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Mapping the potential distribution of the principal vector of Crimean-Congo haemorrhagic fever virus Hyalomma marginatum in the Old World

  • Seyma S. Celina ,

    Roles Conceptualization, Data curation, Formal analysis, Investigation, Methodology, Resources, Software, Validation, Visualization, Writing – original draft, Writing – review & editing (SSC); (AMS)

    Affiliation Center for Infectious Animal Diseases, Faculty of Tropical AgriSciences, Czech University of Life Sciences Prague, Czech Republic

  • Jiří Černý,

    Roles Conceptualization, Investigation, Project administration, Supervision, Validation, Writing – review & editing

    Affiliation Center for Infectious Animal Diseases, Faculty of Tropical AgriSciences, Czech University of Life Sciences Prague, Czech Republic

  • Abdallah M. Samy

    Roles Conceptualization, Data curation, Formal analysis, Investigation, Methodology, Project administration, Resources, Software, Supervision, Validation, Writing – review & editing (SSC); (AMS)

    Affiliations Entomology Department, Faculty of Science, Ain Shams University, Abbassia, Cairo, Egypt, Medical Ain Shams Research Institute (MASRI), Faculty of Medicine, Ain Shams University, Cairo, Egypt


Crimean-Congo haemorrhagic fever (CCHF) is the most widely distributed tick-borne viral disease in humans and is caused by the Crimean-Congo haemorrhagic fever virus (CCHFV). The virus has a broader distribution, expanding from western China and South Asia to the Middle East, southeast Europe, and Africa. The historical known distribution of the CCHFV vector Hyalomma marginatum in Europe includes most of the Mediterranean and the Balkan countries, Ukraine, and southern Russia. Further expansion of its potential distribution may have occurred in and out of the Mediterranean region. This study updated the distributional map of the principal vector of CCHFV, H. marginatum, in the Old World using an ecological niche modeling approach based on occurrence records from the Global Biodiversity Information Facility (GBIF) and a set of covariates. The model predicted higher suitability of H. marginatum occurrences in diverse regions of Africa and Asia. Furthermore, the model estimated the environmental suitability of H. marginatum across Europe. On a continental scale, the model anticipated a widespread potential distribution encompassing the southern, western, central, and eastern parts of Europe, reaching as far north as the southern regions of Scandinavian countries. The distribution of H. marginatum also covered countries across Central Europe where the species is not autochthonous. All models were statistically robust and performed better than random expectations (p < 0.001). Based on the model results, climatic conditions could hamper the successful overwintering of H. marginatum and their survival as adults in many regions of the Old World. Regular updates of the models are still required to continually assess the areas at risk using up-to-date occurrence and climatic data in present-day and future conditions.

Author summary

Hyalomma marginatum is a vector of numerous highly important human and animal pathogens. It is the principal vector of the Crimean-Congo haemorrhagic fever virus (CCHFV) in Europe. This study updated the potential distribution of H. marginatum in the Old World. The model predicted a high suitability for H. marginatum in diverse regions of Africa, along with broader areas in Asia displaying medium to high suitability. The model predicted widespread potential distributions of H. marginatum on the continental European scale, encompassing southern, western, central, and eastern regions and even extending northward to the south of Scandinavian countries. Hyalomma marginatum populations have not yet been established in any country in Central Europe. However, previous studies have reported sporadic records of the species across all countries within the region. Given the frequent occurrence of immature stages of H. marginatum on migratory birds heading northward to temperate Europe, it is crucial to monitor the northward spread and establishment of permanent populations of this species. Our ecological niche model for Central Europe predicted its distribution across all countries within the region, emphasizing the need for ongoing monitoring and surveillance to detect any potential changes in the distribution and establishment of H. marginatum populations. The current prediction of H. marginatum can contribute to our understanding of the disease risk areas associated with this vector.


Crimean-Congo haemorrhagic fever (CCHF) is the most widely distributed tick-borne viral disease in humans, extending from western China, South Asia, and the Middle East to the southeast of Europe and Africa [1]. CCHF is caused by the Crimean-Congo haemorrhagic fever virus (CCHFV). CCHFV is an emerging arbovirus associated with high fatality rates, reaching up to 40% [14]. CCHFV additionally ranks among the deadliest human pathogens in Africa and Eurasia [5].

Hyalomma marginatum sensu lato is a complex species that includes H. marginatum sensu stricto, Hyalomma rufipes, and other closely related species [6]. In Europe, H. marginatum remains the main vector of CCHFV. Hyalomma marginatum has a veterinary and public health importance, particularly if this species can transmit various tick-borne pathogens in humans and animals other than CCHFV, such as Spotted Fever rickettsia to humans, Anaplasma species to animals, Babesia caballi and Theileria equi (piroplasmosis) to horses, and Theileria annulata (tropical theileriosis) to bovines [710]. This is one of the tick species whose distribution and expansion are closely monitored by the European Center for Disease Prevention and Control (ECDC) because of its major medical importance [11].

Unlike Ixodes ticks which adopt an ambush strategy, H. marginatum actively seeks hosts using an active locomotory hunting strategy [12]. Upon spotting a host by sensing certain signals such as vibration, visual objects, carbon dioxide, ammonia, or body heat, H. marginatum can run rapidly several meters across the ground to attack the host. Therefore, they are known as “hunter ticks”. Hyalomma marginatum demonstrates adaptability to diverse abiotic conditions although it prefers localities with high summer temperatures [13]. As a two-host tick, immature stages feed on the same individual animal (e.g., a small mammal like hares, hedgehogs, and rodents) or a ground-dwelling bird, whereas adults prefer larger hosts such as cattle, horses, or occasionally humans [13]. Large domestic mammals play an important role in the biology of H. marginatum and the transmission of Hyalomma-borne pathogens. These mammals serve as hosts, supporting a high tick load, and consequently bringing H. marginatum into close proximity with agricultural workers. In addition, livestock can directly expose humans to Hyalomma-borne pathogens via infected blood or crushing of engorged ticks on the animals during slaughter [1416]. Moreover, migratory birds may introduce infected H. marginatum to new regions by carrying immature ticks during feeding [13].

Hyalomma marginatum is widely distributed across several African countries, particularly in North Africa and the Sahel region. It can be found in Morocco, Algeria, Tunisia, Libya, Egypt, Sudan, Chad, Ethiopia, Niger, Mali, Mauritania, and Senegal. In addition to Africa, H. marginatum is prevalent in various parts of Asia, including the Middle East, India, and Caucasus. The historical known distribution of H. marginatum in Europe includes most of the Mediterranean and Balkan countries, Ukraine, and southern Russia [6]. Further expansion of its potential distribution may have occurred in and out of the Mediterranean region. The wide dispersal of H. marginatum reflects its tolerance to diverse environments, including savannah, steppe, and scrubland hill and valley biotypes [13].

Hyalomma marginatum was first detected in southern Germany in 2007 in Central Europe [17]. Subsequent observations have confirmed its presence in other central European countries, including Hungary in 2009 [18], Austria in 2018 [19], and the Czech Republic in 2018–2019 [20]. Typically, permanent populations of H. marginatum are limited to warmer areas of the Mediterranean basin in Europe. Permanent populations of H. marginatum in Central Europe likely to have occurred owing to ongoing climatic changes. The establishment of these populations and the northern spread of H. marginatum are possibly anticipated due to the passive transportation of immature stages by migratory birds flying to temperate Europe [21,22]. During the spring migration of birds from the southern to the northern regions, H. marginatum is possibly introduced to Central Europe [2326]. The expansion of H. marginatum into new geographic areas raises concerns about the possible emergence of CCHFV in these novel invaded regions. The distribution of CCHFV is related to the distributional potential of its vector species. The presence of the virus, along with its vectors, reservoirs, and amplifying hosts, play a crucial role in the emergence of CCHF under suitable environmental conditions [27]. Climate change, transportation of immature ticks through international animal trade, and migratory birds significantly impact the distributional potential of H. marginatum by allowing the emergence of CCHF in new geographic regions such as Central Europe. Additionally, socioeconomic factors such as human migration and settlement, as well as increasing human populations, may also influence the emergence of various zoonotic tick-borne diseases [28]. Considering these factors, we hypothesize that several abiotic, biotic, and socioeconomic factors may affect the ability of H. marginatum to colonize European areas. Here, we assess the current potential distribution of H. marginatum, the principal vector of CCHFV, across the Old World, with a specific emphasis on Europe and a particular focus on Central Europe using an ecological niche modeling (ENM) approach. Thus, we aimed to derive detailed predictions to assess the potential invasion of new areas by H. marginatum.

Materials and methods

Occurrence records

The occurrence records of H. marginatum were obtained from the Global Biodiversity Information Facility (GBIF; We meticulously reviewed records for synonymous species of H. marginatum, including Hyalomma plumbeum Panzer, 1795, and Hyalomma savignyi Gervais, 1844, while carefully distinguishing them from Hyalomma rufipes. Only occurrence records corresponding to established populations of H. marginatum were considered in this study. These datasets were subjected to several data cleaning steps; 1) dataset was cleaned by removing duplicate records to reduce possible biases in estimating ecological niche models [29], and 2) occurrence records were filtered based on a distance filter of ≤2.5′ (≈ 5 km) using SDMtoolbox 2.4 [30] in ArcGIS 10.7.1 (Environmental Systems Research Institute (ESRI), Redlands, CA). This distance-based thinning approach retains a single unique record within each pixel, preventing overprediction at specific locations or regions. The dataset was randomly partitioned into two portions using Hawth’s Tools [31] available in ArcGIS 10.7.1: 75% for model calibration, and 25% for internal evaluation of model predictions.

Covariate variables

Several sets of environmental variables were used as independent variables in our model to characterize environmental variations across the calibration and projection areas. These variables were defined as potential drivers that limit the distributional potential of the vector H. marginatum [32]. These variables included satellite data from WorldGrids [33], which represented daytime and nighttime land surface temperature (LST), enhanced vegetation index (EVI), and topographic wetness index (TWI). EVI data was included due to its significant role in shaping the ecological niches of tick vectors, particularly immature stages which live on vegetation [32]. EVI is also considered an important factor in reflecting soil moisture’s availability for larvae and nymphs [34,35]. Humidity and aridity are also important factors, considering their major roles in completing the life cycle of H. marginatum ticks. Effects of abiotic factors such as temperature and humidity on the distribution of H. marginatum have been previously described and used in modeling diverse tick vector species [36,37]. We also used data summarizing climate variables from CHELSA database ( CHELSA data includes 19 bioclimatic variables originally derived from monthly temperature and rainfall values collected from weather stations between 1981–2010 [38]. Bioclimatic variables 8–9 and 18–19 were excluded from the analysis to avoid problems deriving from odd spatial artifacts [39].

Climatic and socioeconomic factors influence tick populations; socioeconomic factors exert indirect effects through human activities and land-use practices. It is noteworthy that tick vectors are not confined to natural habitats alone but have successfully adapted to urban environments. In recent years, urban areas have emerged as significant sites for the expansion of tick-borne diseases within regions where these diseases are endemic [40]. Urban areas have characteristic dense human populations and offer suitable hosts and favorable conditions for tick survival. Several studies conducted in urbanized regions, including Finland, Hungary, Slovakia, Poland, and France, have revealed well-established tick populations and a comparable or even higher prevalence of tick-borne pathogens compared with endemic areas [18,4144]. Human population, migration, and transportation play significant roles in shaping tick distribution worldwide [28]. Higher human density increases the availability of tick hosts, whereas migration introduces ticks and diseases to new regions. Transportation networks additionally facilitate tick movement and allow their invasion into novel areas. To comprehensively examine the interplay among climate, socioeconomic factors, and tick vectors, our model included anthropogenic data. Anthropogenic data consisted of data on human population density from 2015 to 2020, nighttime lights, and accessibility via transportation that may play a role in the distribution of H. marginatum ticks. Population density grids were obtained from the Gridded Population of the World, version 4 (GPWv4) available at [45]. Nighttime satellite imagery was obtained from the NOAA-Defense Meteorological Satellite Program ( and was used as a proxy for poverty estimates [46,47]. Accessibility was summarized in terms of travel time by land or sea [48], as connectivity between population sites is an important variable in estimating the potential distributions of disease vectors and emerging diseases [29,49]. This layer was developed by the European Commission and World Bank ( All environmental and socioeconomic variables were resampled to a spatial resolution of 5 km. The importance of the variables was evaluated using the Jackknife function in Maxent. The final sets of variables used in our analysis were as follows: Set 1 (15 bioclimatic variables from CHELSA); Set 2 (12 variables selected based on Jackknife test in Maxent); Set 3 (a combination of 15 bioclimatic variables and satellite data summarizing daytime and nighttime LST, EVI, TWI, population density, nighttime satellite imagery, and accessibility); and Set 4 (only satellite data summarizing daytime and nighttime LST, EVI, TWI, population density, nighttime satellite imagery, and accessibility) (Table 1).

Table 1. Settings and variables used for the construction of the ecological niche modeling for Hyalomma marginatum.

Accessible area (“M”)

The accessible area “M” is a crucial component of the biotic, abiotic, and movement (BAM) diagram [50]. It defines the key parameters for constructing an ecological niche model for the species in question. Accessible area “M” indicates the areas that the species explored and had access to over relevant periods of the species’ history [51]. The delimitation of the H. marginatum accessible area “M” was estimated using the grinnell package in R [52]. This method simulates dispersal and accessibility based on niche estimations. The grinnell package uses a combination of clean occurrence records of the target species and a set of covariates as inputs to estimate the niche.

Ecological Niche Modeling

We constructed ENM using the maximum entropy algorithm implemented in the kuenm R package [53]. While there are various model algorithms available for estimating niche models, such as generalized linear models (GLM), generalized additive models (GAM), and boosted regression trees (BRT), each designed for different types of distribution data and modeling purposes [54], we selected Maxent because of its efficiency in handling complex interactions between response and predictor variables [55]. A total of 1972 candidate models (i.e., these models refer to the different model configurations or combinations of predictor variables considered during modeling) were built with four distinct sets of environmental and socioeconomic variables. These models were additionally constructed based on parameters reflecting all combinations of 17 regularization multiplier settings (0.1–1 with intervals of 0.1, 2–6 with intervals of 1, and 8 and 10; i.e., these settings determine the level of complexity or smoothness of the model), and 29 possible combinations of 5 feature classes (linear = l, quadratic = q, product = p, threshold = t, and hinge = h).

The best candidate model was selected based on three different criteria: 1) significance, 2) performance, and 3) the Akaike information criteria (AIC): AICc, delta AICc, and AICc weights. Performance was measured using the omission rate, which is a threshold that considers an estimate of the likely amount of error among occurrence data and thus removes 5% of occurrences with the lowest suitability values (E  =  5%) [56]. Models were selected with delta AICc ≤ 2 from those that were statistically significant and had omission rates below 5%. We followed the criteria from the original kuenm study [53] to select and evaluate the final model. We created the final model of H. marginatum using 10 replicates by bootstrap, with logistic, product, and hinge outputs. These models were finally transferred from the accessible area “M” to the projection area “G”.

Extrapolation Risk of H. marginatum

This analysis identified the areas with extrapolation risk based on a mobility-oriented parity (MOP) approach to compare the environmental breadth of predictors within “M” (10% reference points sampled) with that in the projection area. Mobility-oriented parity analysis was performed using the MOP function [57] available in kuenm package in R. The risk of extrapolation analysis calculates multivariate environmental distances between projection area “G” and the nearest portion of the calibration region to identify areas that have a condition of strict or combinational extrapolation.

Independent evaluation

We used a set of additional independent records for the final model evaluation. These records were retrieved from a previous study [32] for additional evaluation of model performance to assess its ability to anticipate risk in unsampled areas. We cleaned the dataset to keep only unique records and double-checked the records to remove any source of overlap with the data used in the model training and testing (i.e., the occurrence records employed in this evaluation differ from those used for model calibration, specifically referring to occurrences distinct from the records obtained from GBIF for model calibration). These records were tested for successful predictions based on a binary model indicating areas where the species was present (suitable) or absent (unsuitable). The continuous model was converted to a binary map based on a threshold value. The threshold value was determined based on a maximum allowable omission error rate of 5%, accounting for potential errors in covariate values within 5% of the occurrences. Subsequently, a one-tailed cumulative binomial probability test was used to assess the probability of obtaining the observed level of correct predictions by chance alone, given the background expectation of correct predictions determined by the proportional coverage of the study area by regions of predicted suitability.


The final dataset used for calibration, derived from GBIF, comprised 95 unique occurrence records after removing duplicated and redundant occurrence records, and the diverse cleaning steps (Fig 1). Of the 1972 candidate models, 1846 models were statistically significant. After applying the three selection criteria, a single model successfully met all requirements and was designated as the best candidate model, as evidenced by its performance (Table 2). The optimal model used Set4 of the satellite data, summarizing daytime and nighttime land surface temperature, EVI, TWI, population density, nighttime light, and accessibility.

Fig 1. Hyalomma marginatum occurrence records used in model calibration and final model evaluation across Europe, North Africa, Western and South-Central Asia.

The blue dotted circles represent the occurrence records of H. marginatum collected from GBIF used for model calibration across the “M” area. The red dotted circles represent the retrieved occurrence records of H. marginatum from the literature used for the final model evaluation. Dark grey polygons represent the accessible areas (“M”) where the H. marginatum model was calibrated. The base layer of all the maps (from Fig 1 to Fig 5) is extracted from ArcGIS Hub developed by ESRI.

Table 2. The best candidate model for the construction of the ecological niche modeling for Hyalomma marginatum.

Model performance under optimal parameters using sets of environmental predictors (SEP), statistically significant models (SSM), best candidate models (BCM), regularization multiplier (RM), features classes (FC), mean Area Under the Curve ratio (AUC.r), partial Receiver Operating Characteristic (p.ROC), omission rate 5% (O.rate 5%), Akaike information criterion corrected (AICc), delta Akaike information criterion corrected (ΔAICc), Akaike information criterion corrected weight (AICc.W), number of parameters (#; summarizes the combination of environmental variables, multiple regularizations, and features other than 0 that provide information for the construction of the model based on lambdas—lambda refers to counting all parameters with a nonzero weight in a Maxent-generated text file), and environmental variables of Set4 tested during calibration of Hyalomma marginatum model.

High to very high suitability of H. marginatum occurrence was observed in various regions of Africa, including the northern parts of North Africa (Morocco, Tunisia, and Egypt), West and East Africa, central parts of Central Africa, and eastern parts of Southern Africa (Fig 2). In Asia, the model indicated medium to high suitability in expansive areas of the continent, encompassing India, Pakistan, Bangladesh, and parts of China (Fig 2).

Fig 2. Predicted potential geographic distribution of Crimean-Congo haemorrhagic fever vector Hyalomma marginatum on a global scale.

Red colors indicate highest habitat suitability and blue lowest suitability. The base layer of all the maps (from Fig 1 to Fig 5) is extracted from ArcGIS Hub developed by ESRI.

On a continental European scale, the model projected a widespread potential distribution of H. marginatum (Fig 3). Thus, the model anticipated the occurrence of H. marginatum in Southern, Western, Central, and Eastern Europe, as far north as the southern parts of Scandinavian countries (Fig 3A). A high probability of suitable conditions for H. marginatum in Southern Europe, especially in the Mediterranean parts of Spain, Portugal, Italy, and Greece and along the Adriatic shore, is presented. In the Balkan Peninsula, the southeastern part of the continent, wide areas of all countries were identified as highly suitable areas for H. marginatum. In Western Europe, large areas of northern and southern France, as well as the Benelux states, were predicted to be highly suitable for the distribution of tick species. Although the Scandinavian countries generally presented low suitability, the model predicted medium to high suitability in the southern regions of most Northern European countries (Sweden, Norway, Denmark, and Finland except Iceland), as well as high suitability in scattered areas in the southern parts of Northern European countries. The northeastern region of Europe primarily demonstrated low and low–medium suitability for H. marginatum distribution, with a few scattered points indicating medium to high suitability in the urban areas of Baltic countries (Estonia, Latvia, and Lithuania). In northwestern Europe, the model depicted medium suitability across all areas in the UK, with very high suitability in specific regions such as the southeast and southwest of England, the East Midlands, the West Midlands, Yorkshire, London, and the southern parts of the northwest and central parts of Northeast England. In Scotland, Ireland, and Northern Ireland, low and low–medium suitability for H. marginatum distribution predominated. Eastern Europe, including Romania, Ukraine, and Moldova, was identified as a highly suitable area, characterized by medium to very high suitability.

Fig 3. Predicted potential distribution of Crimean-Congo haemorrhagic fever vector Hyalomma marginatum on a global scale (left top), and close-ups of Europe (A) and Central Europe (B), to provide additional detail to predictions in the region.

Red areas indicate modeled highest suitable conditions, and blue areas are lowest suitable conditions. The base layer of all the maps (from Fig 1 to Fig 5) is extracted from ArcGIS Hub developed by ESRI.

The ENM of H. marginatum in Central Europe provided insights into its distribution across all countries in the region (Fig 3B). The model indicated broader environmental suitability in Germany, Poland, Hungary, and the Czech Republic, with Austria and Slovakia following suit. Germany exhibited medium to high suitability, with the highest suitability observed in North Rhine Westphalia, Hesse, Saarland, Baden-Württemberg, Bremen, Berlin, Hamburg, and scattered areas in Bavaria, Thuringia, Saxony, and Lower Saxony. The same is true for large parts of Poland and Hungary, particularly the entire city of Budapest, which was identified as a very high suitable habitat for H. marginatum occurrence. High-risk areas occurred in eastern Austria and adjoining areas, and in the western and northern parts of Slovakia. While large areas of the Czech Republic have medium suitability, very high suitability of H. marginatum also occurred in several scattered areas.

The final model was evaluated using independent occurrence data [32], comprising 621 points after eliminating duplicated and redundant records through various cleaning steps. The independent set of H. marginatum occurrence records were related to the H. marginatum model prediction. The model successfully predicted 588 of 621 (94.68%) independent data (Fig 4).

Fig 4. Relationship of Hyalomma marginatum ecological niche modeling prediction to the distribution of the independent set of Hyalomma marginatum occurrence records.

Blue shading shows areas predicted suitable for Hyalomma marginatum occurrences. Black and yellow dots represent the independent records of Hyalomma marginatum used for the final model evaluation; black dots are records with successful prediction and yellow dots are records where the prediction is not captured by the model. The base layer of all the maps (from Fig 1 to Fig 5) is extracted from ArcGIS Hub developed by ESRI.

The MOP results indicated high levels of environmental similarities in all areas under the question, except Southwest China (e.g., northern parts of Tibet province), Northwest China (e.g., southern parts of Xinjiang province), and some areas in East Africa (e.g., Ethiopia, Kenya, Somalia, Sudan) where strict extrapolation occurred (Fig 5). Therefore, predictions on these areas should be taken with caution because they were consistently detected as areas with high extrapolation risk.

Fig 5. Mobility-oriented parity (MOP) 10% extrapolation risk analysis for the ecological niche model of Hyalomma marginatum from the calibration area (“M”) to a projection area (“G”) (top), and close-ups of East Africa (A) and Eastern Asia (B), to provide additional detail to strict extrapolations occurred in the areas.

The MOP analysis indicated that areas with the most dissimilar variables conditions (i.e., where one or more covariate variables are outside the range present in the training data) were found beyond the potential distributional areas predicted by the model in the “G” area. Areas with the most dissimilar variables conditions display strict extrapolative areas and are represented by zero value. Other values represent levels of similarity between the calibration area and the “G” transfer area. The MOP raster output was reclassified into five categories; the first category represented a strict extrapolation (i.e., zero value), and the fifth category represented the highest environmental similarities between calibration and projection areas. The base layer of all the maps (from Fig 1 to Fig 5) is extracted from ArcGIS Hub developed by ESRI.


Ecological niche modeling has been widely implemented to predict the distribution of numerous vector-borne diseases [29,39,5864]. These modeling studies play a crucial role in enhancing the efficiency of vector surveillance and control programs.

In this study, we provided detailed maps to identify the potential distribution of H. marginatum, principal vector of CCHFV, in the Old World, particularly in Europe, with a specific emphasis on Central Europe. This study also addresses model uncertainty under current environmental and socioeconomic conditions. These conditions highlight significant factors influencing the spread of ticks and tick-borne diseases, including climate change, vegetation patterns, human population density, poverty levels, and increased movement of animals and humans due to improved accessibility. The introduction of Hyalomma species to new geographical areas is likely facilitated by infested hosts resulting from human activities, the movement of domesticated and wild mammals, and migratory birds [10,65].

In Europe, H. marginatum is mostly endemic to Mediterranean countries, but isolated populations also exist in Transalpine Europe. Our study revealed extensive areas of high suitability for H. marginatum occurrence across the entire European continent. Specifically, high suitability was observed in the Mediterranean regions of Spain, Portugal, Italy, Greece, and along the Adriatic shore. Furthermore, southern, and northern France, large areas in the Netherlands, Belgium, Germany, Balkan countries, Ukraine, Crimea, scattered areas in Central Europe, and even extending into the United Kingdom remained favorable conditions for the tick species. A previous study anticipated high environmental suitability of H. marginatum in southern, southeast, and Central Europe, as well as regions in North Africa (Tunisia, Morocco, and Algeria), the Arabian Peninsula, south-central Asia, and China [66]. Our model improved the prediction and provided a more reliable and detailed map of habitat suitability for H. marginatum. Similar to the previous ecological niche model [66], the highest environmental suitability for H. marginatum was predicted across Southern Europe. In addition, we observed high suitability across all Balkan countries in southeast Europe. Interestingly, our predictions differed from those of the previous model in several aspects. We identified broader areas of high and very high suitability, particularly in Balkan countries (Albania, Croatia, Bosnia and Herzegovina, Kosovo, Montenegro, Romania, and Slovenia), Western Europe, the United Kingdom, and southern parts of Scandinavia, which were underestimated by Okely and colleagues [66]. This previous study ignored important model settings that can lead to errors in model estimation. In addition to the prediction of Okely and colleagues, previous studies have mapped the geographic distribution of H. marginatum at regional and global scales [67,68]. In comparison with these studies, our model anticipated higher suitability for the occurrence of H. marginatum in Central, Western, Eastern, and Northern Europe, contradicting their predictions of low suitability for this tick species in the same areas.

Hyalomma marginatum was first reported in Central Europe in Germany in 2007 [17]. Although it was recorded in other countries of Central Europe, including Hungary [18], the Czech Republic [20], and Austria [19], these observations did not represent stable populations of H. marginatum in Central Europe. Hyalomma marginatum ticks have ecological plasticity that can support several tolerance ranges to temperature and humidity conditions [69]. This tick species prefers dry and warm regions and is most abundant during summer. In the northern hemisphere, it becomes active in spring when temperatures rise, typically around April [70]. Immature stages are active from June to October, peaking in numbers during July and August. After a blood meal, immature ticks either drop in early summer, molt into adults during the same season, and overwinter as adults, or drop in late summer, overwinter as nymphs, and molt into adults the following spring [70]. Stable populations of H. marginatum in Europe are restricted to the warm areas of the Mediterranean basin and are absent in Central Europe, likely because of unsuitable environmental conditions. However, our model predicted its distribution across all countries in Central Europe and provided strong evidence for extensive medium to very high suitability in Germany, Poland, Hungary, and the Czech Republic, followed by Austria and Slovakia. A recent study conducted in Hungary revealed seropositivity for CCHF, indicating that Hungary could be a novel geographical region for the distribution of CCHFV [71]. Sporadic records of H. marginatum in other central European countries, apart from Hungary, indicate potential breeding habitats for this tick vector. In Austria, the first recorded occurrence of H. marginatum was an adult male tick found on a horse in 2018 [19]. Recent studies in the Czech Republic and Slovakia reported H. marginatum complex species exclusively on migratory birds [72]. In addition, a very recent study reported the collection of five adult H. marginatum ticks from horses and households in the Czech Republic [20]. Although H. marginatum does not belong to the endemic tick fauna in Germany, sporadic findings have been reported recently (e.g., 2007, 2011, 2017, and 2018) [73]. In Poland, records of H. marginatum date back to earlier times, with unfed male ticks reported in 1935 and 1943, which are currently archived in the Bytom Museum collection [74,75]. The introduction of these adult ticks to Central Europe is highly probable because they likely originated as nymphs feeding on migratory birds and molted into adults after becoming fully engorged. The environmental conditions in Central Europe offer suitable habitats for Hyalomma spp. to develop and locate appropriate vertebrate hosts for subsequent blood feeding. While it has been proposed that H. rufipes, another significant vector of CCHFV, overwinters in Central Europe [76], there is currently no speculation regarding the establishment of H. marginatum populations in the region.

Furthermore, our results showed medium to high environmental suitability for H. marginatum in the south of Scandinavia. In Northern Europe, documented records of H. marginatum consist solely of transported immature stages found on migratory birds during their northward spring migration. These records include instances in Denmark in 1939 and 1991 [23,77], Finland in 1962 and between 2018 and 2020 [78,79], Norway in 1994 [23], and Sweden between 1990 and 1991 [23]. Although no scientific study has reported the occurrence of H. marginatum in Norway since 1994, Hasle et al. [80] reported the presence of seven fully engorged nymphs of H. rufipes in migratory birds captured during 2003–2005. Recently, the first sightings of adult H. marginatum ticks have been documented on horses, cattle, and humans in Sweden [81]. The rapidly changing climate in Northern Europe appears to create favorable conditions for the development of immature stages of this tick species, carried by migratory birds, to reach the adult stage and potentially attach and feed on large mammals, including humans.

Appropriate climatic and biotic conditions in the regions that are depicted in our maps may provide a suitable environment for introduced H. marginatum ticks. A warming climate trend could enhance the persistence of infected H. marginatum ticks. The expansion of suitable areas has been documented in Central Europe [82]. Thus, it is possible to hypothesize that climate change may potentially lead to an increase in winter temperatures, leading to an increase in the probability of H. marginatum overwintering, and subsequently raising the risk of its establishment in various parts of central European countries. Therefore, modeling studies based on future scenarios should be implemented to better understand the impact of climate change on the dispersion of H. marginatum.

ENM results are valuable for understanding species tolerance to biotic and abiotic factors. When combined with knowledge of ecology, behaviour, and life history, they assist in selecting the most realistic predictions [83]. Our current global potential distribution prediction for this tick vector can provide insights into disease risk areas associated with this vector. However, it is essential to assess the uncertainty in model projections, particularly for decision-makers in vector and disease surveillance and public health. CCHFV, a vector-borne pathogen, requires a “One Health” approach that requires a multidisciplinary perspective encompassing animal, human, and environmental health [84]. Therefore, it is crucial to develop effective control strategies that address emerging Hyalomma-borne diseases within the framework of a “One Health” perspective, where a rapidly changing environment and animal health may impact human health.

In this study, we used a novel improved methodology and allowed different modeling settings to construct the habitat suitability model for H. marginatum based on calibration and evaluation of our models using several updated variables that previously were not used. Although our continental-scale predictions provide valuable insights into the distribution of H. marginatum, it is crucial to investigate the species’ interactions with microclimate and the influence of host availability on its response to prevailing climatic conditions [85].

The model effectively identified known areas where the disease is prevalent, but it has a few limitations. Notably, the abundance of occurrence records in Europe and the Indian subcontinent has probably led to wider predictions, particularly in urban areas and transportation routes. It is noteworthy to mention that human-modified landscapes, such as urban areas, have gained attention as potential habitats for ticks, contrary to the belief that they are restricted to natural habitats. Studies conducted across Europe have revealed the successful establishment of tick populations in urban areas, and the spread of tick-borne diseases has been linked to these urban hotspots [18,4144]. The tick ability to thrive in urban environments emphasizes the significance of considering urban areas as potential hubs for tick populations.

Furthermore, areas with a low number of occurrence records driven by accessibility bias should be further investigated, especially if the model predicts a high suitability habitat for H. marginatum. However, it is essential to distinguish between two key aspects: 1) occurrence records, which represent sampling efforts in specific areas influenced by factors such as tick identification expertise or the need for intensive fieldwork to study tick-borne disease circulation, and 2) model predictions generated by applying algorithms to thinned occurrence records and covariate data. Occurrence records indicated the presence or absence of the species within the sampled areas, whereas the model provided probability values indicating pixel suitability for species presence. This pattern enables the assessment of tick suitability in unsampled areas based on available occurrence records and covariate information, which poses a significant challenge in ecological niche modeling. To ensure reliable predictions, our model underwent careful calibration, and necessary adjustments were implemented to avoid over-prediction. Host parameters were not incorporated into the model because the species’ broad host range encompassed numerous vertebrate species. Incorporating host species data poses challenges because obtaining reliable occurrence information for multiple hosts is difficult, and the optimal approach to their inclusion remains unclear [36]. Nevertheless, although H. marginatum is a generalist species, certain vertebrate hosts may be preferred within its extensive range of potential hosts [86]. However, caution should be exercised when interpreting these host preferences as they may vary across different regions [87]. Finally, the Maxent algorithm used in ecological niche modeling has a few limitations, including reliance on presence-only data that can introduce biases, potential overfitting with complex predictor variables, the risk of unreliable results when extrapolating beyond calibrated conditions, limited mechanistic understanding and sensitivity to variable selection, and the impact of spatial autocorrelation and the assumption of independence on model performance. Considering these limitations is essential when using this model.

In summary, our future studies will consider further detailed mapping of CCHF disease and H. marginatum distribution under different climate change scenarios. In addition to mapping the distribution of this tick species under different future projections, our understanding of the dynamics of the host–tick vector–virus system will be improved by further modeling studies that incorporate the effects of vertebrate hosts (different types of hosts, seasonality, and movements) as well as life traits of the tick species.


The authors would like to thank all the resources and support provided by the Ain Shams University Disease Ecology and Dynamic Laboratory and the Ain Shams University Medical Research Institute (MASRI) and the Department of Entomology.


  1. 1. Bente DA, Forrester NL, Watts DM, McAuley AJ, Whitehouse CA, Bray M. Crimean-Congo hemorrhagic fever: History, epidemiology, pathogenesis, clinical syndrome and genetic diversity. Antiviral Res. 2013;100: 159–189. pmid:23906741
  2. 2. Ergönül Ö. Crimean-Congo haemorrhagic fever. Lancet Infect Dis. 2006;6: 203–214. pmid:16554245
  3. 3. Whitehouse C. Crimean Congo hemorrhagic fever. Antiviral Res. 2004;64: 145–160. pmid:15550268
  4. 4. Yilmaz GR, Buzgan T, Irmak H, Safran A, Uzun R, Cevik MA, et al. The epidemiology of Crimean-Congo hemorrhagic fever in Turkey, 2002–2007. International Journal of Infectious Diseases. 2009;13: 380–386. pmid:18986819
  5. 5. Shayan S, Bokaean M, Shahrivar MR, Chinikar S. Crimean-Congo Hemorrhagic Fever. Lab Med. 2015;46: 180–189. pmid:26199256
  6. 6. Apanaskevich DA, Horak IG. The genus Hyalomma Koch, 1844: v. re-evaluation of the taxonomic rank of taxa comprising the H. (Euhyalomma) marginatum koch complex of species (Acari: Ixodidae) with redescription of all parasitic stages and notes on biology. Int J Acarol. 2008;34: 13–42.
  7. 7. Bakheit MA, Latif AA, Vatansever Z, Seitzer U, Ahmed J. The Huge Risks Due to Hyalomma Ticks. 2012. pp. 167–194.
  8. 8. Wallménius K, Pettersson JH-O, Jaenson TGT, Nilsson K. Prevalence of Rickettsia spp., Anaplasma phagocytophilum, and Coxiella burnetii in adult Ixodes ricinus ticks from 29 study areas in central and southern Sweden. Ticks Tick Borne Dis. 2012;3: 100–106. pmid:22487426
  9. 9. Tirosh-Levy S, Mazuz ML, Savitsky I, Pinkas D, Gottlieb Y, Steinman A. Serological and Molecular Prevalence of Babesia caballi in Apparently Healthy Horses in Israel. Pathogens. 2021;10: 445. pmid:33917822
  10. 10. EFSA (The European Food Safety Authority). Scientific Opinion on the Role of Tick Vectors in the Epidemiology of Crimean-Congo Hemorrhagic Fever and African Swine Fever in Eurasia. EFSA Journal. 2010;8: 1703.
  11. 11. ECDC (European Centre for Disease Prevention and Control). Hyalomma marginatum—current known distribution: March 2023. Available online: (accessed on June 2023).
  12. 12. Sonenshine DE, Roe RM. Book review: Sonenshine D.E.; Roe R.M. 2013: Biology of Ticks. 2nd ed. Eur J Entomol. 2015;112.
  13. 13. Hoogstraal H. Review Article: The Epidemiology of Tick-Borne Crimean-Congo Hemorrhagic Fever in Asia, Europe, and Africa. J Med Entomol. 1979;15: 307–417.
  14. 14. Chinikar S, Ghiasi SM, Moradi M, Goya MM, Shirzadi MR, Zeinali M, et al. Geographical Distribution and Surveillance of Crimean-Congo Hemorrhagic Fever in Iran. Vector-Borne and Zoonotic Diseases. 2010;10: 705–708. pmid:20854025
  15. 15. Sargianou M, Panos G, Tsatsaris A, Gogos C, Papa A. Crimean-Congo hemorrhagic fever: seroprevalence and risk factors among humans in Achaia, western Greece. International Journal of Infectious Diseases. 2013;17: e1160–e1165. pmid:24084247
  16. 16. Mustafa ML, Ayazi E, Mohareb E, Yingst S, Zayed A, Rossi CA, et al. Crimean-Congo Hemorrhagic Fever, Afghanistan, 2009. Emerg Infect Dis. 2011;17: 1940–1941. pmid:22000377
  17. 17. Kampen H, Poltz W, Hartelt K, Wölfel R, Faulde M. Detection of a questing Hyalomma marginatum marginatum adult female (Acari, Ixodidae) in southern Germany. Exp Appl Acarol. 2007;43: 227–231. pmid:17952610
  18. 18. Földvári G, Rigó K, Jablonszky M, Biró N, Majoros G, Molnár V, et al. Ticks and the city: Ectoparasites of the Northern white-breasted hedgehog (Erinaceus roumanicus) in an urban park. Ticks Tick Borne Dis. 2011;2: 231–234. pmid:22108019
  19. 19. Duscher GG, Hodžić A, Hufnagl P, Wille-Piazzai W, Schötta A-M, Markowicz MA, et al. Adult Hyalomma marginatum tick positive for Rickettsia aeschlimannii in Austria, October 2018. Eurosurveillance. 2018;23. pmid:30621821
  20. 20. Lesiczka PM, Daněk O, Modrý D, Hrazdilová K, Votýpka J, Zurek L. A new report of adult Hyalomma marginatum and Hyalomma rufipes in the Czech Republic. Ticks Tick Borne Dis. 2022;13: 101894. pmid:34996002
  21. 21. Hoogstraal H, Kaiser MN, Traylor MA, Gaber S, Guindy E. Ticks (Ixodoidea) on birds migrating from Africa to Europe and Asia. Bull World Health Organ. 1961;24: 197–212. pmid:13715709
  22. 22. Hillyard PD. Ticks of North-West Europe: keys and notes for identification of the species. London: The Linnean Society of London; 1996.
  23. 23. Jaenson TGT, TäLleklint L, Lundqvist L, Olsen B, Chirico J, Mejlon H. Geographical Distribution, Host Associations, and Vector Roles of Ticks (Acari: Ixodidae, Argasidae) in Sweden. J Med Entomol. 1994;31: 240–256. pmid:8189415
  24. 24. Jameson LJ, Morgan PJ, Medlock JM, Watola G, Vaux AGC. Importation of Hyalomma marginatum, vector of Crimean-Congo haemorrhagic fever virus, into the United Kingdom by migratory birds. Ticks Tick Borne Dis. 2012;3: 95–99. pmid:22300969
  25. 25. Hornok S, Flaisz B, Takács N, Kontschán J, Csörgő T, Csipak Á, et al. Bird ticks in Hungary reflect western, southern, eastern flyway connections and two genetic lineages of Ixodes frontalis and Haemaphysalis concinna. Parasit Vectors. 2016;9: 101. pmid:26912331
  26. 26. Hubálek Z, Sedláček P, Estrada-Peña A, Vojtíšek J, Rudolf I. First record of Hyalomma rufipes in the Czech Republic, with a review of relevant cases in other parts of Europe. Ticks Tick Borne Dis. 2020;11: 101421. pmid:32360146
  27. 27. Portillo A, Palomar AM, Santibáñez P, Oteo JA. Epidemiological Aspects of Crimean-Congo Hemorrhagic Fever in Western Europe: What about the Future? Microorganisms. 2021;9: 649. pmid:33801015
  28. 28. Gray JS, Dautel H, Estrada-Peña A, Kahl O, Lindgren E. Effects of Climate Change on Ticks and Tick-Borne Diseases in Europe. Interdiscip Perspect Infect Dis. 2009;2009: 1–12. pmid:19277106
  29. 29. Samy AM, Thomas SM, Abd El Wahed A, Cohoon KP, Peterson AT. Mapping the global geographic potential of Zika virus spread. Mem Inst Oswaldo Cruz. 2016;111: 559–560. pmid:27653360
  30. 30. Brown JL, Bennett JR, French CM. SDMtoolbox 2.0: the next generation Python-based GIS toolkit for landscape genetic, biogeographic and species distribution model analyses. PeerJ. 2017;5. pmid:29230356
  31. 31. Beyer HL. Hawth’s analysis tools for ArcGIS.; 2004.
  32. 32. Estrada-Peña A, Alexander N, Wint GRW. Perspectives on modelling the distribution of ticks for large areas: so far so good? Parasit Vectors. 2016;9: 179. pmid:27030357
  33. 33. a repository of global soil covariates. Available at:
  34. 34. Randolph SE. Ticks and tick-borne disease systems in space and from space. 2000. pp. 217–243.
  35. 35. Guerra M. Predicting the Risk of Lyme Disease: Habitat Suitability for Ixodes scapularis in the North Central United States. Emerg Infect Dis. 2002;8: 289–297. pmid:11927027
  36. 36. Alkishe A, Raghavan RK, Peterson AT. Likely Geographic Distributional Shifts among Medically Important Tick Species and Tick-Associated Diseases under Climate Change in North America: A Review. Insects. 2021;12.
  37. 37. Estrada-Peña A, Vatansever Z, Gargili A, Ergönül Ö. The trend towards habitat fragmentation is the key factor driving the spread of Crimean-Congo haemorrhagic fever. Epidemiol Infect. 2010;138: 1194–1203. pmid:19878611
  38. 38. Karger DN, Nobis MP, Normand S, Graham CH, Zimmermann NE. CHELSA-TraCE21k v1.0. Downscaled transient temperature and precipitation data since the last glacial maximum. Climate of the Past Discussions. 2021;2021: 1–27.
  39. 39. Samy AM, Peterson AT. Climate Change Influences on the Global Potential Distribution of Bluetongue Virus. PLoS One. 2016;11: e0150489. pmid:26959424
  40. 40. VanAcker MC, Little EAH, Molaei G, Bajwa WI, Diuk-Wasser MA. Enhancement of Risk for Lyme Disease by Landscape Connectivity, New York, New York, USA. Emerg Infect Dis. 2019;25: 1136–1143. pmid:31107213
  41. 41. Klemola T, Sormunen JJ, Mojzer J, Mäkelä S, Vesterinen EJ. High tick abundance and diversity of tick-borne pathogens in a Finnish city. Urban Ecosyst. 2019;22: 817–826.
  42. 42. Paul REL, Cote M, Le Naour E, Bonnet SI. Environmental factors influencing tick densities over seven years in a French suburban forest. Parasit Vectors. 2016;9: 309. pmid:27234215
  43. 43. Pangrácová L, Derdáková M, Pekárik L, Hviščová I, Víchová B, Stanko M, et al. Ixodes ricinus abundance and its infection with the tick-borne pathogens in urban and suburban areas of Eastern Slovakia. Parasit Vectors. 2013;6: 238. pmid:23952975
  44. 44. Kowalec M, Szewczyk T, Welc-Falęciak R, Siński E, Karbowiak G, Bajer A. Ticks and the city—are there any differences between city parks and natural forests in terms of tick abundance and prevalence of spirochaetes? Parasit Vectors. 2017;10: 573. pmid:29157278
  45. 45. Warszawski L, Frieler K, Huber V, Piontek F, Serdeczny O, Zhang X, et al. Center for International Earth Science Information Network—CIESIN—Columbia University (2016). Gridded population of the World, Version 4 (GPWv4): Population density. Palisades. NY: NASA Socioeconomic Data and Applications Center (SEDAC). Atlas of Environmental Risks Facing China Under Climate Change. 2017; 228.
  46. 46. Noor AM, Alegana VA, Gething PW, Tatem AJ, Snow RW. Using remotely sensed night-time light as a proxy for poverty in Africa. Popul Health Metr. 2008;6: 5. pmid:18939972
  47. 47. Wang W, Cheng H, Zhang L. Poverty assessment using DMSP/OLS night-time light satellite imagery at a provincial scale in China. Advances in Space Research. 2012;49: 1253–1264.
  48. 48. Nelson A. Travel Time to Major Cities: A Global Map of Accessibility. In: Global Environment Monitoring Unit-Joint Research Centre of the European Commission, Ispra Italy. Jan 2008.
  49. 49. Time Cliff A., travel and infection. Br Med Bull. 2004;69: 87–99.
  50. 50. Soberon Jorge, Peterson A Townsend. Interpretation of Models of Fundamental Ecological Niches and Species’ Distributional Areas. Biodiversity Informatics. 2005;2.
  51. 51. Barve N, Barve V, Jiménez-Valverde A, Lira-Noriega A, Maher SP, Peterson AT, et al. The crucial role of the accessible area in ecological niche modeling and species distribution modeling. Ecol Modell. 2011;222: 1810–1819.
  52. 52. Machado-Stredel F, Cobos ME, Peterson AT. A simulation-based method for selecting calibration areas for ecological niche models and species distribution models. Front Biogeogr. 2021;13.
  53. 53. Cobos ME, Peterson AT, Barve N, Osorio-Olvera L. kuenm: an R package for detailed development of ecological niche models using Maxent. PeerJ. 2019;7: e6281. pmid:30755826
  54. 54. Samy AM, Yáñez-Arenas C, Jaeschke A, Cheng Y, Thomas SM. Modeling Distributional Potential of Infectious Diseases. Geospatial Technology for Human Well-Being and Health. Cham: Springer International Publishing; 2022. pp. 337–353.
  55. 55. Elith J, Phillips SJ, Hastie T, Dudík M, Chee YE, Yates CJ. A statistical explanation of MaxEnt for ecologists. Divers Distrib. 2011;17: 43–57.
  56. 56. Peterson AT, Soberón J, Pearson RG, Anderson RP, Martínez-Meyer E, Nakamura M, et al. Ecological Niches and Geographic Distributions (MPB-49). Princeton University Press; 2011.
  57. 57. Owens HL, Campbell LP, Dornak LL, Saupe EE, Barve N, Soberón J, et al. Constraints on interpretation of ecological niche models by limited environmental ranges on calibration areas. Ecol Modell. 2013;263: 10–18.
  58. 58. Adjemian JCZ, Girvetz EH, Beckett L, Foley JE. Analysis of Genetic Algorithm for Rule-Set Production (GARP) Modeling Approach for Predicting Distributions of Fleas Implicated as Vectors of Plague, Yersinia pestis, in California. J Med Entomol. 2006;43: 93–103. pmid:16506453
  59. 59. Staples JE, Breiman RF, Powers AM. Chikungunya Fever: An Epidemiological Review of a Re-Emerging Infectious Disease. Clinical Infectious Diseases. 2009;49: 942–948. pmid:19663604
  60. 60. Khatchikan C, Sangermano F, Kendell D, Lidvahl T. Evaluation of species distribution model algorithms for fine-scale container-breeding mosquito risk prediction. Med Vet Entomol. 2011;25: 268–275. pmid:21198711
  61. 61. Donalisio MR, Souza CE, Angerami RN, Samy AM. Mapping Brazilian spotted fever: Linking etiological agent, vectors, and hosts. Acta Trop. 2020;207: 105496. pmid:32315604
  62. 62. Lin S, DeVisser MH, Messina JP. An agent-based model to simulate tsetse fly distribution and control techniques: A case study in Nguruman, Kenya. Ecol Modell. 2015;314: 80–89.
  63. 63. Samy AM, Elaagip AH, Kenawy MA, Ayres CFJ, Peterson AT, Soliman DE. Climate Change Influences on the Global Potential Distribution of the Mosquito Culex quinquefasciatus, Vector of West Nile Virus and Lymphatic Filariasis. PLoS One. 2016;11: e0163863. pmid:27695107
  64. 64. Samy AM, Alkishe AA, Thomas SM, Wang Liya, Zhang Wenyi. Mapping the potential distributions of etiological agent, vectors, and reservoirs of Japanese Encephalitis in Asia and Australia. Acta Trop. 2018;188: 108–117.
  65. 65. Valcárcel F, González J, González MG, Sánchez M, Tercero JM, Elhachimi L, et al. Comparative Ecology of Hyalomma lusitanicum and Hyalomma marginatum Koch, 1844 (Acarina: Ixodidae). Insects. 2020;11: 303. pmid:32414220
  66. 66. Okely M, Anan R, Gad-Allah S, Samy AM. Mapping the environmental suitability of etiological agent and tick vectors of Crimean-Congo hemorrhagic fever. Acta Trop. 2020;203: 105319. pmid:31874130
  67. 67. Estrada-Peña A, de la Fuente J, Latapia T, Ortega C. The Impact of Climate Trends on a Tick Affecting Public Health: A Retrospective Modeling Approach for Hyalomma marginatum (Ixodidae). PLoS One. 2015;10: e0125760. pmid:25955315
  68. 68. Williams HW, Cross DE, Crump HL, Drost CJ, Thomas CJ. Climate suitability for European ticks: assessing species distribution models against null models and projection under AR5 climate. Parasit Vectors. 2015;8: 440. pmid:26310856
  69. 69. Bouattour A, Darghouth M, Darghouth M. Distribution and ecology of ticks (Acari: Ixodidae) infesting livestock in Tunisia: an overview of eighth years field collections. Parassitologia. 1999;41.
  70. 70. ECDC (European Centre for Disease Prevention and Control) (Available at: Hyalomma marginatum—Factsheet for experts.
  71. 71. Magyar N, Kis Z, Barabás É, Nagy A, Henczkó J, Damjanova I, et al. New geographical area on the map of Crimean-Congo hemorrhagic fever virus: First serological evidence in the Hungarian population. Ticks Tick Borne Dis. 2021;12: 101555. pmid:33022559
  72. 72. Capek M, Literak I, Kocianova E, Sychra O, Najer T, Trnka A, et al. Ticks of the Hyalomma marginatum complex transported by migratory birds into Central Europe. Ticks Tick Borne Dis. 2014;5: 489–493. pmid:24877976
  73. 73. Chitimia-Dobler L, Schaper S, Rieß R, Bitterwolf K, Frangoulidis D, Bestehorn M, et al. Imported Hyalomma ticks in Germany in 2018. Parasit Vectors. 2019;12: 134. pmid:30909964
  74. 74. Siuda K, Dutkiewicz J. Hyalomma marginatum Koch, 1844 (Acarina: Ixodidae) in Poland—an example of transport of southern tick by migratory birds. Wiad Parazytol. 1979;25: 333–8.
  75. 75. Magdalena Nowak-Chmura, Wojciech Solarz. A new case of transfer to Poland of the tick Hyalomma (Euhyalomma) marginatum Koch, 1844 (Acari: Amblyommidae) on migratory birds. Puławy, Poland: Abstracts of XXII Congress of Polish Parasitological Society; 2010.
  76. 76. Rudolf I, Kejíková R, Vojtíšek J, Mendel J, Peňázziová K, Hubálek Z, et al. Probable overwintering of adult Hyalomma rufipes in Central Europe. Ticks Tick Borne Dis. 2021;12: 101718. pmid:33857747
  77. 77. Johnsen P. Hyalomma marginatum Koch, a tick new to Denmark. Entomol Med. 1943;22: 381–383.
  78. 78. Nuorteva P, Hoogstraal H. The incidence of ticks (Ixodoidea, Ixodidae) on migratory birds arriving in Finland during the spring of 1962. Ann Med exp Fenn. 1963;41.
  79. 79. Sormunen JJ, Klemola T, Vesterinen EJ. Ticks (Acari: Ixodidae) parasitizing migrating and local breeding birds in Finland. Exp Appl Acarol. 2022;86: 145–156. pmid:34787774
  80. 80. Hasle G, Bjune G, Edvardsen E, Jakobsen C, Linnehol B, Røer JE, et al. Transport of Ticks by Migratory Passerine Birds to Norway. Journal of Parasitology. 2009;95: 1342–1351. pmid:19658452
  81. 81. Grandi G, Chitimia-Dobler L, Choklikitumnuey P, Strube C, Springer A, Albihn A, et al. First records of adult Hyalomma marginatum and H. rufipes ticks (Acari: Ixodidae) in Sweden. Ticks Tick Borne Dis. 2020;11: 101403.
  82. 82. Fernández-Ruiz N, Estrada-Peña A. Towards New Horizons: Climate Trends in Europe Increase the Environmental Suitability for Permanent Populations of Hyalomma marginatum (Ixodidae). Pathogens. 2021;10: 95. pmid:33494140
  83. 83. Escobar LE, Craft ME. Advances and Limitations of Disease Biogeography Using Ecological Niche Modeling. Front Microbiol. 2016;07. pmid:27547199
  84. 84. Mackenzie JS, Jeggo M. The One Health Approach—Why Is It So Important? Trop Med Infect Dis. 2019;4: 88. pmid:31159338
  85. 85. Estrada-Peña A, de la Fuente J. The ecology of ticks and epidemiology of tick-borne viral diseases. Antiviral Res. 2014;108: 104–128. pmid:24925264
  86. 86. Grech-Angelini S, Stachurski F, Lancelot R, Boissier J, Allienne J-F, Marco S, et al. Ticks (Acari: Ixodidae) infesting cattle and some other domestic and wild hosts on the French Mediterranean island of Corsica. Parasit Vectors. 2016;9: 582. pmid:27842608
  87. 87. McCoy KD, Léger E, Dietrich M. Host specialization in ticks and transmission of tick-borne diseases: a review. Front Cell Infect Microbiol. 2013;3.