Skip to main content

First report of the influence of temperature on the bionomics and population dynamics of Aedes koreicus, a new invasive alien species in Europe



Aedes koreicus was detected in northern Italy for the first time in 2011, and it is now well established in several areas as a new invasive mosquito species. Data regarding the influence of temperature on mosquito survival and development are not available yet for this species.


We experimentally investigated the influence of different constant rearing temperatures (between 4 and 33 °C) on the survival rates and developmental times of different life stages of Ae. koreicus under laboratory conditions. The resulting data were subsequently used to inform a mathematical model reproducing the Ae. koreicus life-cycle calibrated to counts of adult females captured in the field in the autonomous province of Trento (northern Italy) between 2016 and 2018.


We found that temperatures above 28 °C are not optimal for the survival of pupae and adults, whereas temperate conditions of 23–28 °C seem to be very favorable, explaining the recent success of Ae. koreicus at establishing into new specific areas. Our results indicate that Ae. koreicus is less adapted to local climatic conditions compared to Ae. albopictus, another invasive species which has been invading the area for the last three decades. Warmer seasons, which are more likely to occur in the future because of climate change, might extend the breeding time and therefore increase the abundance of Ae. koreicus in the study region.


Our findings provide, to our knowledge, the first evidence on how temperature influences the bionomics and dynamics of Ae. koreicus and highlight the need for further studies on the phenology of this species in temperate areas of Europe.


Several invasion events by alien mosquito species have occurred in Europe in recent decades [1]. The most successful invasive Aedes mosquito species is Ae. albopictus (Skuse, 1894), which has been recorded in Italy since the end of the 20th century [2]. In 2008, a new aedine mosquito species, Ae. koreicus (Edwards, 1917), was found in Europe (in Belgium) for the first time [3]. It was subsequently detected in Italy in 2011 [4], where it has now established in several areas in the northern part of the country, including Veneto region and the autonomous province of Trento, overlapping with the current distribution of Ae. albopictus [5, 6]. Habitat-suitability models predict that parts of the main rivers (Po and Adige) valleys will be colonized over the next decade and that Ae. koreicus may establish in areas 400–1500 m above sea level, i.e. above the altitude range of Ae. albopictus [7]. Thus, a wider geographical range could be colonized by Aedes mosquitoes, enlarging the areas with possible Aedes-borne disease transmission. In fact, this new invasive species has a potential impact on human and animal health since Ae. koreicus can transmit Dirofilaria immitis, a heartworm, endemic in northern Italy [8], and could be involved in chikungunya virus transmission [9], whose last European autochthonous outbreak occurred in Lazio region (Italy) in 2017 [10].

Mosquito survival and development are critically affected by environmental temperatures as well (e.g. [11,12,13,14]), and quantitative information on this relationship is critical to assess the population dynamics and potential environmental suitability of different mosquito species. Temperature can also affect virus transmission, for example by decreasing the length of the extrinsic incubation period [15] and by increasing transmission probability [16]. To the best of our knowledge, no quantitative data are available for Ae. koreicus. To fill this gap, we carried out laboratory experiments to evaluate whether different rearing temperatures exert an effect on the phenology of this species, in particular on the developmental time and survival of immature stages and on adult survival rates and length of the gonotrophic cycle of Ae. koreicus.

We designed a density-dependent mechanistic model that incorporates the effect of temperature on the temporal variations of Ae. koreicus population for both adults and immature stages. We calibrated our model on the number of trapped adult female mosquitoes recorded in four sites in the province of Trento between 2016 and 2018. This kind of model includes the main mosquito life-cycle processes (from egg hatching to adult mortality), thus replicating closely the actual population dynamics and providing a suitable framework to investigate the main determinants of observed dynamical patterns [17]. Several models have been proposed to explore Aedes mosquitoes population dynamics, especially for Ae. albopictus [18,19,20], Ae. aegypti (Linnaeus, 1762) [21, 22] and more recently also for Ae. japonicus japonicus (Theobald, 1901) [23]. To the best of our knowledge, this is the first attempt to model the population dynamics of Ae. koreicus.

The calibrated model was used to forecast possible changes in Ae. koreicus seasonal dynamics under alternative temperature scenarios, and to compare the adaptation to the local habitat conditions of Ae. koreicus with respect to Ae. albopictus, which has been present in the study area for many years [24].


Study area and entomological data

Mosquito sampling was carried out in the province of Trento (46°04′00″N, 11°07′00″E), northern Italy. This mountainous area covers partially the Dolomites and the southern Alps. The climate of the study region is temperate-oceanic with three main areas: subcontinental (the main valleys with more severe winters), continental (the alpine valleys) and alpine (the areas above the tree line) [25]. Four trapping locations (A: 46°05′0.56″N, 11°09′38.27″E; B: 46°04′40.08″N, 11°08′39.01″E; C: 45°59′30.77″N, 11°40′19.34″E; and D: 46°02′55.21″N, 11°32′26.99″E; see Fig. 1) were chosen within three municipalities (Trento, Grigno and Castel Ivano). We deployed one BG Sentinel (Biogents AG, Regensburg, Germany) trap (version 1) for each location. Traps were sheltered from rain and direct sunlight and were baited with BG-lure and CO2. They ran for 24 h fortnightly from the end of April or beginning of May to the end of October or beginning of November between 2016 and 2018. Each trap was powered by a 12 V battery. All mosquitoes were collected in a catch bag and carried to Edmund Mach Foundation laboratories (San Michele all’Adige, Italy) for identification under a stereoscope to the species level using taxonomic keys [26, 27].

Fig. 1
figure 1

Study area. Key: red dots, trap locations; orange triangles, weather stations. Map data © OpenStreetMap contributors [40]

Climatic data

Temperature time series (daily average), collected by three ground stations (Fig. 1, orange triangles), were obtained from Meteotrentino [28].

Mosquito colony

We established an Ae. koreicus colony in the laboratory from larvae and pupae collected in the field (Castel Ivano, Italy; 46°02′N, 11°32′E; 360 m a.s.l) and kept in a climatic chamber at 23 ± 1 °C and a relative humidity of 75 ± 5%, with a photoperiod of 16L:8D with 1 h of dawn and 1 h of dusk [29]. Larvae were reared in 500 ml plastic cups filled with 250 ml of dechlorinated water and fed daily with finely ground cat food (Cat food Adult Fit 32TM, Royal Canin®, Aimargues, France). Adults were kept in a cage 45 × 45 × 45 cm (Bugdorm, MegaView Science Co., Ltd, Taiwan) supplied with cotton soaked in 10% sugar solution ad libitum. As suggested in Watson et al. [30], we set a black fabric on the back side of the cage to offer shaded oviposition and resting sites. Twice a week the colony was fed on cow blood for 1 h provided with Hemotek blood-feeding system (Hemotek Ltd., Accrington, England). Two ovitraps were placed inside the cage with filter paper as oviposition substrate. Strips with eggs were then removed and placed in plastic cups, stored in plastic bags loosely sealed and sprayed with water every week to maintain high RH [29].

Egg-hatching experiment

One/two months-old colony eggs were placed in groups of 20 in white plastic glasses filled with 100 ml of dechlorinated water. Preliminary laboratory experiments showed that most of the newly laid eggs needed several days before being completely embryonated, thus we decided to use eggs old enough to be viable. Twenty replicates of 20 eggs each were made for each tested temperature, namely 8, 13, 23, 28 and 33 °C. Experiments at 13 °C and 23 °C were performed first; because survival did not show any remarkable difference (see “Results” section), we decided not to perform the experiment at intermediate temperatures. Five repetitions of 20 eggs each were used as controls at 23 °C for each temperature tested. RH and light were set as in the mosquito colony rearing conditions. Four mg of finely ground cat food was added to the water as hatching stimulus. The 20-eggs papers were left in water for 5 days and the number of larvae counted daily and removed.

Larval survival and developmental time

A group of 10 less than 12-h-old first-instar larvae were placed in a plastic cup filled with 100 ml of dechlorinated water. We set 12 cups for each tested temperature, namely 4, 13, 18, 23, 28 and 33 °C. RH and light were set at the same values as mosquito colony rearing conditions. Every day exuviae and dead larvae were removed. The stage of each living larva was identified, and the number of each instar counted. Finely ground cat food was added daily to the water according to the larval stage: 0.1 mg/larva for L1; 0.2 mg/larva for L2; 0.3 mg/larva for L3; and 0.4 mg/larva for L4. The food amount was chosen consistently with the protocol proposed in [11], where Ae. albopictus larvae were fed daily, with the quantity of food increasing according to the stage of development (0.2 mg for L1, 0.4 mg for L2, 0.6 mg for L3, and 0.8 mg for L4). Preliminary experiments showed that halved quantities were still sufficient for Ae. koreicus larval development, as usually the placed food was not wholly consumed within one day. Every 48 h, excess food was removed, and half of the water was changed to avoid formation of bacterial scum. Cups were refilled with dechlorinated water to maintain the initial volume, and randomly rotated on the tray to prevent any position effects. Pupae were removed from the cups and isolated, and then the number of males and females was recorded.

Adult longevity and gonotrophic cycle

Larvae were reared in 500 ml plastic cups filled with 250 ml of dechlorinated water in a climatic chamber at 23 ± 1 °C and 75 ± 5% RH with a photoperiod of 16L:8D with 1 h of dawn and 1 h of dusk, adapting the protocol adopted in [11]. Finely ground cat food was added daily to the water according to the larval stage: 0.1 mg/larva for L1; 0.2 mg/larva for L2; 0.3 mg/larva for L3; and 0.4 mg/larva for L4. Every 48 h, food excess was removed, and half of the water was changed to avoid formation of bacterial scum. Cups were refilled with dechlorinated water to maintain the initial volume. Pupae were isolated in plastic cups filled with 250 ml of dechlorinated water and placed in 22 × 22 × 22 cm cages (Bugdorm, MegaView Science Co., Ltd, Taiwan). Every day the cup with pupae was moved in another cage with the same size, therefore all the adults inside a cage were at the same age (˂ 24 h). Male and female mosquitoes were left together for 5 days for free mating and supplied with cotton soaked in 10% sugar solution ad libitum. After this period, females were allowed to feed on cow blood provided via a Hemotek blood-feeding system (Hemotek Ltd., Accrington, UK) for 30 min twice a week. Then, one male and one engorged female of the same age were isolated as a couple in a cage with an ovitrap lined with filter paper as oviposition substrate and 10% sugar solution ad libitum. We set 15 cages for the trials at 18, 28 and 33 °C, and 22 cages for the trial at 23 °C. To stimulate oviposition, the ovitrap was filled with 200 ml dechlorinated water and 5 ml of grass infusion prepared following the protocol proposed in [31]. A black fabric was set on the back side of the cage to offer shaded oviposition and resting sites. The date of blood meal and oviposition was recorded to calculate the gonotrophic cycle length of females. Ovitraps were checked daily for eggs laid on filter paper and, if present, counted and removed. The dates of death were recorded to calculate adult longevity.

Temperature-dependent functions

For each immature stage, we computed daily death rates from measures of the average developmental time and survival. Taking as example the transition from eggs (E) to first-instar larvae (L1), we can describe the dynamics with the following system of ordinary differential equations (ODE)

$$E^{\prime} = - \left( {\tau_{E} + \mu_{E} } \right)E$$
$$L_{1}^{'} = \tau_{E} E$$

The experiment starts with E0 initial eggs that eventually develop into k (k ≤ E0) first-instar larvae over an average time of 1/τE days. Thus, a simple calculation leads to compute the death rate as

$$\mu_{E} = \tau_{E} \left( {\frac{{E_{0} }}{k} - 1} \right).$$

Similarly, we computed \(\mu_{j} \forall j \in \left\{ {L_{1} ,L_{2} ,L_{3} ,L_{4} ,P} \right\}\).

Subsequently, we modeled the mortality and developmental rates across different mosquito life stages as functions of temperature by fitting a suitable set of functions of the temperature T:

$$F_{1} \left( T \right) = \frac{{\exp \left( {a - b \cdot T} \right)}}{{1 + \exp \left( {a - b \cdot T} \right)}},\;F_{2} \left( T \right) = \frac{1}{{a + b \cdot { \exp }\left( {c \cdot T} \right)}},\;F_{3} \left( T \right) = a + b \cdot { \exp }\left( {c \cdot T} \right).$$

Uncertainty in model parameters was estimated by perturbing the computed functions with an additive error sampled from a normal distribution with variance equal to the average of the interpolation residuals [18].

Model design

We modelled the population dynamics of Ae. koreicus by accounting for its 7 life stages, namely eggs (E), the four larval instars (L1, L2, L3, L4), pupae (P) and female adults (A). The model can be described with the following system of ODE:

$$E^{\prime} = n_{E} \tau_{A} A - \left( {\tau_{E} + \mu_{E} } \right)E$$
$$L_{1}^{'} = \tau_{E} E - \left( {\tau_{{L_{1} }} + \mu_{{L_{1} }} \left( {1 + \frac{L}{K}} \right)} \right)L_{1}$$
$$L_{2}^{'} = \tau_{{L_{1} }} L_{1} - \left( {\tau_{{L_{2} }} + \mu_{{L_{2} }} \left( {1 + \frac{L}{K}} \right)} \right)L_{2}$$
$$L_{3}^{'} = \tau_{{L_{2} }} L_{2} - \left( {\tau_{{L_{3} }} + \mu_{{L_{3} }} \left( {1 + \frac{L}{K}} \right)} \right)L_{3}$$
$$L_{4}^{'} = \tau_{{L_{3} }} L_{3} - \left( {\tau_{{L_{4} }} + \mu_{{L_{4} }} \left( {1 + \frac{L}{K}} \right)} \right)L_{4}$$
$$P^{\prime} = \tau_{{L_{4} }} L_{4} - \left( {\tau_{P} + \mu_{P} } \right)P$$
$$A^{\prime} = \frac{1}{2}\tau_{P} P - \left( {\mu_{A} + \chi \alpha \tau_{A} } \right)A$$
$$C^{\prime} = \chi \alpha \tau_{A} A$$

where τj and μj are respectively the temperature-dependent developmental and daily death rates of stage j with \(j \in \left\{ {E,L_{1} ,L_{2} ,L_{3} ,L_{4} ,P,A} \right\}\). Similarly to what proposed for Ae. albopictus, mortality rates for immature stages and adults were multiplied by the same scaling factors as in [18] to take into account the lower survival in the field compared to laboratory-controlled conditions. The developmental rates correspond to egg hatching (τE), larval molting (τL1, τL2, τL3), pupation (τL4), adult emergence (τP) and gonotrophic cycle (τA). K is a density-dependent scaling factor driving the carrying capacity for the larval stages (L = L1 + L2 + L3+ L4). The average number of eggs laid in one oviposition, nE, was set to 100 [32]. Female adults are trapped with rate α∙χ, where α is the daily capture rate of the traps and χ is a function of time defined equal to 1 when the trap is open and 0 otherwise. Since BG traps capture host-seeking mosquitoes, only a fraction A·τA of adults can be trapped. C represents the cumulative number of captured female adult mosquitoes. As only female adult mosquitoes are explicitly considered in the model, the term 1/2 in the equation for adults accounts for the sex ratio. The seasonal dynamics of the mosquito population was simulated from April 1 to October 31 for each site and year under study. Since no data are available on the overwintering mechanisms of Ae. koreicus, we simulated each year separately by initializing the system with 500 eggs.

The model has two free parameters: the daily capture rate of adult mosquitoes α and a larval density dependent factor K. While α is assumed to be equal among different traps and years, K is assumed to be both site- and year-specific. Thus, there are 13 parameters to estimate which form the set of unknown parameters Ψ. Specifically, \(\varPsi = \left\{ {\alpha ,K\left( {s,y} \right)_{{s \in \left\{ {A,B,C,D} \right\},y \in \left\{ {2016,2017,2018} \right\}}} } \right\}\). The posterior distributions of Ψ were estimated by Markov Chain Monte Carlo (MCMC) sampling. The Poisson likelihood of the observed weekly captures given model-predicted ones was multiplied across the 12 datasets (4 traps and 3 years) under study to provide the overall likelihood of observations:

$$L = \mathop \prod \limits_{y = 2016}^{2018} \mathop \prod \limits_{{s \in \left\{ {A, \ldots ,D} \right\}}} \mathop \prod \limits_{m = 1}^{{M\left( {s,y} \right)}} e^{{ - C\left( {s,y,m,\psi } \right)}} \cdot \frac{{C\left( {s,y,m,\uppsi} \right)^{{n\left( {s,m,y} \right)}} }}{{n\left( {s,m,y} \right)!}}$$

where y, s and m run over the considered years, trapping sites and trapping sessions respectively, M(s,y) is the total number of trapping sessions carried out for the specific site and year, n(s,m,y) is the observed number of trapped adults and C(s,y,m,Ψ) is the number of captures predicted by the model with parameters Ψ. The posterior distribution of Ψ was obtained by using random-walk Metropolis-Hastings as an acceptance criterion, recursive normal jumps for parameter sampling and uninformative (uniform) priors.

We then applied the model to assess the influence of temperature on the population dynamics, using temperature records from the closest weather station to each trap site. To this aim, we re-simulated the mosquito abundance for each year y and site s using the estimated posterior distributions of Ψ and 10 different temperature patterns Ts,y(t) ranging from \(\overline{{T_{s,y} }} \left( t \right) - 2.5^\circ\) to \(\overline{{T_{s,y} }} \left( t \right) + 2.5^\circ\), where \(\overline{{T_{s,y} }} \left( t \right)\) is the recorded daily average temperature associated to year y and study site s.

Finally, we investigated whether Ae. albopictus is better adapted to the climate conditions of the study area by running the population model proposed in [18] for this species with the estimated posterior distributions of Ψ. In particular, we used the same capture rate α since our estimate was consistent (see “Results” section) with a previously published measure for this parameter for Ae. albopictus [33].


Entomological collections

The total numbers of trapped female Ae. koreicus over all sites were 100, 145 and 214 in 2016, 2017 and 2018 respectively. A larger number of captures was observed in rural sites (C and D), which accounted for 36% and 26% of total collections, respectively. Capture data are presented in Additional file 1: Table S1.

Laboratory experiments

As shown in Fig. 2, higher temperatures shortened the developmental periods, with no substantial differences above 23 °C. Egg hatching rate was low at 8 °C, while it ranged between 50.50% and 52.25% for the other considered temperatures. At 4 °C, no first-instar larva survived. On the other hand, above 13 °C larval survival was quite high and seems little affected by temperature changes. Pupal and adult mortality increased considerably above 28 °C. In fact, adult females survived on average less than 6 days at 33 °C and at such temperature they never completed the gonotrophic cycle. Conversely, at the lower studied temperatures, females could survive for more than one month, taking on average between 9 and 15 days to complete the gonotrophic cycle. Observed survival rates, developmental times and longevities are reported in Tables 1, 2, 3.

Fig. 2
figure 2

Temperature-dependent functions. Dots represent the experiments observations; shaded area represents 95% CI of predicted values

Table 1 Experimental results for immature stages. Egg hatching rate (%) and larvae and pupae survival (%) at different temperatures obtained with the laboratory experiments. Numbers in parentheses represent the 95% CI
Table 2 Experimental results for immature stages: developmental time
Table 3 Experimental results for female adults. Average female adult longevity (μ −1A ) and gonotrophic cycle length (τ −1A ) (days)

Transition and death rates

All transition rates τ were fitted with logistic or exponential type functions (see Tables 4 and 5 and Fig. 2). The proposed functions interpolated quite well the experimental measures. In fact, the 95% confidence intervals (CI) of the predicted values were usually very narrow and the observed values always lie within them (Fig. 2). As temperature seems to have little influence on larval survival between 13 °C and 33°C, we decided to assume a temperature-independent daily death rate for each larval instar, obtained by averaging the rates observed at the different temperatures. Similarly, we assumed the gonotrophic cycle to last 11.6 days, the average computed with the experiments between 18 °C and 28 °C. As shown in Tables 4 and 5, the residuals between such averages and the estimates at different temperatures are quite small and comparable to those obtained with the fitted functions for the other rates.

Table 4 Temperature-dependent functions for transition rates τj, \(j \in \left\{ {E,L_{1} ,L_{2} ,L_{3} ,L_{4} ,P,A} \right\}\). Parameters for the temperature dependent functions for the development rates
Table 5 Temperature-dependent functions for daily death rates µj, \(j \in \left\{ {E,L_{1} ,L_{2} ,L_{3} ,L_{4} ,P,A} \right\}\). Parameters for the temperature dependent functions for the daily death rates

Modelling results

As shown in Fig. 3, the mosquito population model fits the observed weekly captures quite well. Considering the 12 datasets (4 traps and 3 years), 82.3% of the observed captures lie within the 95% credible intervals of model predictions.

Fig. 3
figure 3

Model fit for each trapping site A, B, C, D (from first to last row) from 2016 to 2018 (from first to last column). Dots: recorded captures; boxplots (median, quartiles and 95% quantiles): predicted captures

The estimated capture rate α was on average 0.157 (95% CI: 0.094–0.203), meaning that about 16% of the host-seeking females are captured in one day. Thus, an active trap might attract on average about 1.35% (α·τA) of the adult females living in the trapped area. A similar percentage (1.64%) was estimated for Ae. albopictus with the same trap type in the same study region [33]. As expected, the larval density dependent factor K varied between sites and each site showed different values across the three years (see Additional file 2: Text S1). A strong positive correlation was found between K(s, y) and the total number of Ae. koreicus collected at site s during year y (Pearsonʼs correlation coefficient r(10) = 0.96, P < 0.0001).

Figure 4 shows that changes in the daily average temperatures produced proportional effects on Ae. koreicus adult abundance from June onwards. Colder seasons are associated with a smaller size of adult populations, whereas hotter daily temperatures usually result in larger abundances and earlier occurrence of substantial densities. However, temperature peaks might cause temporary population drops (e.g. in all sites in 2017) and breeding seasons with sustained hot temperatures may be suboptimal for the maximal abundance during August and September (e.g. site A in 2018). Shifts in the daily temperatures may produce larger differences in specific some sites and years (e.g. site C in 2018).

Fig. 4
figure 4

Effect of temperature on Aedes koreicus. Predicted average densities (number of adult females per hectare) for 10 different scenarios obtained varying daily temperature T from −2.5 °C (dark blue) to 2.5 °C (dark red) with a step of 0.5 °C for each trapping site A, B, C, D (from first to last row) and year (from first to last column). Black lines represent the estimated average abundance with no temperature perturbations

Figure 5 shows the predicted average ratio in adult abundance between Ae. albopictus and Ae. koreicus. Higher Ae. albopictus abundances are expected during the summer, while Ae. koreicus is more abundant at the beginning and end of the breeding season. In fact, Ae. albopictus is generally more adapted to higher temperatures; for instance, pupal development is faster for this species above 25 °C (see Additional file 2: Text S1). The ratio of the two predicted population sizes reached its peak between August and September and was higher for more urban and warmer sites (A and B, see Additional file 2: Text S1) and during hotter seasons (2016 vs 2018). Finally, in colder sites and years the abundance ratio favors Ae. albopictus later in the season, meaning that cold temperatures are more optimal for Ae. koreicus for a longer part of the breeding season.

Fig. 5
figure 5

Aedes albopictus/Ae. koreicus ratio. Ratio between the average predicted adult Ae. albopictus and Ae. koreicus abundances for each trapping site A, B, C, D for each year under study


In this study, we provided for the first time important data on the influence of temperature on the bionomics and population dynamics of Ae. koreicus. Colder temperatures slow the development of immature stages and decrease egg survival, especially below 10 °C. On the other hand, temperatures above 28 °C are very unfavorable for pupae and adults as they increase the death rates and prevent females from completing the gonotrophic cycle. Thus, the optimal thermal range for this species lies between 23 °C and 28 °C, where mortality is low across all stages and the development of immature stages is rapid.

A population dynamics model incorporating data on the effect of temperature on the mosquito life-cycle explained the observed temporal and spatial variability of the population density quite well. The model slightly overestimates the mosquito abundance at the end of the breeding season, when mosquitoes are known to be less active and possibly less likely to be captured. This reduction in activity is usually triggered by endogenous factors such as lower temperatures and photoperiod [34]. In addition, Ae. albopictus mosquitoes start to lay more resistant eggs at the end of the breeding season [34], which hatch only during the following spring, thereby reducing the number of emerging adults. A similar behavior may hold also for Ae. koreicus, but because of the lack of available data we could not explicitly consider it in our model.

We found that warmer seasonal temperatures usually cause an upper shift of the adult abundance curve and an anticipation of the breeding season, although very high temperatures in hotter months may cause sudden population drops. Warmer conditions are more likely to occur in the study area in the future because of climate change; indeed, a recent study suggested that temperatures might increase by up to 4 °C by the end of the 21st century throughout the Alpine region [35].

Captures were usually higher in the colder sites, possibly because of a larger availability of breeding sites, which is reflected by larger estimated larval scaling factors. In addition, previous studies in the same region showed that forested areas seem suitable for Ae. koreicus, while Ae. albopictus prefers artificial ones [5, 36].

Our findings clearly indicate that Ae. koreicus is still less adapted to the study region’s climate than Ae. albopictus. Although Ae. koreicus develops faster than Ae. albopictus at colder temperatures, the latter is more adapted to warmer conditions similar to the ones observed during summer in the province of Trento (see Additional file 2: Text S1 for a comparison of temperature-dependent rates). Our modelling results confirm that, given the same availability of breeding sites, Ae. koreicus might be more abundant than Ae. albopictus during the colder months of the breeding season, i.e. May-June and October-November. A weak larval interspecific competition has been demonstrated under laboratory conditions between these two species, with a slight advantage for Ae. albopictus [29]; however, shared breeding sites are not very common [5, 26]. Ecological competition could be taken into account in the model as previously done with Cx. pipiens (Linnaeus, 1758) [37] to assess its occurrence in the field, and this mechanism, similarly to diapause, might contribute to reduce the predicted overabundance at specific times of the year as it would decrease larval survival; however, this was beyond the scope of this work, also because of the limited available data.

We modelled mosquito population dynamics by considering only average daily temperatures, similarly to previous studies [10, 18,19,20,21,22, 37]; nonetheless, temperature fluctuations within a day might have a significant impact on mosquito abundance [38] and should be considered. However, we did not have access to temperature data at a finer temporal resolution than the daily average, and experiments on developmental rates were carried out at constant temperatures.

Aedes koreicus has been shown to be a competent vector for chikungunya virus [9] and Dirofilaria immitis [8]. In order to estimate pathogen transmission risks from the observed abundance of this species [19], several important factors still need to be quantified. For instance, the feeding preference, i.e. the preferred hosts for a blood meal, of Ae. koreicus has not been evaluated yet. Larvae of this species were found far from human settlings, indicating that the species can complete its life-cycle feeding on animals other than humans [26]. Another key parameter is the flight range, which is essential to compute the density of mosquito populations from capture data. The adult population estimated by our model depends on the attraction basin of the traps and eventually on the mosquito flight range. Here, because of the lack of available data, we assumed that the flight range of Ae. koreicus is equal to that of Ae. albopictus (150 m, see [39]), which resulted in densities in the same order of magnitude as Ae. albopictus in the same region [19]. An experimental estimate of the Ae. koreicus dispersal is crucial to accurately estimate the adult density, which is in turn critical to evaluate epidemiological risks for vector-borne pathogens.

Future studies, such as an assessment of the potential future areas of colonization of this species or an estimate of the transmission risk of an Ae. koreicus-borne pathogen, will certainly benefit from the present results, including the entomological dataset (Additional file 1: Table S1). In particular, our temperature-dependent model might be used, in the future, in an epidemiological framework to estimate pathogen transmission risks [18, 19, 22].


This study provides, to our knowledge, the first experimental data on how temperature affects the bionomics of Ae. koreicus mosquitoes, a new invasive mosquito species in Europe. The most favorable temperature range is between 23 °C and 28 °C, while hotter temperatures produce excessive pupal and adult mortality and block the gonotrophic cycle. These results explain the recent success of this species at establishing into temperate areas of Europe. Our modelling results validate these findings by reproducing population dynamics of the mosquito in the wild, predict the nonlinear effect of different temperature scenarios and highlight the need to investigate further the feeding and dispersal behavior of this species to estimate quantitatively the risks of transmission of pathogenic agents associated with Ae. koreicus.

Availability of data and materials

All data generated or analyzed during this study are included in this published article, its bibliography and its additional files.



relative humidity


confidence interval


  1. Medlock JM, Hansford KM, Schaffner F, Versteirt V, Hendrickx G, Zeller H, et al. A review of the invasive mosquitoes in Europe: ecology, public health risks, and control options. Vector Borne Zoonotic Dis. 2012;12:435–47.

    Article  Google Scholar 

  2. Sabatini A, Raineri V, Trovato G, Coluzzi M. Aedes albopictus in Italy and possible diffusion of the species into the Mediterranean area. Parassitologia. 1990;32:301–4.

    CAS  PubMed  Google Scholar 

  3. Versteirt V, Pecor JE, Fonseca DM, Coosemans M, Bortel WV. Confirmation of Aedes koreicus (Diptera: Culicidae) in Belgium and description of morphological differences between Korean and Belgian specimens validated by molecular identification. Zootaxa. 2012;3191:21–32.

    Article  Google Scholar 

  4. Capelli G, Drago A, Martini S, Montarsi F, Soppelsa M, Delai N, et al. First report in Italy of the exotic mosquito species Aedes (Finlaya) koreicus, a potential vector of arboviruses and filariae. Parasit Vectors. 2011;4:188.

    Article  Google Scholar 

  5. Baldacchino F, Montarsi F, Arnoldi D, Barategui C, Ferro Milone N, Da Rold G, et al. A 2-yr mosquito survey focusing on Aedes koreicus (Diptera: Culicidae) in northern Italy and implications for adult trapping. J Med Entomol. 2017;54:622–30.

    Article  CAS  Google Scholar 

  6. Montarsi F, Drago A, Martini S, Calzolari M, De Filippo F, Bianchi A, et al. Current distribution of the invasive mosquito species, Aedes koreicus [Hulecoeteomyia koreica] in northern Italy. Parasit Vectors. 2015;8:614.

    Article  Google Scholar 

  7. Marcantonio M, Metz M, Baldacchino F, Arnoldi D, Montarsi F, Capelli G, et al. First assessment of potential distribution and dispersal capacity of the emerging invasive mosquito Aedes koreicus in Northeast Italy. Parasit Vectors. 2016;9:63.

    Article  Google Scholar 

  8. Montarsi F, Ciocchetta S, Devine G, Ravagnan S, Mutinelli F, di Frangipane Regalbono A, et al. Development of Dirofilaria immitis within the mosquito Aedes (Finlaya) koreicus, a new invasive species for Europe. Parasit Vectors. 2015;8:177.

    Article  Google Scholar 

  9. Ciocchetta S, Prow NA, Darbro JM, Frentiu FD, Savino S, Montarsi F, et al. The new European invader Aedes (Finlaya) koreicus: a potential vector of chikungunya virus. Pathog Glob Health. 2018;112:107–14.

    Article  CAS  Google Scholar 

  10. Manica M, Guzzetta G, Poletti P, Filipponi F, Solimini A, Caputo B, et al. Transmission dynamics of the ongoing chikungunya outbreak in central Italy: from coastal areas to the metropolitan city of Rome, summer 2017. EuroSurveillance. 2017;22:17–00685.

    Article  Google Scholar 

  11. Delatte H, Gimonneau G, Triboire A, Fontenille D. Influence of temperature on immature development, survival, longevity, fecundity, and gonotrophic cycles of Aedes albopictus, vector of chikungunya and dengue in the Indian Ocean. J Med Entomol. 2009;46:33–41.

    Article  CAS  Google Scholar 

  12. Loetti V, Schweigmann N, Burroni N. Development rates, larval survivorship and wing length of Culex pipiens (Diptera: Culicidae) at constant temperatures. J Nat Hist. 2011;45:2203–13.

    Article  Google Scholar 

  13. Reuss F, Wieser A, Niamir A, Bálint M, Kuch U, Pfenninger M, et al. Thermal experiments with the Asian bush mosquito (Aedes japonicus japonicus) (Diptera: Culicidae) and implications for its distribution in Germany. Parasit Vectors. 2018;11:81.

    Article  Google Scholar 

  14. Spanoudis CG, Andreadis SS, Tsaknis NK, Petrou AP, Gkeka CD, Savopoulou-Soultani M. Effect of temperature on biological parameters of the West Nile virus vector Culex pipiens form ‘molestus’ (Diptera: Culicidae) in Greece: constant vs fluctuating temperatures. J Med Entomol. 2019;56:641–50.

    Article  Google Scholar 

  15. Tjaden NB, Thomas SM, Fischer D, Beierkuhnlein C. Extrinsic incubation period of dengue: knowledge, backlog, and applications of temperature dependence. PLoS Negl Trop Dis. 2013;7:e2207.

    Article  Google Scholar 

  16. Vogels CBF, Fros JJ, Göertz GP, Pijlman GP, Koenraadt CJM. Vector competence of northern European Culex pipiens biotypes and hybrids for West Nile virus is differentially affected by temperature. Parasit Vectors. 2016;9:393.

    Article  Google Scholar 

  17. Bolker BM. Ecological models and data in R. Princeton, NJ: Princeton University Press; 2008.

    Book  Google Scholar 

  18. Poletti P, Messeri G, Ajelli M, Vallorani R, Rizzo C, Merler S. Transmission potential of Chikungunya virus and control measures: the case of Italy. PLoS One. 2011;6:e18860.

    Article  CAS  Google Scholar 

  19. Guzzetta G, Poletti P, Montarsi F, Baldacchino F, Capelli G, Rizzoli A, et al. Assessing the potential risk of Zika virus epidemics in temperate areas with established Aedes albopictus populations. Eurosurveillance. 2016;21:30199.

    Article  Google Scholar 

  20. Tran A, L’Ambert G, Lacour G, Benoît R, Demarchi M, Cros M, et al. A rainfall- and temperature-driven abundance model for Aedes albopictus populations. Int J Environ Res Public Health. 2013;10:1698–719.

    Article  Google Scholar 

  21. Otero M, Solari HG, Schweigmann N. A stochastic population dynamics model for Aedes aegypti: formulation and application to a city with temperate climate. Bull Math Biol. 2006;68:1945–74.

    Article  Google Scholar 

  22. Marini G, Guzzetta G, Toledo CAM, Teixeira M, Rosà R, Merler S. Effectiveness of ultra-low volume insecticide spraying to prevent dengue in a non-endemic metropolitan area of Brazil. PLoS Comput Biol. 2019;15:e1006831.

    Article  Google Scholar 

  23. Wieser A, Reuss F, Niamir A, Müller R, O’Hara RB, Pfenninger M. Modelling seasonal dynamics, population stability, and pest control in Aedes japonicus japonicus (Diptera: Culicidae). Parasit Vectors. 2019;12:142.

    Article  Google Scholar 

  24. Roiz D, Neteler M, Castellani C, Arnoldi D, Rizzoli A. Climatic factors driving invasion of the tiger mosquito (Aedes albopictus) into new areas of Trentino, northern Italy. PLoS One. 2011;6:e14800.

    Article  CAS  Google Scholar 

  25. Neteler M, Roiz D, Rocchini D, Castellani C, Rizzoli A. Terra and Aqua satellites track tiger mosquito invasion: modelling the potential distribution of Aedes albopictus in north-eastern Italy. Int J Health Geogr. 2011;10:49.

    Article  Google Scholar 

  26. Montarsi F, Martini S, Dal Pont M, Delai N, Ferro Milone N, Mazzucato M, et al. Distribution and habitat characterization of the recently introduced invasive mosquito Aedes koreicus [Hulecoeteomyia koreica], a new potential vector and pest in north-eastern Italy. Parasit Vectors. 2013;6:292.

    Article  Google Scholar 

  27. European Centre for Disease Prevention and Control. Guidelines for the surveillance of invasive mosquitoes in Europe. Stockholm: ECDC; 2012.

    Google Scholar 

  28. Meteotrentino. Accessed 6 Aug 2019.

  29. Baldacchino F, Arnoldi D, Lapère C, Rosà R, Montarsi F, Capelli G, et al. Weak larval competition between two invasive mosquitoes Aedes koreicus and Aedes albopictus (Diptera: Culicidae). J Med Entomol. 2017;54:1266–72.

    Article  Google Scholar 

  30. Watson TM, Marshall KL, Kay BH. Colonization and laboratory biology of Aedes notoscriptus from Brisbane, Australia. J Am Mosq Control Assoc. 2000;16:138–42.

    CAS  PubMed  Google Scholar 

  31. Scott JJ, Crans SC, Crans WJ. Use of an infusion-baited gravid trap to collect adult Ochlerotatus japonicus. J Am Mosq Control Assoc. 2001;17:142–3.

    CAS  PubMed  Google Scholar 

  32. Ciocchetta S, Darbro JM, Frentiu FD, Montarsi F, Capelli G, Aaskov JG, et al. Laboratory colonization of the European invasive mosquito Aedes (Finlaya) koreicus. Parasit Vectors. 2017;10:74.

    Article  Google Scholar 

  33. Guzzetta G, Trentini F, Poletti P, Baldacchino FA, Montarsi F, Capelli G, et al. Effectiveness and economic assessment of routine larviciding for prevention of chikungunya and dengue in temperate urban settings in Europe. PLoS Negl Trop Dis. 2017;11:e0005918.

    Article  Google Scholar 

  34. Denlinger DL, Armbruster PA. Mosquito diapause. Annu Rev Entomol. 2014;59:73–93.

    Article  CAS  Google Scholar 

  35. Coppola E, Raffaele F, Giorgi F. Impact of climate change on snow melt driven runoff timing over the Alpine region. Clim Dyn. 2018;51:1259–73.

    Article  Google Scholar 

  36. Baldacchino F, Marcantonio M, Manica M, Marini G, Zorer R, Delucchi L, et al. Mapping of Aedes albopictus abundance at a local scale in Italy. Remote Sens. 2017;9:749.

    Article  Google Scholar 

  37. Marini G, Guzzetta G, Baldacchino F, Arnoldi D, Montarsi F, Capelli G, et al. The effect of interspecific competition on the temporal dynamics of Aedes albopictus and Culex pipiens. Parasit Vectors. 2017;10:102.

    Article  Google Scholar 

  38. Beck-Johnson LM, Nelson WA, Paaijmans KP, Read AF, Thomas MB, Bjørnstad ON. The importance of temperature fluctuations in understanding mosquito population dynamics and malaria risk. R Soc Open Sci. 2017;4:160969.

    Article  Google Scholar 

  39. Marini F, Caputo B, Pombi M, Tarsitani G, Della Torre A. Study of Aedes albopictus dispersal in Rome, Italy, using sticky traps in mark-release-recapture experiments. Med Vet Entomol. 2010;24:361–8.

    Article  CAS  Google Scholar 

  40. OpenStreetMap. Accessed 6 Aug 2019.

Download references


Not applicable.


This study was partially funded by the Autonomous Province of Trento (Italy), Research funds for Grandi Progetti, Project LExEM (Laboratory of excellence for epidemiology and modelling, The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.

Author information

Authors and Affiliations



AR, GM and RR conceived the experimental design and paper structure. DA and FB carried out laboratory experiments. DA, FB, GC and FM coordinated the mosquito collections and built the original dataset. GM, GG, SM and RR developed the model and designed the in-silico experiments. GM performed model simulations and drafted the manuscript. FB, DA, AR, GC, GG, RR, SM and FM contributed to interpretation and critical review. All authors read and approved the final manuscript.

Corresponding author

Correspondence to Giovanni Marini.

Ethics declarations

Ethics approval and consent to participate

Not applicable.

Consent for publication

Not applicable.

Competing interests

The authors declare that they have no competing interests.

Additional information

Publisher's Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Supplementary information

Additional file 1: Table S1.

Observed Ae. koreicus time series used for model calibration.

Additional file 2: Text S1.

Supporting text containing methodological details and additional results.

Rights and permissions

Open Access This article is distributed under the terms of the Creative Commons Attribution 4.0 International License (, which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. The Creative Commons Public Domain Dedication waiver ( applies to the data made available in this article, unless otherwise stated.

Reprints and permissions

About this article

Check for updates. Verify currency and authenticity via CrossMark

Cite this article

Marini, G., Arnoldi, D., Baldacchino, F. et al. First report of the influence of temperature on the bionomics and population dynamics of Aedes koreicus, a new invasive alien species in Europe. Parasites Vectors 12, 524 (2019).

Download citation

  • Received:

  • Accepted:

  • Published:

  • DOI: