The wMel strain of Wolbachia bacteria is known to prevent dengue and Zika virus transmission in the mosquito vector Aedes aegypti. Accordingly, the release of wMel-infected A. aegypti in endemic regions has been recommended by the World Health Organization as a potential strategy for controlling dengue and Zika outbreaks. However, the utility of this approach could be limited if high temperatures in the aquatic habitats where A. aegypti develop are detrimental to Wolbachia. We exposed wMel-infected A. aegypti eggs and larvae to fluctuating daily temperatures of 30–40°C for three, five, or seven days during their development. We found that Wolbachia levels in females emerging from heat treatments were significantly lower than in the controls that had developed at 20–30°C. Notably, seven days of high temperatures starting at the egg stage reduced Wolbachia levels in emerging females to less than 0.1% of the wMel control levels. However, after adult females returned to 20–30°C for 4–7 days, they experienced differing degrees of Wolbachia recovery. Our findings suggest that the spread of Wolbachia in wild A. aegypti populations and any consequent protection from dengue and Zika viruses might be limited in ecosystems that experience periods of extreme heat, but Wolbachia levels recover partially after temperatures return to normal.
The proposed arbovirus biocontrol strategy of releasing mosquitoes infected with the wMel strain of Wolbachia bacteria promises to reduce the transmission of dengue and Zika viruses, but its utility in the field may be limited by the local environment. We show that when Aedes aegypti infected with wMel experience high temperatures during egg and larval development, they have lower Wolbachia levels as emerging adults. High temperatures starting at the egg stage and lasting for seven days reduce Wolbachia levels in emerging females to less than 0.1% of control levels. However, partial recovery of Wolbachia occurs by 4–7 days of age. The spread of Wolbachia in wild A. aegypti populations and any resulting impacts on dengue and Zika transmission could be limited by periods of extreme heat, but Wolbachia levels may subsequently recover.
Citation: Ulrich JN, Beier JC, Devine GJ, Hugo LE (2016) Heat Sensitivity of wMel Wolbachia during Aedes aegypti Development. PLoS Negl Trop Dis 10(7): e0004873. https://doi.org/10.1371/journal.pntd.0004873
Editor: Pattamaporn Kittayapong, Mahidol University, THAILAND
Received: March 11, 2016; Accepted: July 2, 2016; Published: July 26, 2016
Copyright: © 2016 Ulrich 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: All relevant data are within the paper and its Supporting Information files.
Funding: This study was supported by the Leonard and Jayne Abess Center for Ecosystem Science and Policy at the University of Miami, Florida, the Australian Infectious Diseases Research Centre (http://www.aidrc.org.au/), and by the National Science Foundation Graduate Research Fellowship Program (https://www.nsfgrfp.org/) under Grant No. 2015178889. 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.
Mosquito-borne arboviruses are a growing public health threat. The alarming geographic spread and costly health burden of dengue fever have led the World Health Organization (WHO) to deem it “the most important mosquito-borne viral disease in the world.” Over the last 50 years, the incidence of dengue cases has increased 30-fold . Now more than 100 countries have endemic dengue and over 40% of the world's population is at risk . Zika virus, which recently caused a surge of children born with microcephaly and other neurological disorders, was declared a Public Health Emergency of International Concern (PHEIC) by the WHO after it spread from Brazil to 26 other countries or territories in the Americas within one year [3, 4]. With no effective antiviral treatments in the arsenal and just one licensed dengue vaccine that is 65.6% effective for those 9 years or older, control of the mosquito vectors, Aedes aegypti and Aedes albopictus, is the most viable option for curbing transmission of these arboviruses [5–7]. However, in resource-limited cities with endemic dengue, vector control efforts are often only pursued in response to explosive epidemics [8, 9]. Failure to control these vectors in tropical urban environments is one of the major drivers of the growing incidence and geographic expansion of dengue and other mosquito-borne arboviruses .
Alarmingly, existing control options for A. aegypti are of little use in urban areas [9, 11]. Space spraying with ultra-low volume insecticides, including organophosphates and pyrethroids, has been used by many countries in the face of dengue outbreaks for the past 40 years despite limited evidence of its epidemiological benefits [10, 12, 13]. Vector densities inevitably recover after space spraying because ideal larval habitats for A. aegypti abound in cities—exposed water sources for drinking or washing and non-biodegradable trash that collects water . Targeted spraying of potential larval development containers with residual insecticides [14, 15] and indoor residual spraying targeting adult mosquitoes  in combination can substantially reduce local dengue incidence, but only if high coverage is achieved [17, 18]. For countries faced with nearly ubiquitous breeding of A. aegypti in their sprawling cities, the comprehensive spraying required to stop transmission is unrealistic . Consequently, there is no urban setting in which vector control has completely eliminated dengue virus (DENV) transmission or prevented dengue epidemics [13, 20].
A potential solution for DENV and Zika virus (ZIKV) transmission involves releasing A. aegypti infected with Wolbachia, a common bacterium infecting the reproductive systems of many insects [21–24]. The fitness effects of Wolbachia on insect hosts are strain specific, ranging from life-shortening to pathogen-blocking phenotypes [25, 26]. The pathogen-blocking properties of some strains of Wolbachia have led researchers to characterize them further and transfer them into vector species for potential use in vector-borne disease control. The wMel strain of Wolbachia shows the most promise currently, as it blocks DENV and ZIKV transmission by the mosquito, raising the possibility of disrupting dengue and Zika transmission cycles [27–30]. The wMel strain was transinfected from Drosophila melanogaster into A. aegypti, and wMel-infected A. aegypti have been released at sites in Australia, Vietnam, Brazil, Indonesia, and Colombia . The success of each Wolbachia strain in invading insect populations is determined by the net fitness effect of the strain coupled with the extent to which it manipulates host reproduction . One key mechanism of reproductive manipulation is cytoplasmic incompatibility (CI). When a strain causes complete CI, Wolbachia-infected females can mate successfully with Wolbachia-infected males, while uninfected females cannot . The wMel Wolbachia strain causes complete CI and has had some success in invading wild A. aegypti populations [28, 33]. However, the prevalence of wMel Wolbachia must remain high in the A. aegypti population in order for wMel to reliably and substantially reduce the capacity of the mosquito population to transmit pathogens [32, 34]. Protection against DENV in field-collected wMel A. aegypti is similar to that observed in the original transinfected wMel line , indicating that this strategy might be used to reduce dengue transmission in endemic areas [28, 29, 36]. Recently the WHO recommended the use of Wolbachia for dengue and Zika control , although there is currently insufficient epidemiological evidence to know if the approach is effective. It is also unknown whether the prevalence of wMel-infected A. aegypti and the wMel Wolbachia levels within individual mosquitoes will remain high enough to prevent DENV and ZIKV transmission in all environments.
The levels of wMel Wolbachia load throughout the various stages of the A. aegypti lifespan have not been described, as most studies have focused on population dynamics and fitness effects of wMel Wolbachia after adult emergence [28, 33, 35, 37–40]. The early stages of development comprise a sensitive period during the A. aegypti lifespan; immature forms are confined to their aquatic habitats, whereas adults can seek out favorable microclimates to increase their chances of survival [41–43]. Immature A. aegypti develop in containers in the domestic environment that hold water, including flower pots, tanks, and drums as well as bottles, cans, and automobile tires [8, 44]. These containers sometimes hold as little as 5 mL of water . Female A. aegypti preferentially lay their eggs in shaded containers, but it is not uncommon to find immatures in containers fully exposed to the sun [46, 47]. Although comprehensive temperature measurements in sun-exposed containers have not been carried out, lab-reared A. aegypti larvae can tolerate aquatic temperatures as high as 43°C if they are pre-exposed to high but sublethal temperatures . The ability of wMel Wolbachia to tolerate the same elevated temperatures as immature A. aegypti has not been investigated.
The heat sensitivity of Wolbachia with respect to its hosts has been characterized in other arthropods. Exposure to high temperatures during development cured the Wolbachia infections of two-spotted spider mites Tetranychus urticae , Tribolium flour beetles , and Drosophila spp. [51–54]. In the mosquito Aedes scutellaris, the reproductive effect of CI caused by Wolbachia was lost when larvae were reared at 32.5°C, but it was unknown whether the loss of Wolbachia or host expression of heat-shock proteins was responsible [55–57]. In A. albopictus all life stages maintained at 37°C had a lower levels of Wolbachia than those reared at 25°C, indicating that high temperatures may reduce Wolbachia levels in mosquito hosts .
Reduced Wolbachia levels in response to high temperatures during larval development could represent a barrier to the spread of wMel Wolbachia in A. aegypti populations if fundamental drive mechanisms such as maternal transmission and CI are affected. Because only Wolbachia-infected females produce viable offspring with Wolbachia-infected males, CI creates a selective pressure for the spread of Wolbachia . The spread of Wolbachia in mosquito populations is crucial, because incomplete wMel Wolbachia coverage in the A. aegypti population leaves the potential for DENV and ZIKV transmission. A recent study found geographical clusters of uninfected mosquitoes in a wMel-infected A. aegypti release suburb of Cairns, Far North Queensland, Australia . The incomplete Wolbachia coverage was suggested to be due to immigration of uninfected mosquitoes from outside the release area, cryptic breeding sites, or other environmental phenomena such as “larval curing” (loss of Wolbachia infection during larval development) . However, the occurrence of larval curing in mosquitoes has been poorly defined to date. Specifically, little is known about the temperature thresholds for Wolbachia during mosquito development or whether any potential curing persists after temperatures return to normal. Understanding larval curing in wMel-infected A. aegypti has important applications, as lower Wolbachia levels in adults might have downstream impacts on cytoplasmic incompatibility [60–67] (although in D. simulans between-strain differences in CI are not explained by Wolbachia density ), maternal transmission [69, 70], and pathogen inhibition [29, 68, 71–73].
We investigated the effects of high temperatures during egg and larval development on laboratory-reared wMel-infected A. aegypti using fluctuating daily temperatures that simulate the real-world conditions of a heatwave in Cairns, Australia. Our results have implications for the projected spread of wMel Wolbachia through A. aegypti populations and for the vector competence of wMel-infected A. aegypti under different environmental conditions.
Blood feeding of mosquito colonies using human volunteers was performed in accordance to the QIMR Berghofer Human Research Ethics Committee permit QIMR HREC361. Written informed consent was obtained from all volunteers who participated in the study.
Mosquitoes were taken from a Wolbachia-free A. aegypti colony (“Cairns” line) started from eggs collected in Cairns, Australia, in January 2015 and from a colony of wMel-infected A. aegypti (“wMel” line) started from eggs collected in suburbs of Cairns in April 2015. The colonies were maintained in separate, identical climate-controlled rooms at 27 ± 1°C and 70 ± 10% relative humidity with a 12:12 hour light:dark cycle and crepuscular periods. Eggs were flooded in aged (≥ 48 h) tap water and allowed to hatch naturally. Larval stages were reared under a controlled density (< 200 larvae per tray) in trays with 3 L of aged tap water. Larvae were fed on ground TetraMin tropical fish food (Tetra, Germany). Pupae were transferred into cages measuring 40 × 40 × 30 cm for adult emergence. Colonies were maintained with a population size of > 500 individuals per generation. Adult mosquitoes received 10% sucrose solution ad libitum, and females were blood-fed on a human volunteer for 15 min every 7 d. The wMel-infected A. aegypti colony was regularly screened for Wolbachia using PCR of the wsp gene from the time of establishment . Prior to the start of the experiments, our screening showed that the colony was completely infected with Wolbachia.
For the experiments, eggs were collected from A. aegypti wMel (F16 and F17 generations used) and A. aegypti Cairns (F18 and F19 generations) colonies at 8:30 A.M. following the first night of oviposition. Eggs were counted under a stereomicroscope at 23°C and were separated into batches of approximately 600 eggs. Each batch was placed inside a dry paper towel, which was folded and placed next to a damp paper towel inside an open plastic bag. Egg bags were placed inside their corresponding environmental chambers at the coldest point of the temperature cycles, which was 20°C for the control condition and 30°C for the treatment condition. Eggs were left to mature for 48 h, and then batches of approximately 150 eggs were flooded in 500 mL aged tap water in plastic trays (183 × 152 × 65 mm). Four replicate trays were used per treatment group. From the day of hatching until pupation, ground TetraMin tropical fish food (Tetra, Germany) was administered daily at the coldest point of the temperature cycles using the “medium” diet described by Hugo et al. . Pupae were transferred into 1-L plastic containers with mesh tops, and emerging adults were given 10% sucrose solution ad libitum. Adult females were aspirated out at 0–2 days post-emergence and at 4–7 days post-emergence. They were frozen at -20°C until processing.
We tested the effect of high temperatures during egg and larval development on Wolbachia levels in A. aegypti wMel adult females in two replicate experiments: Each replicate experiment compared various heatwave temperature regimes applied during particular periods of immature mosquito development that varied in duration and stage of onset. The temperature profiles we used simulated observed temperatures during average and extreme conditions in Cairns, Queensland. The Australian Bureau of Meteorology defines a heatwave as “a period of at least three days where the combined effect of excess heat and heat stress is unusual with respect to the local climate” . We designed our treatment temperature profile to surpass the severe daily mean temperature threshold of 30.4°C for Cairns, which is based on temperature data from 1958 to 2011 . Both treatment and control temperature profiles followed a truncated sinusoidal progression during the day and exponential decrease at night, representing a profile of daily temperature variation . The shapes of the profiles were the same for each condition, but the profile was raised or lowered to adjust the mean temperature (S1 Fig). Experiments were conducted in two environmental chambers (294-L Panasonic MLR-352H-PE and MLR-351H, Gunma, Japan). Nine treatment groups were exposed to fluctuating heatwave temperatures between 30°C and 40°C for varying durations beginning at various life stages. Controls consisted of wMel A. aegypti and wildtype Cairns A. aegypti exposed to diurnal temperature fluctuations between 20°C and 30°C. Transfers between environmental chambers were made at the coldest point of the temperature cycles (20°C for the control condition and 30°C for the treatment condition) in order to minimize the likelihood of heat shock. As illustrated in Fig 1, treatment groups exposed to high temperatures beginning from early embryogenesis (eggs at ≤ 15 hours post-oviposition) lasting three, five, or seven days are denoted by “E3,” “E5,” and “E7.” Groups exposed to high temperatures beginning at the immature larval stages (1st/2nd instars) lasting three, five, or seven days are denoted by “I3,” “I5,” and “I7.” Groups exposed to high temperatures beginning at more mature larval stages (3rd/4th instars) lasting three, five, or seven days are denoted by “M3,” “M5,” and “M7.” Prior to the two studies, a pilot study was conducted to determine differences in means for a range of onsets and durations (S2 Fig).
All treatment groups (rows) were transferred to environmental chambers as eggs within 15 hours of being laid, and all developed into adults by the end of the experiment. “wMel” denotes the wMel-infected A. aegypti controls, and “Cairns” denotes the wildtype (Wolbachia-free) A. aegypti controls. For each of the other treatment groups, the letter represents the stage of heat onset, with “E” indicating embryogenesis, “I” indicating immature larvae (1st/2nd instars), and “M” indicating more mature larvae (3rd/4th instars). The number represents the number of days the group remained in the high temperature treatment before returning to control temperatures (three days, five days, or seven days). Moving across each row, the cells track the days for each treatment group, with blue cells representing days spent in the control chamber and red cells representing days in the high temperatures chamber. Inverted triangles represent adult collection time points at 0–2 days and 4–7 days after emergence.
Data loggers, both factory installed and independent HOBO data loggers (Onset, Cape Cod, MA), recorded light intensity and temperature variation. Actual water temperatures in the control chamber were within 1.00°C of the programmed air temperature throughout the duration of the experiments. This was also the case in the treatment chamber, except during the coldest periods, when water temperature was as much as 2.93°C lower than the programmed air temperature.
Wolbachia density in adult females
Wolbachia densities within individual adult females were determined by quantitative PCR. The head was removed from each frozen adult female before DNA extraction. Genomic DNA was extracted using QuickExtract DNA Extraction Solution (Epicentre Technologies Corporation) as per the manufacturer’s instructions and was diluted 1:10 in purified water. Multiplex qPCR was performed, amplifying the target Wolbachia-specific wsp gene and the somatic Actin5c gene, which acted as a reference gene to standardize for mosquito body size (wsp F: 5´–CATTGGTGTTGGTGTTGGTG–3´, R: 5´–ACACCAGCTTTTACTTGACCAG–3´, Actin5c F: 5´–GACGAAGAAGTTGCTGCTCTGGTTG–3´, R: 5´–TGAGGATACCACGCTTGCTCTGC–3´) (full methods in S1 Appendix) [73, 78, 79]. Quantification cycles (Cq) were normalized by taking into consideration the different amplification efficiencies of the wsp and Actin5c genes, and Wolbachia to host genome ratios were calculated using Q-Gene .
Wolbachia visualization in mosquito ovaries
Fluorescence in situ hybridization (FISH) was carried out using a Wolbachia-specific 16S rRNA probe . Three freshly collected adult females (legs and wings removed) from each treatment group were fixed in 4% paraformaldehyde in 0.1 M phosphate buffer overnight and were transferred to 70% ethanol. Bodies were embedded in paraffin wax and sectioned with a microtome. Slides were dewaxed with two successive xylene washes for 10 min, two successive 5-min washes with 100% ethanol, and two successive 5-min washes in 95% ethanol. Slides were hybridized with the Wolbachia-specific W2 probe (5´–CTTCTGTGAGTACCGTCATTATC–3´)  conjugated on the 5´ end to the fluorescent probe Alexa Fluor 488 (Molecular Probes, Inc). Slides were left in a dark humidity chamber at 37°C overnight and washed briefly in 1× saline sodium citrate (SSC) buffer + 10 mM dithiothreitol (DTT) at room temperature, then two 15-min washes in 1× SSC + 10 mM DTT at 55°C, two 15-min washes in 0.5× SSC at 55°C, a 10-min wash in 0.5× SSC + 10 mM DTT + 4',6-Diamidino-2-phenylindole (DAPI) (0.01 mg/50 mL) at room temperature, and then a final 10-min wash in 0.5× SSC + 10mM DTT at room temperature. Slides were washed briefly with distilled water and mounted with Vectashield Hard Set mounting medium (Vector Laboratories, Burlingame, CA). Slides were allowed to dry in a refrigerator overnight. Images from all sections were captured with a DeltaVision Core Deconvolution Microscope (GE) using identical acquisition settings (S2 Appendix). Images were reformatted using SoftWorx (Enterprise Softworks (Pty) Ltd.) and were cropped and standardized for contrast using Adobe Photoshop CS6 (Adobe Systems, Inc.).
To determine the effect of the heat treatments on adult body size, the left wing of six females from each treatment group was removed and dry mounted on a slide. The distance from the axial notch to the wing tip, excluding the fringe scales, was used as a proxy for body size [75, 81].
All analyses were performed in R  and GraphPad Prism v. 6 (GraphPad Software, San Diego, California, USA). Normality and homogeneity of variances within treatments were tested using Shapiro-Wilk and Bartlett’s tests, respectively. Log10-transformed Wolbachia densities were used for all analyses. A two-way blocked analysis of variance (ANOVA) was performed to determine the effects of treatment and collection time point and their interaction on Wolbachia density. Replicate was included as a blocking factor to account for any variation between the two experiments. An analogous two-way blocked ANOVA was performed to determine the effects of treatment group and collection time point and their interaction on body size. Pair-wise post-hoc comparisons between treatments and controls and between collection time points were made for both ANOVAs, and P values were adjusted for multiple comparisons using Tukey’s honest significant difference test. Differences were considered significant if adjusted P values were < 0.05. A nonlinear regression was performed using ordinary least squares fit for each stage of onset at the two collection time points to determine relationships between the heat treatment duration and Wolbachia density. Sum of squares F-tests were used to determine significant differences in slopes and y-intercepts.
Wolbachia density in adult females
We found significantly lower Wolbachia densities relative to wMel controls in 0–2 d-old females emerging from eight of the nine treatments (Fig 2), with only the mature instar treatment lasting three days (M3) showing no significant reduction. Wolbachia levels in the 0–2 d-old females that were exposed to 30–40°C for seven days starting at the egg stage (E7) were less than 0.1% of wMel control densities (Fig 2). Both treatment group and collection time point were significant predictors of Wolbachia density (F(10, 362) = 197.34, MSE = 55.24, P < 0.001 and F(1, 362) = 397.21, MSE = 111.20, P < 0.001, respectively). Compared with the 0–2 d adult collection time point, 4–7 d-old adult females in all treatment groups except the wMel control group and the M3 group had higher Wolbachia levels, with adults from three-day treatments (E3, I3, and M3) showing Wolbachia densities that were not significantly different from wMel-infected controls (Fig 2). The Wolbachia levels in 4–7 d-old adults from the six other treatments remained significantly lower than in wMel-infected controls. There were inverse relationships between the duration of heat treatment and Wolbachia density and for all stages of onset; however, the relationships differed significantly both in their slopes and y-intercepts (F(5, 305) = 3.68, P = 0.003 and F(5, 305) = 2.79, P = 0.02, respectively). Duration of heat exposure had the greatest impact on Wolbachia density in emerging females when high temperatures began in the 3rd/4th instar stages. At 4–7 days of age the impact of heat duration on density was most pronounced when high temperatures began at the egg stage.
Wolbachia densities in 0–2 d-old (circles) and 4–7 d-old (inverted triangles) female wMel A. aegypti exposed to various temperature treatments. “wMel” denotes the wMel-infected A. aegypti controls that were not exposed to high temperatures, and for the other treatment groups the letter represents the stage of heat onset—“E” for embryogenesis, “I” for 1st/2nd instars, and “M” for 3rd/4th instars—and the number represents the number of days the group remained in the high temperature treatment. Wolbachia density was measured by qPCR of the Wolbachia-specific wsp gene and the somatic insect gene Actin5c. Displayed values are relative concentrations of wsp and Actin5c calculated in Q-Gene. The horizontal line at y = 10−3.552 represents the detection limit of Wolbachia by qPCR, which was established by the average Cq values for Wolbachia-free Cairns A. aegypti controls. Bars denote means bounded by their 95% confidence intervals. The lower 95% confidence limit for the 0–2 d-old I5 group (y = −0.009) is not shown because it cannot be represented on the log scale. The significance levels of differences between time points are indicated above brackets and between treatment groups and the wMel controls at the top of the graph as P < 0.05 (*), P < 0.01 (**), P < 0.001 (***). Each point represents an individual mosquito.
Wolbachia visualization in mosquito ovaries
We also investigated whether we could visualize reductions in Wolbachia levels in the ovaries of adult mosquitoes after exposure to high temperatures during development. Using FISH we visualized very low levels of Wolbachia in the ovaries of 0–2 d-old E7 females (Fig 3B). We also noticed that the E7 ovaries were much less developed than in controls, a possible consequence of the heat exposure. In 4–7 d-old E7 females (Fig 3D), Wolbachia remained at very low levels compared with 4–7 d-old wMel-infected controls (Fig 3C).
Ovaries of A. aegypti wMel females emerging from the control (A,C) and E7 (B,D) treatment groups, collected at 0–2 d (A, B) and 4–7 d (C, D) after emergence are shown. Wolbachia were stained with Alexa Fluor 488 (green) and cell nuclei with DAPI (blue).
We found a significant effect of treatment group on wing length (F(10,71) = 13.70, MSE = 0.32, P < 0.001) and of the treatment group–collection time point interaction (F(9,71) = 2.81, MSE = 0.07, P = 0.007). Collection time point and replicate were not significant predictors (F(1, 71) = 0.22, MSE = 0.005, P = 0.64 and F(1, 71) = 1.21, MSE = 0.03, P = 0.27, respectively). Treatment groups E7, I5, I7, M3, M5, and M7 were all significantly smaller than wMel controls (S3 Fig). There was no significant difference in wing length between wMel controls and Cairns controls.
We found that when A. aegypti infected with the wMel strain of Wolbachia were exposed to daily fluctuating temperatures of 30–40°C during early development, the emerging females had reduced Wolbachia levels compared with controls. The most affected group consisted of mosquitoes exposed to high temperatures starting at the egg stage and lasting for seven days (E7). In E7 emerging females, mean Wolbachia levels were less than 0.1% of the levels of wMel controls. Loss of Wolbachia density from a subset of the mosquito population may be a concern for Wolbachia-based dengue and Zika control efforts in regions where the aquatic habitats of juvenile A. aegypti can reach extremely high temperatures. It has previously been shown that different Wolbachia strains attain different infection densities and that density is correlated with the level of virus inhibition [68, 71, 73, 78]. The relationship between wMel density and DENV and ZIKV inhibition can be assumed from near complete blockage of these viruses in Ae. aegypti harboring dense wMel infections [28, 30, 35], but the relationship has not been specifically defined. A recent study found that exposure of adult wMel-infected A. aegypti to 28°C ± 4°C beginning at 5–8 d of adult age was associated with reduced Wolbachia densities; however, there was no interaction between the reduced densities and DENV infection, dissemination, or transmission . Eggs and larvae exposed to high temperatures in our study produced adult A. aegypti with very low Wolbachia densities; therefore, the level of pathogen inhibition in adult mosquitoes that were subject to impacts of heat exposure during early development deserves investigation. The partial recovery of Wolbachia density by 4–7 days of age suggests that any impacts of heat exposure during mosquito development on subsequent virus inhibition may be attenuated with age.
This study is the first to investigate the duration and timing of heatwave conditions in relation to immature development of mosquitoes infected with Wolbachia. To achieve this we simulated normal and heatwave conditions based on temperature data from a city selected for Wolbachia biocontrol. We found an inverse relationship between the duration of heat exposure and Wolbachia density in adult females, raising the possibility that longer periods of heat might be capable of clearing Wolbachia. The slope of this relationship varied by the stage of heat onset and by the age of adult females collected. Duration of heat exposure had the greatest impact on Wolbachia density in emerging females when high temperatures began in the 3rd/4th instar stages; however, the impact of heat duration on density at 4–7 days of age was most pronounced when high temperatures began at the egg stage. In addition to reducing bacterial densities, high temperatures resulted in smaller adult body sizes, with more prominent effects in the later stages of heat onset and the longer durations. This is likely due to the known inverse relationship between larval rearing temperature and adult body size . We controlled for the effect of body size by standardizing Wolbachia density measurements with the host gene Actin5c.
Loss of Wolbachia density in response to heat has also been reported in T. urticae  O. scapulalis , D. simulans , D. bifasciata , A. albopictus , the predatory mite Metaseiulus occidentalis , and the wasp Leptopilina heterotoma . The mechanism behind the loss of Wolbachia in response to high temperatures is not fully understood, but deformation of the Wolbachia cellular membrane could be a contributing factor . Our FISH visualization confirms the loss of Wolbachia from the ovaries of mosquitoes exposed to high temperatures. Partial recovery of Wolbachia in the ovaries after the mosquito returns to normal temperatures suggests that Wolbachia replication continues even after the ovaries are fully developed. It is uncertain whether replication continues throughout the female lifespan and at what age Wolbachia densities would be restored to control levels in heat-exposed females.
Our results support the notion that wMel has a more restricted thermotolerance than its mosquito host A. aegypti. Loss of thermotolerance in insect symbionts can be due to point mutations that occur as the symbiont co-evolves with the host . In the case of the obligate symbiont of aphids Buchnera aphidicola, a point mutation affecting heat-shock protein transcription leads to death of the symbiont following a heat treatment . Compared with other symbionts of insects, wMel has experienced far less reductive evolution, as evidenced by its large genome with very high levels of repetitive DNA and mobile DNA elements . Because of the low mutation rate of wMel , loss of thermotolerance is less likely than for other symbionts . If reductive evolution of wMel does occur, then rearing wMel-infected A. aegypti under constant temperatures in the lab might accelerate loss of wMel thermotolerance. More studies are needed to understand the co-evolution of wMel and A. aegypti.
Wolbachia may hold the potential to reduce and even eliminate dengue and Zika transmission in endemic areas. The advent of a promising control tool for dengue fever and Zika could not have come at a better time, as currently many tropical countries have no options to control the massive arbovirus outbreaks they experience. The strategy of releasing wMel-infected A. aegypti is being tested in dengue-endemic regions around the globe, including Australia, Vietnam, Brazil, Indonesia, and Colombia , although substantial epidemiological data is still needed to assess the impacts on dengue and Zika transmission. The importance of measuring Wolbachia density in field trials, as opposed to presence or absence of Wolbachia, is highlighted by our results and other investigations [61, 64, 78]. We found that the high temperatures that A. aegypti may experience during early development can attenuate wMel Wolbachia levels. Consequently, wMel Wolbachia might be less effective as a dengue or Zika control strategy in regions experiencing periods of extreme heat. If the effectiveness is compromised, increased surveillance and supplementary mosquito control may be required in these regions. Further estimates of Wolbachia recovery rates after heat exposure are needed to understand the impacts on DENV and ZIKV inhibition and the spread of wMel through naïve A. aegypti populations.
In summary, we showed that fluctuating daily temperatures of 30–40°C experienced during wMel-infected A. aegypti egg and larval development significantly reduced Wolbachia levels in emerging adult females. However, Wolbachia recovered to differing degrees after adults returned to 20–30°C. These findings suggest that the effectiveness of Wolbachia-based arbovirus control might be compromised in ecosystems that experience periods of extreme heat, but given that Wolbachia levels partially recover after temperatures return to normal, any effects may be temporary. Greater understanding of environmental variables that affect Wolbachia can inform release site selection and help to better predict the impacts of Wolbachia on arbovirus transmission.
S1 Fig. Water temperature fluctuations in environmental chambers.
Control and treatment chambers are shown in blue and red, respectively. Data loggers were submerged in 500 mL aged tap water in trays (183 × 152 × 65 mm) and temperature was recorded every 30 min for the duration of both experiments. Bars denote means and standard errors over days logged.
S2 Fig. Pilot study results.
Log10-transformed relative Wolbachia densities in 0–2 d-old female A. aegypti in different treatment groups. Treatments not included in subsequent experiments include the pupae onset stage (P1, P3) and the one-day duration (I1, M1, P1). Wolbachia density was measured by qPCR of the Wolbachia-specific wsp gene and the somatic insect gene Actin5c. Displayed values are relative concentrations of wsp and Actin5c calculated in Q-Gene. Bars denote means bounded by their 95% confidence intervals. Significant differences between treatment groups and the wMel controls are displayed as P < 0.05 (*), P < 0.01 (**), P < 0.001 (***). Each point represents an individual mosquito.
S3 Fig. Wing length by treatment group.
Significant differences between treatment groups and wMel controls are indicated by asterisks, P <0.05 (*), P <0.01 (**), P <0.001 (***). Bars denote means bounded by their 95% confidence intervals. Each point represents an individual mosquito.
S1 Appendix. qPCR conditions.
The Actin5c gene was used to normalize wsp gene copies. qPCR reactions were performed in 10 μl total volume containing 5.0 μl Platinum SYBR Green qPCR SuperMix-UDG (Invitrogen), 1 μM of each primer, and 2 μL of DNA template. Cycling was performed using a RotorGene 6000 system (Corbett Research) with the following program: 95°C for 2 min, 50°C for 2 min, and 50 cyclic repeats of 95°C for 10 s, 52°C for 10 s, and 72°C for 20 s. This was followed by a standard melt analysis to confirm that only the expected product had been amplified. Quantification cycles (Cq) values were calculated using the Comparative Quantification algorithm in the RotorGene 6000 software (Corbett Research). Repeat reactions were performed with samples for which the duplicate Cq values differed by more than 0.75.
S2 Appendix. Microscopy methods.
Images were captured with GE DeltaVision Core Deconvolution Microscope (GE) equipped with an Olympus X181 inverted microscope using an Olympus 20X/0.75 U Apo 340 lens or an Olympus 10X/0.40 D Plan Apo UV lens and a Photometrics Cool Snap HQ CCD camera. Images were acquired at a resolution of 1024 x 1024. DAPI excitation was 390/18nm and emission collection was 435/48 nm with 0.2 s exposure (5% ND filter). AlexaFluor 488 excitation was 475/28 nm and emission was 523/36 nm with a 0.15 s exposure (32% ND filter).
S1 Dataset. Wolbachia density data from first replicate.
S2 Dataset. Wolbachia density data from second replicate.
We thank Jonathan Darbro and Elise Kho of the Mosquito Control Laboratory, QIMR Berghofer Medical Research Institute, for assisting with the establishment of wMel-infected and wild type A. aegypti colonies at QIMR Berghofer Medical Research Institute. We also thank Leesa Wockner from the QIMR Berghofer Medical Research Institute/Metro North Hospital and Health Service Statistics Unit for statistical advice. In addition, we thank Clay Winterford from the QIMR Berghofer Medical Research Institute Histotechnology Facility for histology advice and Nigel Waterhouse and Tam Nguyen at the ACRF Centre for Biomedical Imaging at QIMR Berghofer Medical Research Institute for assistance with imaging.
Conceived and designed the experiments: JNU LEH. Performed the experiments: JNU. Analyzed the data: JNU. Contributed reagents/materials/analysis tools: LEH GJD. Wrote the paper: JNU JCB GJD LEH.
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