethrin. We present findings from the laboratory and two field sites (Thailand and Peru) where validation studies using experimental huts were conducted.
Aedes aegypti test populations (F2-F5 generations) from Iquitos, Peru (PERU strain) were used for all laboratory experiments. Larvae were reared from eggs shipped to the Uniformed Services University of the Health Sciences (USUHS), Bethesda, USA from the Naval Medical Research Unit No. 6 (NAMRU-6) Iquitos Entomology Laboratory, Iquitos, Peru (INRENA authorization number 128-2007-INRENA-IFFS-DCB, permit number 000703-AG-DGFFS), following previously described protocols . Females (4–7 days old) were provided with sugar pads saturated in a 10% sucrose solution until 24 hours prior to the day of testing. The USUHS colonies were maintained using a membrane blood-feeding system until the F5 generation at which time the colony was refreshed with F1 field material to control for behavioral comparability between laboratory and field populations.
Aedes aegypti were collected as immatures from experimental hut locations: Pu Teuy Village, Kanchanaburi Province, Thailand (THAI strain); and Iquitos, Peru (PERU strain). Larval populations were reared to adults at respective field insectaries using site-specific established protocols and colonized until the F5 generation. Aedes aegypti from Pu Teuy Thailand has been described as pyrethroid tolerant , ; while a recent survey from neighborhood sites in Iquitos, Peru have reported Ae. aegypti populations susceptible to pyrethroids (Vasquez La Torre, personal communication). As with laboratory studies, mosquito test populations were maintained with sugar pads saturated in a 10% sucrose solution until 24 hours prior to day of testing. Test cohorts (100 per hut) were marked with a unique color fluorescent dust (BioQuip Products, Inc., Gardena CA) to facilitate visual observation of mosquitoes during experimental hut trials. The use of a unique marking color per hut also allowed to determine the total number of mosquitoes that were present inside each hut during each experimental day, and thus defining proportion escape using a known denominator.
Chemicals evaluated were chosen based on current World Health Organization Pesticide Evaluation Scheme (WHOPES) recommendations and/or historical use in vector control programs . Compounds were acquired as neat grade material purchased from Sigma-Aldrich (St. Louis, MO): alphacypermethrin (CAS 67375-30-8), lambdacyhalothrin (CAS 91465-08-6), and deltamethrin (CAS 52918-63-5). Test concentrations evaluated included WHO recommended field application rates (FAR) and ½FAR; where FAR = 7.2 nmol/cm2 (0.03 g/m2) for alphacypermethrin and lambdacyhalothrin, and 4.9 nmol/cm2 (0.025 g/m2) for deltamethrin.
The previously described box assay was used for all laboratory evaluations . Briefly, the assay is composed of metal and Plexiglas chambers (30 cm3) that are joined together using draw latches. The metal test chamber is fitted with textile panels (either chemical-free or treated) and has a funneled exit portal through which mosquitoes can escape into the Plexiglas receiving chamber. The metal test chamber is covered with a Plexiglas lid to facilitate viewing of mosquito behavior during testing, as well as, a removable tinted lid that can be added to maintain darkness throughout the test procedure as desired. A full description of the assay along with accompanying standard operating procedures can be found at www.usuhs.mil/pmb/gsvc.
Contact irritant assay.
Laboratory studies were conducted using both black and white cotton fabric (Natural Charm 43/44″ wide 100% cotton 68×68 D/R-black and white, Bruce Variety, Bethesda, MD, USA) based on results from previous Ae. aegypti resting preference evaluations . All fabric pieces were treated approximately 30 min prior to initiating the first assay replicate and allowed to air-dry for at least 15 min prior to inserting it into the test chambers. New fabric panels were prepared daily. Treated and chemical-free cotton were fitted into the metal chamber at 100% dark (D), 100% light (L), and 75%∶25%, 50%∶50%, and 25%∶75% D∶L surface area coverage (SAC) ratios . Only dark material strips were treated with chemical solutions except during 100%L evaluations. Fabric panels were attached to assay walls using magnets. Groups of 20 female mosquitoes were introduced into the metal chamber and allowed to rest for 30 sec after which time the funnel gate linking the metal and Plexiglas chambers was opened to allow mosquito escape during a 10 min sampling period. The following data was then collected: 1) the number of Ae. aegypti in the Plexiglas chamber (i.e., escaping); 2) the number of mosquitoes within the metal chamber (mosquitoes that did not escape) and; 3) knockdown (KD) (defined as mosquitoes lying on their side or back that are unable to right themselves) in both clear and metal chambers. Mosquitoes were immediately removed from the assay using vacuum power hand aspirators and placed into containers labeled according to the respective chamber and maintained at 28°C and 80% RH to monitor 24 hour mortality. A total of 6 replicates were performed for each chemical concentration and D∶L coverage. A matched control assay fitted with acetone-only treated fabric at the same D∶L coverage was conducted simultaneously for each replicate. All testing was performed under controlled temperature (28–30°C) and relative humidity (50–60%) conditions. Box assays were cleaned with a 10% bleach solution at the end of each testing day to control for residual chemical and allowed to air-dry overnight before reuse.
Trials were conducted in both Thailand and Peru using experimental huts fitted with window and door interception traps. Three (Thailand) and five (Peru) portable huts were constructed using dimensions and materials that mimic indigenous homes at each site (Figure 1). Details of the experimental hut and intercept trap design in Thailand have been previously described . In Peru, the huts measured 4 m wide×6 m long×6 m height. Each hut had two windows (96 cm wide×96 cm height) and two doors (1 m wide×2 m height); one window and one door each at the front and the back, which were fitted with interception traps. At both field sites, the huts were positioned on raised platforms 30 cm above ground. The support columns for the platform sit atop cement ant traps to prevent predation on indoor KD mosquitoes. Floors were covered with white plastic sheeting to facilitate the detection of KD responses. Huts at both locations contained metal frame panels with wire-mesh backing positioned along the interior walls. Treated fabric panels were fixed to these metal panels using magnets, thereby avoiding chemical contact with the wall surface and potential contamination during subsequent chemical testing or treatment concentration. Environmental parameters of indoor/outdoor temperature and relative humidity were recorded using HOBO data loggers (series H08-004-02 and H21-001, respectively). HOBO U30/NRC Data Logging Weather Stations (Onset Computer Corporation Cape Cod, MA, USA) were used at both sites and were positioned centrally to the experimental huts.
Black and white cotton (Consorcio la Parcela Products, Ate, Lima, Peru; size 39.4×0.8/inch); and green and white polyester (BioQuip Products, Rancho Dominguez, CA, USA; mesh size 24×20/inch) fabric panels were used in Peru and Thailand, respectively. Experimental design for measuring mosquito escape behavior followed previously established protocols . Briefly, fabric panel strips were measured to cover a specific surface area coverage (SAC) of interior hut walls. Chemical solutions were prepared using either acetone (in Thailand) or absolute ethanol (in Peru) to test concentration and applied to fabric panels using a pipette. Additional fabric panels were treated with solvent only, to serve as matched chemical-free controls. Panels were treated no more than 48 hours prior to initiating the first replicate of a trial. Following treatment, the fabric was wrapped in aluminum foil and placed under cold storage (4°C) for transport to the field. The day before testing, chemical-treated and chemical-free fabric panels were affixed onto the metal frames inside each hut at 100% D, 75%∶25%, 50%∶50%, and 25%∶75% D∶L ratios where only dark fabric was chemical-treated. A matched control hut with similar SAC was performed simultaneously for each D∶L trial using solvent-only treated fabric.
Interception traps were affixed on the outside of doors and windows to capture exiting mosquitoes. Three to seven day-old marked female Ae. aegypti (100 per hut) were released inside each hut at 05.30 Hrs each experimental day. An additional container holding 25 marked mosquitoes was positioned in the center of each hut to serve as an internal control for monitoring KD due to indoor environmental conditions. During testing, one person was positioned indoors underneath an untreated bed net to generate host cues and monitor hourly KD. From 06.00 Hrs–18.00 Hrs at 20 min (Thailand) and 30 min (Peru) intervals, collector pairs located outside each hut removed mosquitoes within interception traps. Captured mosquitoes were placed into individual holding cups labeled by hut, trap number and time. At the top of each hour, all KD mosquitoes on the floor were collected and placed into holding cups labeled by hut and time. Both escape and KD mosquito samples were provided with cotton pads soaked in 10% sugar solution and held overnight in field insectaries to monitor 24 hour mortality. Four (Thailand) or five (Peru) replicates (i.e. experimental days) were performed for each experimental trial. Outdoor collector pairs rotated between huts every sampling period and indoor hosts at mid-day during an experimental day to control for individual bias. At the end of each experimental day, all mosquitoes that remained inside the huts were collected using backpack (Thailand) and Prokopack (Peru)  aspiration. The following treatments were tested in Thailand: alphacypermethrin at FAR and ½FAR at 75% D∶L SAC; and in Peru: alphacypermethrin at FAR and ½FAR at 100%, 75%, 50%, and 25% D∶L SAC.
All analyses were performed using SAS v. 9.2 software . Proportional data were subjected to arcsine square root transformation before statistical analysis. Output tables represent back-transformed values. Mean percentage escaping (or corrected percentage escaping) was obtained from the number escaping in the treatment over the number released after correcting for the number escaping in the control and KD in the metal test chambers). Knockdown and 24 hour mortality rates of populations that escaped and those that did not escape were corrected based on measurements from populations in control assays using Abbott's formula . For each chemical dose and SAC ratio trial, the difference between the number escaping from treated and control test chambers; and the difference between KD or dead in mosquitoes that escaped and those that did not escape were analyzed using the Wilcoxon 2-sample test as previously described , , . Variations in the percentage of mosquitoes escaping, KD and dead after 24 hours per trial were analyzed for each chemical by 2-way analysis of variance (ANOVA) with 2 main factors (treatment concentration and surface area coverage). For those chemicals that showed significant variations, an additional one-way ANOVA was conducted to examine the main factors (treatment concentration or SAC ratio), independently, on percentage escaping, KD and mortality. Means were separated using t-test and Sheffe's test (α = 0.05).
The mean daily percentages of mosquitoes that escaped, indoor KD and 24 hour mortality rates from those collected inside the huts (mosquitoes that did not escape) and those that escaped were compared between treatment and control huts using one-way ANOVA with means separated using Student Newman Keuls (SNK) tests (α = 0.05). The percentage of mosquitoes that escaped was compared between huts at three time periods: 06.00–10.00 Hrs, 11.00–14.00 Hrs and 15.00–18.00 Hrs corresponding to expected morning, mid-day and afternoon Ae. aegypti resting behavior patterns (Castro et al. unpublished data). Percentage escape was calculated using the number of mosquitoes that escaped over the number of mosquitoes that were available to escape (total number of mosquitoes recaptured from the hut each day minus number knockdown within the hut).
The mean number of female Ae. aegypti escaping in the treatment and matched control assays, with corrected percentage escaping for all trials is presented in Tables 1–3. In general, escape was higher in treatment assays as compared to matched controls. Most importantly, significant escape response was observed at ½FAR and/or at SAC less than 100% for each pyrethroid evaluated (Tables 1–3). Against alphacypermethrin treatment, corrected percent escape ranged from 8–49% with highest responses observed at FAR for all SAC evaluated (Table 1). Percent escape was comparable among all treatment coverages at the ½FAR dose (Table 1). With lambdacyhalothrin and deltamethrin treatments, corrected percent escape ranged from 1–59% (Table 2) and from −1–40% (Table 3), respectively. At each treatment concentration, escape response was highest using 100%L SAC, while for each treatment coverage (except 100%L), escape response was comparable among doses (Tables 2 and 3).
Knockdown and 24 hour mortality.
In most trials, KD and 24 hour mortality rates were higher in Ae. aegypti that did not escape than in those that escaped (Table S1 and Table 4, respectively); however, there was minimal KD observed overall in test populations that escaped with rates ranging from 0–25% in all test chemicals. Highest KD was observed using alphacypermethrin at 100%D SAC and FAR (Table S1). No KD was observed in mosquitoes that escaped against lambdacyhalothrin or deltamethrin (Table S1). For mosquitoes that did not escape, percentage KD ranged from 0–48%, 0–15% and 0–1% using alphacypermethrin, lambdacyhalothrin and deltamethrin, respectively, with highest rates occurring in alphacypermethrin trials using FAR (Table S1). Most importantly, KD observed in both mosquito cohorts that escaped and those that did not were comparable between 100% and 25% SAC for each test concentration and chemical evaluated.
In general, 24 hour mortality rates were highest in mosquitoes that did not escape compared to Ae. aegypti test populations that escaped the laboratory assay (Table 4). Mortality ranged from 0–100%, 0–25%, and 0–7% in mosquitoes that escaped and from 45–84%, 0.5–28%, and 1–16% in those that did not escape for alphacypermethrin, lambdacyhalothrin and deltamethrin, respectively. For alphacypermethrin, highest mortality was observed at FAR 100%D in mosquitoes that escaped and 25%D in those that did not escape, although the latter was statistically comparable among all SAC using both test concentrations (Table 4). Percentage mortality in mosquitoes that escaped was comparable among all SAC using each test concentration of lambdacyhalothrin and deltamethrin (Table 4). Trials using ½FAR lambdacyhalothrin and deltamethrin indicated percentage mortality in mosquitoes that did not escape varied significantly among SAC, with mortality significantly low at 25% (lamdacyhalothrin) and 50% (deltamethrin) SAC (Table 4).
In comparison to the matched control hut, there was a 42.3% and 46.4% increase in the percentage of marked Ae. aegypti females that exited huts containing fabric panels treated at FAR and ½FAR alphacypermethrin, respectively (Table 5); although these results were statistically comparable among treatment and control conditions (P = 0.4). In both treatment huts, the percentage of KD mosquitoes collected indoors were comparable but both significantly higher compared to the control hut (P<0.01). Similar results were obtained from analyses of mosquitoes collected inside the exit traps that were dead 24 hours post-escape (P = 0.02) (Table 5). In both treatment huts, more mosquitoes exited during the early sampling periods of 06.00–14.00 Hrs (10.0%±3.8 and 9.7%±1.2 for FAR and ½FAR, respectively) as compared to the untreated control hut (1.9%±1.2) (P = 0.05), which had highest escape later in the day (15.00–18.00 Hrs) (Table S2). Mean indoor temperature (P = 0.9) and relative humidity (P = 0.6) readings were comparable among all huts during the trials (Table 5).
The percentage of Ae. aegypti that exited from huts treated with alphacypermethrin at FAR (at all SAC) (P = 0.8) and percentage dead 24 hours post-escape (P = 0.3) was comparable to control, with 0–11% increase in escape compared to the untreated hut (Table 6). However, the percentage of KD mosquitoes inside the huts (P<0.01) and subsequent 24 hour mortality in the same KD populations (P<0.01) were significantly higher in all the huts treated with chemical (even 25% SAC) than in the untreated hut indicating a chemical effect (Table 6). Similar results in escape (P = 0.2) and mortality (P = 0.9) rates 24 hours post-escape were observed using alphacypermethrin at ½FAR treatment (Table 6). Unlike the FAR trials, percentage KD inside the huts (P = 0.2) and 24 hour mortality rates (P = 0.4) in these KD populations were comparable between treated and untreated huts at all SAC (Table 6). The percentage of exiting mosquitoes during each time period was comparable among treated and the untreated hut for each chemical concentration evaluated (Table S3). Mean indoor daily temperature was comparable among huts during both FAR and ½FAR trials (P = 0.6 and P = 0.2, respectively), while RH significantly varied among huts during both experimental trials (P<0.01) (Table 6).
The objective of the current study was to evaluate the efficacy of contact irritant chemicals to elicit Ae. aegypti escape responses from a treated space under both laboratory and field conditions. The approach included treating at concentrations below standards for insect toxicity and at surface area coverage below 100%. The overall goal was to describe the potential of focal application of irritant compounds to drive sublethal vector behaviour (such as escape) that could disrupt human-vector contact. If evident, the role for these approaches in novel control strategies would be strengthened.
In the laboratory, significant escape responses were observed at treatment concentrations equal to but also below corresponding WHO recommended field application rates for the test compounds based on chemical levels required for vector mortality . Our field studies in Thailand corroborate this finding with a 46% increase in the percentage of Ae. aegypti exiting a hut treated with alphacypermethrin at ½FAR and significantly more mosquitoes exiting the treated hut prematurely, by four hours, compared to the control hut. The time of vector escape from inside a treated space is as important as the total density of escape since the faster irritation and escape occurs, the greater the probability that contact (i.e., biting) of the human host has or can been prevented. Combined, these results are similar with previous studies conducted in Thailand that found significant escape response in an Ae. aegypti local strain to alphacypermethrin tested at concentrations below the WHO FAR and continue to support the fact that insecticides can be used to elicit irritant actions even if applied at concentrations below toxic levels , , .
The current study also evaluated the escape behavior of Ae. aegypti in response to different treatment surface area coverage (SAC) of a space using dark∶light fabric panels, where chemical was applied on dark surfaces only representing focal application. The approach of using contrasting colors and treating black fabric alone was based on exploiting known behavior that Ae. aegypti adults prefer to rest in dark, damp locations in households, and are generally attracted to black colors –. The evaluation of varying SAC was founded on the theory that taking advantage of resting characteristics could result in desired outcomes achieved with less than 100% treatment of indoor resting sites. A previous laboratory study  reported on the resting patterns of Ae. aegypti using different dark: light SAC ratios of sublethal concentrations of various pyrethroid chemicals. Results from these experiments indicated that Ae. aegypti preferred to rest on dark versus light-colored surfaces, even at the lowest 25% dark coverage and that when preferred Ae. aegypti resting sites (i.e., dark surfaces) were chemical-treated, mosquitoes did not significantly alter their resting behavior to safe-sites (untreated areas). Instead, they became agitated, and took to flight rather than seeking out alternate resting sites. However, in that study, the test populations were not provided the opportunity to escape from the test arena so measurements of exiting were not captured .
We report here that exposure of Ae. aegypti females to alphacypermethrin using FAR at 25% and 50% SAC resulted in escape responses that were comparable with those reported at 100% SAC. In addition, escape responses greater than controls were also observed using treatment coverage at <100% at the ½FAR sublethal concentration of all test compounds. It is noted that in most trials, escape responses were highest when using treated 100%L SAC. This agrees with previous data  that showed less overall Ae. aegypti resting on light versus dark fabric material. Higher escape responses on 100%L SAC may be due to the combination effect of light color (reduction of preferred resting sites) and the irritating chemical. Field studies from Thailand also indicated a substantial premature escape and an average of 40% increase in exiting an alphacypermethrin-treated hut using 75% SAC. Combined, these results demonstrate that, irrespective of treatment concentrations, substantial escape responses can be elicited in Ae. aegypti test populations at treatment coverage below the traditional 100% SAC used in indoor residual spray campaigns. These findings agree with studies conducted in southern Mexico using selective spraying to target the preferred resting sites of An. albimanus which showed that reduced coverage application was as effective as full spraying in controlling adult populations . In addition, preferred resting sites, as determined by landing frequencies, times of resting, preferred surface types and resting heights were not modified by the insecticide applications. In essence, the preferred resting sites of the mosquitoes did not change, even on insecticide-treated surfaces after four successive spray rounds .
The use of this approach - sublethal concentration and <100% treatment area coverage - against Ae. aegypti, or other vector species, if effective, holds the potential for reducing programmatic costs due to reduced requirements for active ingredient. Arredondo-Jimenez et al (1995) showed that selective spraying of preferred resting sites required 46% less time and cost 67% less than conventional full-spraying. Cost and manpower constraints could be further reduced by integrating the proper active ingredients into consumer-based products (pre-treated material strips, plastic sheeting, tiles, wallpaper, paint, etc.) thereby sharing vector control costs with community members. Initial focus group studies evaluating acceptability of sublethal approaches to vector control have indicated that treated materials are viable options for chemical application inside homes . While all trials in the current study were performed with fresh chemical applications, the pyrethroids evaluated are known to have residual properties , –, therefore their effectiveness over a long period of time would be anticipated, further supporting a cost-effective approach. In addition, such control strategies may increase sustainability of an intervention through home ownership, and broaden the delivery platforms available for traditional house treatment. This concept recognizes that householders in many developing countries already buy pesticides to control insects in the homes , , and there are advantages in engaging market forces to promote such products, rather than relying solely on public health appeals.
Experimental hut experiments in Peru showed only an 8.7% increase in escape from huts treated with alphacypermethrin at FAR using 75% SAC as compared to an untreated hut and no increase in escape rate when alphacypermethrin was used at ½FAR, irrespective of the SAC. In addition, the time of exit in Peru trials was comparable between treatments and chemical-free control. These results are in contrast to both laboratory and Thailand field trials that showed substantial increases in escape rates for the same compound and treatment coverage in relation to controls. These differences are most likely due to the naturally high exit rate of Ae. aegypti observed during baseline studies in Peru when no chemicals were used (Castro et al. unpublished data), making any impact due to chemical difficult to measure, and the variation in fabric material type used between the two field sites (polyester in Thailand versus cotton in Peru). Differences in material type may lead to differences in chemical uptake, absorption and release. Previous studies ,  showed less mosquito KD and mortality when locally sourced mosquito nets (treated with K-O Tab 1-2-3 ‘dip-it-yourself’ long-lasting formulation) were made from cotton as opposed to polyester. Although cotton retained a higher concentration of insecticide, the majority of the chemical is bound within the cotton fibers rather than remaining on the surface where the mosquitoes make contact . However, the chemical was shown to be available for uptake and effect based on indoor KD rates observed within alphacypermethrin-treated huts. The difference between our laboratory findings, where minimal escape occurred from control chambers, and results from our field studies in Peru, where high escape occurred from chemical-free huts, most likely reflects influences from environmental parameters such as temperature and humidity in the micro-environment of the experimental huts. A previous study in Thailand demonstrated how Ae. aegypti exit behavior is affected by ambient environmental factors of temperature and humidity . The possibility that behavioral variation between the Thailand and Peru study sites in the current study is the result of the geographically different strains is unknown. These results illustrate that despite considerable progress in the field of vector behavior as a whole, there remains much to understand on how external and genetic factors affect the biology and behavior of important disease vectors.
Both laboratory and field results from the current study showed that KD and mortality were considerably low (<90%) in our Ae. aegypti test populations despite using FARs that are based on concentrations required to produce lethal outcomes (i.e. LD90) . Aedes aegypti THAI strain from Pu Tuey has been characterized as pyrethroid tolerant ,  while the PERU strain from Iquitos, Peru is most likely susceptible to the chemicals evaluated in this study (Vasquez La Torre, personal communication). It was therefore expected that KD and mortality would be low in test populations from Thailand. However, the low mortality rates observed in Ae. aegypti from Peru that did not escape in our laboratory tests could be explained by the minimum exposure time compared to standard resistance testing ,  (i.e. 10 min in a single contact irritancy replicate versus standard one hour used in toxicity assays); also by the potential difference in chemical uptake, absorption and release between the cotton material used in this study and bottle and/or filter test methods used in many resistance testing , .
More importantly, our Ae. aegypti assay cohorts from Thailand continued to exhibit a contact irritant response when exposed to test pyrethroids, despite indication of tolerance, thus indicating that a sublethal approach to vector control may be effective in locations where insecticide resistance occurs. It is worth noting that highest mortality was observed at FAR at 25%D in mosquitoes that did not escape. This finding suggests that although they did not escape, the mosquitoes rested on treated material long enough to receive a lethal dose. Combined, results suggests that escape can occur from a treated area at <100% SAC and of those that do not escape, resting on treated surfaces will continue as supported by a previous study  and result in mortality. As expected, we also show that KD and mortality were lower in mosquitoes that escaped as compared to those that did not escape. It is logical that killing those vectors that remain in a treated space (i.e. inside a home) and may have contact with humans will impact pathogen transmission. However, the role of escape and survival for disease management seems counterintuitive. We theorize that an escape and survival response could lead to reduced selection pressure for insecticide resistance which would not only potentially interrupt human-vector contact inside the home through contact irritancy but also extend the effective life of the chemical. Those mosquitoes that are irritated and exit have the opportunity to transfer their genetic material to the next generation, thereby potentially selecting for the mechanistic pathway that result in behavior modification – i.e., irritancy. Of course, this is dependent on linking the mode of action for contact irritancy to one that is dependent on up- or down-regulation of particular cascade drivers. Such information is not yet available. The inclusion of an outdoor trap, such as in a push-pull strategy, could serve to remove irritated vectors from the peridomestic environment thereby controlling potential movement to an untreated location and hosts.
Pertinent to the goal of developing a push-pull strategy, results presented here suggest a role for contact irritancy to drive vectors from a space occupied by a human host, and indicate efficacy using minimal chemical concentration (<LD90) and treatment coverage area (<100%). This in spite of the fact that the chemical delivery platform and formulation we evaluated were not formulated (i.e., optimized for chemical residuality). Although encouraging, current results suggest that behaviors observed in one species or strains might not translate into other mosquito species or strains found in different environmental settings. In addition, the inside environment of an experimental hut is much different than that of a local home; therefore future evaluations of contact irritant efficacy must be performed using indigenous houses against natural Ae. aegypti populations. Lastly, although contact irritancy may promote escape, it will be critical to measure the level of reduction, if any, in human-vector contact (i.e., biting) to truly understand the impact of sublethal behaviors on pathogen transmission. The irritant response must occur prior to blood meal acquisition. Due to this challenge, we are therefore currently applying a similar concept of sublethal concentrations and focal treatment application to the use of spatial repellent compounds in a push-pull strategy. This is an attempt to exploit the deterrent actions of chemicals to prevent Ae. aegypti entry into homes and thereby reduce indoor densities of mosquito vectors available for human-vector contact. The latter, if successful, may provide greater protection from pathogen transmission as compared to contact irritancy as repellency functions to provide a barrier of protection that is not dependent on vector contact with a treated surface .
Percentage knockdown Ae. aegypti1 that escaped and those that did not escape under laboratory conditions.
Percentage escape of Ae. aegypti1 against alphacypermethrin (75% SAC) at designated time periods in Thailand.
We thank Luana Arce and Tarra Foggie, Uniformed Services University of the Health Sciences for their technical support. We express our gratitude to Carlos Ique, Director of the Instituto Veterinario de Investigaciones (IVITA), Iquitos, Peru; and to the Armed Forces Development Command, Department of Defense, Sai Yok District, Kanchanaburi Province, Thailand for the use of land for study sites. Special thanks to the reviewers for valuable comments. Some of the authors are U.S. government employees. The opinions contained herein are the private views of the authors and are not to be construed as official or reflecting the views of the Department of Defense or the Uniformed Services University of the Health Sciences. Mention of specific commercial products does not constitute an endorsement or recommendation.
Conceived and designed the experiments: NLA JPG HM TC. Performed the experiments: HM PS FC SP NLA JPG TC. Analyzed the data: HM PS NLA JPG. Wrote the paper: HM NLA JPG TC RGB AM.
- 1. Gubler DJ (2002) Epidemic dengue/dengue hemorrhagic fever as a public health, social and economic problem in the 21st century. Trends Microbiol 10: 100–103.
- 2. Kroeger A, Lenhart A, Ochoa M, Villegas E, Levy M, et al. (2006) Effective control of dengue vectors with curtains and water container covers treated with insecticides in Mexico and Venezuela: cluster randomised trials. BMJ 332: 1247–52.
- 3. Gubler DJ (1997) Human behavior and cultural context in disease control. Trop Med Int Health 2 (11) A1–2.
- 4. Harrington LC, Scott TW, Lerdthusnee K, Coleman RC, Costero A, et al. (2005) Dispersal of the dengue vector Aedes aegypti within and between rural communities. Am J Trop Med Hyg 72: 209–220.
- 5. Scott TW, Amerasinghe PH, Morrison AC, Lorenz LH, Clark GG, et al. (2000) Longitudinal studies of Aedes aegypti L. (Diptera: Culicidae) in Thailand and Puerto Rico: blood feeding frequency. J Med Entomol 37: 89–101.
- 6. World Health Organization (1999) Prevention and control of dengue and dengue hemorrhagic fever: comprehensive guideline. WHO Regional Publication, SEARO, No. 29, New Delhi.
- 7. Chareonviriyaphap T, Aum-Aung B, Ratanatham S (1999) Current insecticide resistance patterns in mosquito vectors in Thailand, Southeast Asian. J Trop Med Public Health 30: 184–194.
- 8. Rodriguez MM, Bisset J, Ruiz M, Soca A (2002) Cross-resistance to pyrethroid and organophosphorus insecticides induced by selection with temephos in Aedes aegypti (Diptera: Culicidae) from Cuba. J Med Entomol 39: 882–888.
- 9. Vasquez-Prokopec GM, Kitron U, Montgomery B, Horne P, Ritchie SA (2010) Quantifying the spatial dimension of dengue virus epidemic spread within a tropical urban environment. Plos Negl Trop Dis 4 (12) e920.
- 10. Ritchie SA, Long S, Smith G, Pyke A, Knox TB (2004) Entomological invstigations in a focus of dengue transmission in Cairns, Queensland, Australia, by using the sticky ovitraps. J Med Entomol 41: 1–4.
- 11. Sulaiman S, Karim MA, Omar B, Jeffery J, Mansor F (1993) The residual effects of the synthetic pyrethroids lambda-cyhalothrin and cyfluthrin against Aedes aegypti (L.) in wooden huts in Malaysia. Mosq Borne Dis Bull 10: 128–131.
- 12. Lee HL, Khadri MS, Chiang YF (1997) Preliminary field evaluation of the chemical adulticidal, larvicidal, and wall residual activity of ULV-applied bifenthrin against mosquitoes. J Vector Ecol 22: 146–149.
- 13. Perich MJ, Sherman C, Burge R, Gill E, Quintana M, et al. (2001) Evaluation of the efficacy of lambdacyhalothrin applied as ultra-low-volume and thermal fog for emergency control of Aedes aegypti in Honduras. J Am Mosq Control Assoc 17: 221–224.
- 14. Reiter P, Gubler DJ (1997) Surveillance and control of urban dengue vectors. In Gubler DJ, Kumo G, editors. Dengue a nd dengue hemorrhagic fever. New York: CAB International pp. 425–462.
- 15. Mani TR, Arunachalam N, Rajendran R, Satyanarayana K, Dash AP (2005) Efficacy of thermal fog application of deltacide, a synergized mixture of pyrethroids, against Aedes aegypti, the vector of dengue. Trop Med Inter Health 10: 1298–1304.
- 16. Morrison AC, Zielinski-Gutierrez E, Scott TW, Rosemberg R (2008) Defining challenges and proposing solutions for control of the virus vector Aedes aegypti. PLos Med 5: e68 .
- 17. World Health Organization (1997) Dengue Hemorrhagic fever. Diagnosis, Treatment, Prevention and Control. Geneva: WHO.
- 18. Erlanger TE, Keiser J, Utzinger J (2008) Effect of dengue vector control interventions on entomological parameters in developing countries: a systematic review and meta-analysis. Med Vet Entomol 22: 203–221.
- 19. Muirhead-Thomson RC (1951) Mosquito behavior in relation to malaria transmission and control in the tropics. London: Edward Arnold.
- 20. Cullen JR, Dezulueta J (1962) Observation on the irritability of mosquitoes to DDT in Uganda. Bull WHO 27: 239–250.
- 21. Hamon J, Mouchet J, Brengues J, Chauvet G (1970) Problems facing anopheline vector control: vector ecology and behavior before and after application of control measures. Conference on Anopheline Biology and Malaria Eradication. Misc Pubs Entomol Soc Am 7: 28–41.
- 22. Elliot R (1972) The influence of mosquito behavior on malaria transmission. Am J Trop Med Hyg 21: 755–763.
- 23. Gillies MT (1988) Anopheline mosquitoes: vector behavior and bionomics. In: Wernsdofer WG, McGregor I, eds. Malaria, principles and practice of malariology. New York: Churchill Livingstone. pp 453–485.
- 24. Chareonviriyaphap T, Roberts DR, Andre RG, Harlan HJ, Manguin S, et al. (1997) Pesticide avoidance behavior in Anopheles albimanus, a malaria vector in the Americas. J Am Mosq Control Assoc 13: 171–183.
- 25. Grieco JP, Achee NL, Andre RG, Roberts DR (2000) A comparison study of house entering and exiting behavior of Anopheles vestitipennis (Diptera: Culicidae) using experimental huts sprayed with DDT or Deltamethrin in the southern district of Toledo, Belize, C.A. J Vector Ecol 25: 62–73.
- 26. Grieco JP, Achee NL, Chareonviriyaphap T, Suwonkerd W, Chauhan K, et al. (2007) A new classification system for the actions of IRS chemicals traditionally used for malaria control. Plos ONE Aug 8; 2: e716 .
- 27. Polsomboon S, Poolprasert P, Bangs MJ, Suwonkerd W, Grieco JP, et al. (2008) Effects of physiological conditioning on behavioral avoidance by using a single age group of Aedes aegypti exposed to deltamethrin and DDT. J Med Entomol 45: 251–259.
- 28. Achee NL, Sardelis MR, Dusfour I, Chauhan KR, Grieco JP (2009) Characterization of spatial repellent, contact irritant, and toxicant chemical actions of standard vector control compounds. J Am Mosq Control Assoc 25: 156–167.
- 29. Roberts DR, Alecrim WD, Hshieh P, Grieco JP, Bangs M, et al. (2000) A probability model of vector behavior: effects of DDT repellency, irritancy and toxicity in malaria control. J Vector Ecol 25: 48–61.
- 30. Kelly-Hope L, Ranson H, Hemingway J (2008) Lessons from the past: managing insecticide resistance in malaria control and eradication programmes. Lancet Infect Dis 8 (6) 387–9.
- 31. Manda H, Arce LM, Foggie T, Shah P, Grieco JP, et al. (2011) Effects of Irritant Chemicals on Aedes aegypti Resting Behavior: Is There A Simple Shift to Untreated “Safe Sites”? PLoS Negl Trop Dis 5 (7) e1243 .
- 32. McLean-Cooper N, Achee NL, Tolbert T, Grieco JP, Williams J (2008) Space optimization method of laboratory production of Aedes aegypti. J Am Mosq Control Assoc 24: 460–462.
- 33. Kanutcharee T, Achee NL, Bangs MJ, Grieco JP, Suwonkerd W, et al. (2009) Irritancy and repellency behavioral responses of three strains of Aedes aegypti exposed to DDT and α-cypermethrin. J Med Entomol 46: 1407–1414.
- 34. WHO [World Health Organization] (2009a) WHO recommended insecticides for indoor residual spraying against malaria vectors. Geneva, Switzerland: World Health Organization. Available: http://apps.who.int/malaria/cmc_upload/0/000/012/604/IRS Insecticides.htm. Accessed 2009 September 2.
- 35. Chareonviriyaphap T, Grieco JP, Suwonkerd W, Prabaripai A, Polsomboon S, et al. (2010) An improved experimental hut design for the study of Aedes aegypti (Diptera: Culicidae) movement patterns in Thailand. J Vector Ecol 35 (2) 428–31.
- 36. Vasquez-Procopec GM, Galvin WA, Kelly R, Kitron U (2009) A new, cost-effective, battery-powered aspirator for adult mosquito collections. J Med Entomol 46 (6) 1256–1259.
- 37. SAS Institute (1999) SAS Online Doc. Version 9.2. Cary, NC: SAS Institute.
- 38. Abbott WS (1925) A method of computing the effectiveness of an insecticide. J Econ Entomol 18: 265–267.
- 39. Grieco JP, Achee NL, Sardelis M, Chauhan K, Roberts DR (2005) A novel high-throughput screening system to evaluate the behavioral response of adult mosquitoes to chemicals. J Am Mosq Control Assoc 21: 404–411.
- 40. Sippell WL, Brown AW (1953) Studies of the responses of the female Aedes mosquito. Part V. The role of visual factors. Bull Entomol Res 43: 567–574.
- 41. Schoof HF (1967) Mating, resting habits and dispersal of Aedes aegypti. Bull World Health Org 36: 600–601.
- 42. Muir LE, Kay BH, Thorne MJ (1992) Aedes aegypti (Diptera: Culicidae) vision: response to stimuli from the optical environment. J Med Entomol 29: 445–450.
- 43. Arredondo-Jimenez JI, Bown DN, Rodriguez MH, Loyola EG (1995) Control of Anopheles albimanus mosquitos in southern Mexico by spraying their preferred indoor resting sites. Bull World Health Organization 73 (3) 329–337.
- 44. Paz-Soldan VA, Plasai V, Morrison AC, Rios-Lopez EJ, Guedez-Gonzales S, et al. (2011) Initial Assessment of the Acceptability of a Push-Pull Aedes Aegypti Control Strategy in Iquitos, Peru and Kanchanaburi, Thailand. Am J Trop Med Hyg 84 (2) 208–217.
- 45. Ansari MA, Razdan RK (2003) Bio-efficacy and operational feasibility of alphacypermethrin (Fendona) impregnated mosquito nets to control rural malaria in northern India. J Vector Borne Dis 40 (1–2) 33–42.
- 46. Yadav RS, Sampath RR, Sharma VP (2001) Deltamethrin treated bednets for control of malaria transmitted by Anopheles culicifacies (Diptera: Culicidae) in India. J Med Entomol 38 (5) 613–22.
- 47. Sampath TR, Yadav RS, Sharma VP, Adak T (1998) Evaluation of lambdacyhalothrin-impregnated bednets in a malaria endemic area of India. Part 1. Implementation and acceptability of the trial. J Am Mosq Control Assoc 14 (4) 431–6.
- 48. Mulla MS, Tharvara U, Tawatsin A, Kong-Ngamsuk A, Chompoorsi J (2001) Mosquito burden and impact on the poor: Measures and costs for personal protection in some communities in Thailand. J Am Mosq Control Assoc 17: 153–159.
- 49. Oxborough RM, Weir V, Irish S, Kaur H, N'Guessan R, et al. (2009) Is K-O Tab 1-2-3® long lasting on non-polyester mosquito nets? Acta Trop 112 (1) 49–53.
- 50. Bhatt RM, Yadav RS, Adak T, Babu CJ (2005) Persistence and wash-resistance of insecticidal efficacy of nettings treated with deltamethrin tablet formulation (K-O TAB) against malaria vectors. J Am Mosq Control Assoc 21 (1) 54–8.
- 51. Suwannachote N, Grieco JP, Achee NL, Suwonkerd W, Wongtong S, et al. (2009) Effects of Enviromental Conditions on the Movement Patterns of Aedes Aegypti (Diptera: Culicidae) Into and Out of Experimental Huts in Thailand. J Vector Ecol 34 (2) 267–275.
- 52. WHO [World Health Organization] (1998) Report of the WHO informal consultation. WHO/CDS/CPC/MAL/98.12. Geneva, Switzerland: World Health Organization.
- 53. Centers for Disease Control. Evaluating mosquitoes for insecticide resistance: a web based instruction Available: http://www.cdc.gov/ncidod/wbt/resistance/assay/bottle/index.htm.
- 54. Achee NL, Bangs MJ, Farlow R, Killeen G, Lindsay S, et al. (2012) Spatial repellents: from discovery and development to evidence-based validation. Malaria J 11: 164 .