Differences in timing of mating swarms in sympatric populations of Anopheles coluzzii and Anopheles gambiae s.s. (formerly An. gambiae M and S molecular forms) in Burkina Faso, West Africa
© Sawadogo et al.; licensee BioMed Central Ltd. 2013
Received: 20 October 2012
Accepted: 13 September 2013
Published: 22 September 2013
The M and S molecular forms of Anopheles gambiae s.s. Giles appear to have speciated in West Africa and the M form is now formally named An. coluzzii Coetzee & Wilkerson sp.n. and the S form retains the nominotypical name (abbreviated here to An. gambiae). Reproductive isolation is thought to be the main barrier to hybridisation; even though both species are found in the same mating swarms, hybrid fertilisations in copulae have not been found in the study area. The aim of the study, therefore, was to determine whether differences in circadian and/or environmental control over the timing of swarming in the two species contribute to reproductive isolation.
The timing of male swarming in these species was recorded four nights per month over four years at five swarming sites in each of two villages. The timing of the start and end of swarming, and the concurrent environmental parameters, temperature, humidity and light intensity, were recorded for n = 20 swarms/month/species. The timing of 'spontaneous’ activity at dusk of individual An. coluzzii and An. gambiae males was video-recorded in an actograph outdoors for 21 nights.
Of the environmental parameters considered, swarming was most strongly correlated with sunset (r2 > 0.946). Anopheles gambiae started and stopped swarming earlier than An. coluzzii (3:35 ± 0:68 min:sec and 4:51 ± 1:21, respectively), and the mean duration of swarming was 23:37 ± 0:33 for An. gambiae and 21:39 ± 0:33 for An. coluzzii. Accordingly, in principle, whenever both species swarm over the same marker, a mean of 15.3 ± 3.1% of An. gambiae swarming would occur before An. coluzzii males arrived, and 19.5 ± 4.55% of An. coluzzii swarming would occurred after An. gambiae males had stopped swarming. These results are consistent with the finding that An. gambiae males became active in the actograph 09:35 ± 00:22 min:sec earlier than An. coluzzii males.
The timing of swarming and spontaneous activity at dusk are primarily under circadian control, with the phase linked closely to sunset throughout the year. The mating activity of these two species is temporally segregated for 15-20% of the swarming period, which may contribute to the observed reproductive isolation of these species in local sympatric populations.
Despite concerted international efforts to reduce malaria worldwide, in sub-Saharan Africa alone there were > 600,000 deaths in 2010 attributed to this deadly disease, and more than half the world’s population is still at risk of malaria infection. In the absence of an effective vaccine, long-lasting insecticide-treated nets (LLINs) and indoor residual spraying (IRS) are the most common methods used to control malaria. However, the success of malaria vector control programmes is threatened by the emergence and spread of insecticide resistance to all major classes of insecticides, including pyrethroids, and to a lesser degree carbamates and organophosphates[3–7]. Alternative novel vector control strategies, such as those based on genetically modified mosquitoes (GMO) or the release of sterile males[8–12], are being investigated to explore their usefulness for sustainable long-term malaria control. The application of current control strategies and the prospects of using innovative control tools, however, crucially depend on accurate knowledge of the bionomics of the vectors, with particular reference to their reproductive biology, population structure and circulation of genes of interest in natural field populations.
The major afro-tropical malaria vector Anopheles gambiae s.s. Giles represents a challenging model in this context, because its composite population structure is complicated by the emergence of independent reproductive units marking a process of incipient speciation. Two such units, originally referred to as 'M’ and 'S’ molecular forms and now formally recognised as An. coluzzii Coetzee & Wilkerson and An. gambiae s.s. Giles (hereafter An. gambiae) based on population genomic evidence, appear to be following independent evolutionary trajectories, diverging at the genetic and ecological levels despite ongoing, albeit limited, gene flow. Across most of West Africa, the frequencies of hybrids of the two species are < 1%. Current hypotheses point to a process of ecological speciation, whereby a combination of divergent ecological and behavioural characteristics have contributed to reduced gene flow and nearly complete reproductive isolation.
The exact nature of the reproductive barrier between An. coluzzii and An. gambiae, which is substantiated, with a few exceptions[16–19], by the rarity of hybrids in natural field populations, is not fully established. There is evidence that pre-mating isolation must play a significant role; in a zone of sympatry in Mali, only 3 out of 250 (1.2%) wild caught An. coluzzii and An. gambiae females were found to contain the sperm of the 'other’ species, and in Burkina Faso no hybrid fertilisations have been found in copulae caught in mixed-species swarms (i.e., swarms consisting of both An. coluzzii and An. gambiae males). Although the occasional mixed-species copulae have been caught, in all cases the females contained sperm only of the female’s species.
It is generally agreed that swarming in mosquitoes at species-specific sites and times of day facilitates mating[22–27] and that males and virgin females are attracted to swarm sites by visual features in the landscape. Upon reaching a swarm site, each mosquito maintains a looping flight pattern, station-keeping in relation to a visual 'marker’, until a potential mate is detected, whereupon a mating chase ensues[22, 28, 29]. Mosquito swarms differ from other types of swarms (e.g., of bees or termites) in that swarm cohesion depends primarily on individuals responding in the same way to stationary markers, and to a lesser extent on interactions between individuals. Hence, a single mosquito can be said to 'swarm’, since it will continue to hold station with respect to the marker in the absence of other mosquitoes. Although the daily timing of swarm formation and site choice tends to be associated with particular species, different species may swarm in the same area, although they generally form separate swarms at varying distances from the marker.
Anopheles gambiae has been shown in the laboratory to mate within the first hour of darkness, during a peak in flight activity, and when males are most responsive to the flight tones of females. Field studies of An. gambiae swarming have focused primarily on flight patterns and on the close association between swarming and mating[32–35].
Recent studies on swarming and mating behaviour in An. gambiae s.l. in Mali and Burkina Faso have targeted differences in the behaviour of An. coluzzii and An. gambiae that appear to have contributed to a premating barrier to hybridisation in some locations[21, 34, 36–39]. Studies in Mali have shown that the lack of hybridisation between An. coluzzii and An. gambiae could be explained, in part at least, by form-specific differences in choice of swarming sites, i.e., spatial segregation of mating sites[38, 39]. In a previous study conducted at the same sites in Burkina Faso as the study described here, out of 90 swarms monitored over 2 years, 60% were single-species swarms of necessity, as the species were segregated either spatially or seasonally (i.e., did not occur in the same villages during the same months), 23% were single species swarms even though both species were present in the village and only 17% were 'mixed-species’ swarms. Of the 33 females caught in copulae collected from these mixed-species swarms, all were found to be inseminated by males of their own species, suggesting that there are as yet unidentified mechanisms preventing hybrid matings within mixed-species swarms. One of these mechanisms could be slight differences in the start and/or end times of swarming on a given day, i.e., daily, as opposed to seasonal, temporal mating segregation. In the previous study, swarms were sampled during the daily peak time of swarming, a sampling regime that would not have detected differences between species in the timing of their swarming.
The studies referred to above[21, 38, 39] focused on factors that affect where swarming takes place. The factors that could affect when swarming occurs, however, remain poorly investigated, and, therefore, are the main focus of the study presented here.
Generally, the timing of mosquito behaviour is mediated by circadian rhythms of activity that are controlled by endogenous factors, and to a lesser degree in response to environmental cues, such as changes in temperature, humidity and light intensity[27, 40]. Male and virgin female An. gambiae have been shown to express similar patterns of daily 'spontaneous’ activity (i.e., flight in the absence of environmental stimuli), with a major peak during the first hour after 'lights off’ in the laboratory (i.e., at sunset) and a smaller peak at 'lights on’ (sunrise), that coincide with the observed timing of swarms in the field[27, 41].
Little is known, however, about the relative timing of swarming behaviour in An. coluzzii and An. gambiae in the field. Therefore, to test the hypothesis that An. coluzzii males start and/or end swarming at different times to An. gambiae males, we recorded the timing of swarming activity of each species at natural swarm sites and the timing of spontaneous activity levels of individual An. coluzzii and An. gambiae males at dusk in an actograph; in both cases the mosquitoes were under the influence of both their endogenous circadian rhythms of spontaneous activity and natural changes in potential environmental cues. We recorded the timing of the start and end of swarming activity at dusk, the concurrent environmental parameters that might affect the timing of swarming in the field (temperature, humidity, light intensity and the time of sunset) to assess the relative importance of endogenous and environmental factors in the control of the timing of swarming in An. coluzzii and An. gambiae.
We also recorded the timing of spontaneous activity at dusk, which would normally initiate the egress of mosquitoes from their day-time resting sites, thereby exposing them to environmental cues related to a range of behaviours, e.g., visual and possibly auditory and olfactory cues that guide them to swarming sites and/or sources of nectar. Small differences in the timing of activation could have a profound effect on the chances of males and virgin females of the two species encountering each other during the short window of time each day when mating occurs.
Vallée de Kou (11°24’29”N; 04°24’37”W) consists of a cluster of villages ~30 km north-west of Bobo-Dioulasso, in the valley of the Kou River, a region of extensive rice cultivation that was established during the 1970s. Seven villages covering 7,200 ha were created as part of an irrigation development scheme. Each village lies at the edge of rice fields and is surrounded otherwise by wooded savannah. Since the Kou River flows all year, it offers a permanent source of water for irrigation, enabling the growth of two crops of rice per year (July-November and January-May), and as a result the rice fields are highly productive permanent mosquito breeding sites. More typical anopheline breeding sites (rain puddles and rain or ground-water filled depressions, such as tyre tracks) are also present. Both An. coluzzii and An. gambiae have been recorded at high densities during the rainy season (May-October), with typical biting rates for An. coluzzii of ~ 200 bites person–1 night–1. Since 2003 various attributes of An. coluzzii and An. gambiae mating swarms have been monitored in the village known as 'VK7’ and a range of associated environmental and ecological parameters have been recorded, as described by.
Soumousso (11°00’46”N, 4°02’45”W) is a typical Guinean savannah village situated ~ 55 km east of Bobo-Dioulasso. The main anopheline breeding sites are rain puddles and a semi-permanent swamp. Three main malaria vectors are found in this village An. coluzzii, An. gambiae, An. funestus Giles and An. nili (Theobold). Anopheles arabiensis Patton, another member of the An. gambiae s.l. species complex, is occasionally reported at low frequencies (<5% of An. gambiae s.l. samples). Since 2003 the swarming behaviour of An. coluzzii and An. gambiae have been studied in this village[21, 37].
Monitoring the timing of An. coluzzii and An. gambiae swarming
Since 2005 male swarms in the two study villages have been monitored with the aim of characterising swarming sites and monitoring the identity of males collected from each swarm. The main findings of the earliest surveys (2005- early 2006) were that An. coluzzii swarms predominate in Vallée de Kou, whereas An. gambiae swarms predominate in Soumousso, and specific swarm sites were identified where only An. coluzzii or An. gambiae swarms occurred. On the basis of these data, for the present study five swarm sites were chosen in each village that were most likely to have single-form swarms of An. coluzzii in Vallée de Kou and An. gambiae in Soumousso.
Trained IRSS/Centre Muraz field teams (> 5 years experience) monitored the five selected swarm sites in each village on four consecutive days each month for a year from January to December 2007, and each month from August to October 2006, and June-Oct in 2008 and 2009, with no exceptions due to weather or any other factors. Swarm observations were made from 17:00 to 20:00. The number of swarms monitored each month was: two species × five swarms/species × four observations of each swarm/month = 40 swarms observed/month × 25 months, i.e., a total of 1,000 swarms.
The start of swarming was defined as the time the first male was seen flying in characteristic swarming flight at the specified swarm sites. It was observed that, after the first male arrived, there was a rapid accumulation of males in swarms, which eventually consisted of tens to thousands of males, depending mainly on seasonal variation in population densities. The total number of males was not static; individual males appeared to leave and join the swarm throughout the swarming period. Toward the end of this period, the number of males appeared to decrease as quickly as they had accumulated. By the end of the swarming period it was too dark to see every mosquito clearly with the naked eye. Therefore, to be sure the end of swarming was recorded accurately, as determined by the departure of the last mosquito, a camera flashbulb was lit ~ once per minute near the expected end of swarming; single mosquitoes are clearly visible in the brief but high intensity light of the flash, which is too brief to disturb swarming behaviour. The only exception to the observation regime described in the previous paragraph is that the end of swarming was not recorded in 2009.
Ideally, the time at which each mosquito entered and left the swarm should have been recorded, along with its molecular form identity and the total numbers of males swarming each evening. In practice, however, equipment to continuously record the numbers of males present was not available, and it would be difficult to sample each swarm more than once an evening without disrupting their natural behaviour.
Mosquito sampling and identification
At least 30 males from each swarm were collected by a single sweep with a sweep net at the estimated peak of the swarming period, as for the surveys in 2005 and early 2006. Samples were identified to species and molecular form by the PCR method described by Favia et al.. The identity of mosquitoes in swarm sites where single-species swarms had occurred in 2005 and early 2006 continued to be monitored for this study August-October of 2006, throughout 2007 and July-October of 2008 and 2009. The identities of at least 30 males per swarm were assessed for all the swarms used in the study presented here from 2006 – 2009, and none were found to consist of more than one species. It must be noted, however, that it is not possible to be absolutely certain a given swarm consists of only a single species without collecting the entire swarm, which would defeat the purpose of recording swarm duration. We have, however, undertaken a standardised sampling protocol and identified a reasonable number of mosquitoes from each swarm; 30 mosquitoes from each of 1,000 swarms (see 'Monitoring the timing of An. coluzzii and An. gambiae swarming’).
Genomic DNA (~10-50 ng) from individual An. gambiae s.l. specimens was PCR amplified using primers R3, R5, Mopint and B/Sint. The PCR conditions were 30 s at 94°C, 30 s at 63°C and 30 s at 72°C for 25 cycles, with a final extension step at 72°C for 7 min. Amplification products were run in a 1.5% agarose gel. The few specimens (~1.1%) that failed to be identified by this protocol were further analysed by the PCR technique of Scott et al., which reliably detects An. arabiensis, a sibling species in the An. gambiae s.l. complex. Only half of these specimens were found to be An. arabiensis. The remaining unidentified specimens were reanalysed by the PCR method of Fanello et al., and were confirmed to be An. coluzzii. We are confident in our choice of methods, in spite of the potential errors raised by Santolamazza et al.[46, 47], since the risk is an overestimate of hybrid An. coluzzii/An. gambiae females, but we only identified males.
Recording environmental parameters in the field
The environmental parameters air temperature (T°), relative humidity (% RH) and light intensity (W/m2) were recorded on a data logger (Model: ETHG912, OREGON Scientific, Tualatin, Oregon, U.S.A.) at the start of every swarm observed in 2007. One such data logger was placed on the ground at each swarming site one hour before swarm formation was expected. The sensors were placed on top of the data logger (~ 10 cm above ground), where they would not disrupt the flight of swarming mosquitoes, which occurred from ~ 1 – 2 m above ground. The IRSS/Centre Muraz field teams were responsible for checking that the data loggers ran smoothly and geo-referenced each swarm site to be certain the same sites were used on each occasion.
Recording individual male activity at dusk under ambient environmental conditions
The male mosquitoes were the offspring of gravid females collected from the wild in Vallée du Kou (An. coluzzii) and Soumousso (An. gambiae) and reared under the same environmental conditions in the insectary at IRSS/Centre Muraz. To ensure that the males were sexually mature and a standardized age, only 3-day-old males were used.
Six males of each species were randomly selected, placed in the actograph ~ 1 hour before sunset and their behaviour was video-recorded for a single 3 hour dusk period (17:00 – 20:00) at IRSS/Centre Muraz (Figure 1). The placement of An. coluzzii and An. gambiae males in the actograph was varied daily to control for position.
The behaviour of each of the 12 mosquitoes in the actograph was recorded with a video camera (SONY Model: DCR-TRV60E; Figure 1B) installed on a platform 2 m above ground, where the actograph was exposed to ambient environmental conditions (Figure 1C). The video camera was positioned above the actograph looking down, so that the mosquitoes in all 12 chambers were visible (Figure 1C). A bank of infra-red lights (900 nm wavelength LEDs; at the peak sensitivity of the video camera, but beyond the mosquito’s spectral sensitivity was positioned under the actograph (Figure 1B) to provide even lighting for the video camera throughout the steep change in ambient light intensity across dusk. The intensity of infra-red light was high enough to compensate for changes in ambient illumination throughout dusk, so that the recorded video image remained at a constant brightness throughout the recording period.
The timing of spontaneous activity was recorded for n = 126 males of each species (6 males of each form/night, for 21 nights in September – October, 2008). The data on timing of activity of each group of mosquitoes in the actograph was determined by Security Spy (http://www.bensoftware.com/securityspy|) software installed on a Mac G5 computer.
Pearson’s Correlation Coefficient Test, based on critical values for the regression 'r’ (two-tailed distributions), was used to assess the correlation between each environmental variate in turn (temperature, humidity, light intensity and time of sunset) with the start and end of swarming times, with the statistical package 'R’. The distribution of all variates was found to be normal by visual observation of histograms. The squared correlation coefficient (r2) is also reported as a measure of how much of the variability in swarm times can be explained by a particular variate, e.g., if r2 = 0.54, it is likely that 54% of the correlation can be accounted for by that variate.
Unfortunately, it is not possible to compare the mean swarm start and stop times of the two species directly because the data for An. coluzzii were collected only in VK7 and for An. gambiae only in Soumousso since site and species are confounded. The cause of statistically significant differences could be due to differences between the villages and/or between species. Indeed, since the villages are situated ~ 24' latitude and ~ 22’ longitude apart, the clock times at sunset differed by an average of 1:30 (min:sec) throughout the year, varying within a range of 0:46 (December) to 2:12 (June) due to the tilt of the Earth and its irregular shape. Accordingly, even if the two species started swarming at the same 'time of day’ in relation to sunrise/sunset, on average An. gambiae in Soumousso would begin to swarm ~1:30 min:sec before An. coluzzii in VK7 by clock time. Therefore, for comparisons between the two species, swarming start and end times were indexed to local sunset times at their respective sites by calculating the offset between the local start time or end time of swarming and the local time of sunset on the same evening. The mean monthly differences between the two species in relation to the time after sunset swarming started or ended, and swarm durations were compared by Welch’s t-test (unequal variances).
To analyse the actograph recordings, the 3 hour dusk observation period was divided into 180–1 minute 'time bins’, and each mosquito was given a score of '1’ if it was active for at least 25% of the minute, or '0’ otherwise. The proportion of mosquitoes active out of the total possible (126 male for each species) was calculated for each species for each minute. The time at which 50% of males were active was calculated with a probit-like 'LD50’ GLM analysis, modified by fitting a 'cauchit’ transformation (similar to a probit, but with more weight on the tails of the distribution). An ANOVA was used to test sequentially the effect of time, form and time:form on the distribution of data points.
Species composition of swarms
We genotyped 30 mosquitoes per swarm to determine their species and molecular form identity. As expected, the samples from Vallée du Kou were composed exclusively of An. coluzzii and those from Soumousso were exclusively An. gambiae.
Effects of environmental parameters on swarm times
Regression analysis of swarm start and stop times against environmental parameters based on Pearson’s Correlation Coefficient test (two-tailed distribution)
An. gambiae s.s.
df = n-2
Time of sunset
Time of sunset
The patterns of variation in data points above and below the regression lines in Figure 5 reflect monthly variations in swarm times, as is also evident in Figures 2C and3C. The effect of month has not been analysed in depth since we have only one month’s data for November, December and January-May. Nonetheless, the 95% confidence interval lines (fine dashed lines, Figure 5) show, overall, how tightly distributed the data are along the regression lines in all four cases.
Differences in swarming times between species
Comparisons of the mean times (minutes) of swarming activity in relation to sunset
An. gambiae s.s.
Offset between swarm start and sunset
Offset between swarm end and sunset
Onset of spontaneous activity at dusk in An. coluzzii and An. gambiae males
These results are consistent with the field observations that male An. gambiae start swarming earlier than An. coluzzii males (Results above, Figure 4A). The criteria used to define the start of activity in the two assays are too different, however, to allow more detailed comparisons between the swarm start times and actograph activity times; the start of swarming is defined as the time that the first mosquito started swarming at a particular site, and the start of flight activity in the actograph is defined as the first minute in which more than half the individual mosquitoes of a given species were active. It is worth noting, however, that the actograph assessment compared the activity levels of both species in the same apparatus at the same time, and, therefore, direct comparisons between the species are more reliable.
The occurrence of dusk swarms in An. coluzzii and An. gambiae appears to be controlled predominantly by time of day. Most reports on the timing of An. gambiae swarms in the literature state that swarms form within ~ 10 min of 18:00[36–39, 51]. The field data presented here shows that the time of sunset is the environmental factor that is most strongly correlated with the start and end of swarming activity. Taken together with laboratory-based evidence that male and virgin female An. gambiae have a circadian peak in activity during the first hour after lights off, the findings presented here suggest that the timing of swarming activity in An. gambiae s.l. species is mainly regulated by a biological clock that enables them to adjust to cyclic changes in day length (photoperiod) and the timing of sunset throughout the year. This circadian rhythm of activity enables the synchronisation of male and female sexual activation even as day length varies throughout the year. This observation is not new, as a range of physiological processes and behavioral activities have been shown to be under circadian control in organisms from bacteria to mammals.
Humidity was also significantly correlated with the start and end of swarming. It is worth noting, however, that changes in mean humidity closely followed changes in the timing of sunset; both increased from April-July and decreased from July-December, and, therefore, it is not possible, based on this data set alone, to determine the extent to which changes in humidity have a direct affect on swarming, or are simply correlated with other seasonal changes, such as sunset. Temperature and light intensity at the time of swarming were also significantly correlated with swarming in some cases (Table 1), but unfortunately, changes in these parameters were not measured during the period at dusk leading up to swarming, so it is not possible to determine the extent to which short-term changes in these parameters at sunset might have had an effect on the timing of swarming, or whether changes in these parameters are simply correlated with the overall changes in meterological conditions at dusk, and, therefore, are an alternative way of assessing the correlation of swarming times with sunset. Likewise, it is beyond the scope of this study to distinguish the subtle effects of changes in each environmental parameter over a scale of months since all of these parameters are correlated with seasonal meteorological changes. It is clear, however, that the timing of swarming was not 'triggered’ or initiated in some way by particular values of temperature, humidity or light intensity, or we would have recorded more constant values of these parameters across the seasons and irrespective of changes in sunset times.
Our results also show that swarming began earlier in An. gambiae than in An. coluzzii, with a mean difference in the start of swarming of ~ 3.5 min, and ended earlier by a mean of ~ 5 min, over the course of a swarming period that lasted for ~22 min in each species. The difference in swarming times of the two species suggest that, when the two species swarm at the same site, each species would be allochronically (i.e., temporally) isolated from the other for ~ 15- 20% of their respective swarm durations. The accuracy of these estimates is compromised by two sources of error due to the limitations of fieldwork; 1) the observations of each species were made in separate villages, separated by ~24' latitude and ~22’ longitude, which means that clock times are not directly comparable, and 2) the timings of the start and end of swarming are based on the appearance of the very first and very last male to be seen swarming over a marker, and therefore subject to variation between individuals as well as between species. The first limitation is, perhaps the most serious one, in that the times of sunset according to a clock would be earlier in Soumousso, where An. gambiae swarms were monitored, than in VK7, where An. coluzzii swarms were monitored, due to the former being further east and south than the latter. Hence, the swarm start and end times for the two species are not independent of their respective geographic positions. However, the actograph results are more robust because both species were recorded on the same nights under identical conditions, and the differences in timing of activity are based on the mean behaviour of six mosquitoes per data point. The actograph findings indicate that the difference between the two species in onset of activity is ~ 10 min, which implies an even greater degree of allochronic separation between the species in mixed swarms. Thus, the differential timing of swarming in the two species may have contributed to the reproductive isolation of these two taxa, a hypothesis that was proposed by Charlwood and Jones in relation to speciation within the An. gambiae complex more than 30 years ago.
A recent laboratory study by Rund et al. on differences in the timing of daily activity in M (An. coluzzii) and S (An. gambiae) molecular form males from laboratory-reared colonies of strains that originated in Mali found that the peak in male M form occurred 2.9 – 4.1 min earlier than in S form males, whereas the study presented here found that An. gambiae were active earlier than An. coluzzii. Although at first sight these results appear to be contradictory, it is interesting to note that the order of magnitude of difference in the timing of activity is similar (3 – 5 min) in both cases and that the Rund et al. study was conducted with strains of mosquito that had been colonised for many generations. The timing of flight activity may be relatively labile within a range of changes of up to 5 minutes, and that the direction of selection for early or late onset of activity may be fairly arbitrary.
Both studies confirm that the timing of mating is predominantly under circadian control, and based on a range of studies in Drosophila spp and other insect species[53–55] differences in the phase of activity may lead to temporal separation, and thereby contribute an allochronic component to speciation.
We have shown that swarming in An. coluzzii and An. gambiae lasts ~ 20 min at dusk, and that the start and end of swarming in two species occurs at significantly different times; should they swarm at the same site, they would overlap for only 15-20% of the their respective swarming periods. These results support the hypothesis that the two species swarm at partially different times, and, when considered together with their differences in swarm site preferences[21, 37] and seasonal differences in population sizes, the overall effect is a reduced likelihood of hybridisation. The implications of these findings are of relevance to the basic concept of releasing genetically modified mosquitoes or sterile males to interfere with reproduction in An. gambiae populations; we have shown that the window for mating in swarms is short, and relatively small differences in the timing of activity can significantly reduce the mating competitiveness of colonies reared for release. In addition, the findings presented here contribute to a greater understanding of the prezygotic barriers to hybridisation between An. coluzzii and An. gambiae.
The success of a GMO or sterile release programmes will depend largely on whether released males can survive and successfully compete for mates against wild males[56–59]. The use/release of such GMO or sterile males requires a proper understanding of potential interactions with naturally occurring populations. Gathering information on the behavioural and ecological factors that govern Anopheles reproductive biology in general and in particular regarding swarming and mating behaviour, will increase the chances of success of GMO and sterile male-based control efforts[57–60].
This study was financially supported by the Multilateral Initiative on Malaria (MIM) Project A60098 through the UNICEF/UNDP/World Bank/WHO Special Programme for Research and Training in Tropical Diseases (TDR). The authors are grateful to the populations of Soumousso and Vallée du Kou who made this study possible.
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