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. 2023 Oct 5;28(40):2200844. doi: 10.2807/1560-7917.ES.2023.28.40.2200844

West Nile virus in the Iberian Peninsula: using equine cases to identify high-risk areas for humans

José-María García-Carrasco 1, Antonio-Román Muñoz 1, Jesús Olivero 1, Marina Segura 2, Ignacio García-Bocanegra 3, Raimundo Real 1
PMCID: PMC10557382  PMID: 37796440

Abstract

Background

West Nile virus (WNV) is a flavivirus with an enzootic cycle between birds and mosquitoes; humans and horses are incidental dead-end hosts. In 2020, the largest outbreak of West Nile virus infection in the Iberian Peninsula occurred, with 141 clusters in horses and 77 human cases.

Aim

We analysed which drivers influence spillover from the cycle to humans and equines and identified areas at risk for WNV transmission.

Methods

Based on data on WNV cases in horses and humans in 2020 in Portugal and Spain, we developed logistic regression models using environmental and anthropic variables to highlight risk areas. Models were adapted to a high-resolution risk map.

Results

Cases of WNV in horses could be used as indicators of viral activity and thus predict cases in humans. The risk map of horses was able to define high-risk areas for previous cases in humans and equines in Portugal and Spain, as well as predict human and horse cases in the transmission seasons of 2021 and 2022. We found that the spatial patterns of the favourable areas for outbreaks correspond to the main hydrographic basins of the Iberian Peninsula, jointly affecting Portugal and Spain.

Conclusion

A risk map highlighting the risk areas for potential future cases could be cost-effective as a means of promoting preventive measures to decrease incidence of WNV infection in Europe, based on a One Health surveillance approach.

Keywords: Distribution models, Favourability, Horse, One Health, Pathogeography, Prediction, Risk map, West Nile virus, Zoonoses


Key public health message.

What did you want to address in this study?

West Nile fever is a viral infection transmitted to humans and other animals via mosquitoes. Infections of West Nile virus are increasing in Europe and the disease has a considerable impact on human and animal health. We wished to explore the environmental conditions that influence the transmission of the virus to humans and horses and test the role of horses as indicators of the disease in humans.

What have we learnt from this study?

Data on West Nile virus infection in horses can be useful indicators of risks of human cases. In addition, river basins play an important role as places where outbreaks occur and spread.

What are the implications of your findings for public health?

Horses can be used as part of an integrated surveillance system focused on reducing the number of people and animals infected with the virus. Decision-making would be more efficient using river basins as management units, instead of political administrative units, for example to alert the health facilities after infected horses have been detected.

Introduction

West Nile virus (WNV) is a mosquito-borne arbovirus of the family Flaviviridae [1]. The virus is mainly transmitted from birds to mammals by blood-feeding ornithophilic mosquito species. Humans and equines are the main dead-end hosts: in humans, the virus may cause symptoms from febrile illness to neuroinvasive disease, although the latter occurs in less than 1% of cases [2]. Although the virus has been circulating in Europe since 1950, it was not until 2004 that Spain detected the first human case of West Nile neuroinvasive disease [3]. The same year, Portugal confirmed two cases of WNV infection in humans [4]. In 2010, Europe experienced the first large outbreak with 391 cases, and the same year, Spain had its first outbreak among equines and humans [5,6] and Portugal confirmed one human and two equine cases [7]. From 2011 to 2019, WNV activity was low but endemic in the Iberian Peninsula, with few outbreaks in equids and humans reported [5,8,9]. In the Iberian Peninsula, the largest outbreak to date occurred in 2020, affecting new regions. A total of 77 human cases were detected, including eight deaths [8,10]. Moreover, 141 clusters of WNV infection in horses occurred in the peninsula [9].

Equines are particularly sensitive to WNV infection. In horses, neurological disorders are more common than in humans [11]. Neurological symptoms of WNV infection in equines may include recumbency, cranial nerve deficits, muscular tremors, ataxia, hyperesthesia, fasciculations, convulsions, paralysis of the limbs, photophobia, vacuum chewing, disorientation, behavioural changes and tetany [12-15]. As WNV infection in equids is often symptomatic, horses, donkeys and mules could be useful identifiers of risk of virus circulation and the possibility of human infections and disease in areas with cases in equids [16]. Also, bird species of the family Corvidae can be used as sentinels for WNV detection, as the infection may result in high mortality in birds [17,18]. Indicator species for risk could be useful if there is a time window to implement control programmes to protect surrounding human communities.

Based on data of 77 human cases and 141 clusters in horses notified in the 2020 season, we aimed to analyse the geographical distribution of cases of WNV infection in horses and humans and create a risk map of the Iberian Peninsula to visualise environmental and spatial patterns from a macroecological perspective. We wanted to test if equine WNV infection cases could predict risk areas for human cases, which could be useful to implement early warning mechanisms, improve planning of surveillance measures and develop prevention policies in at-risk areas before outbreaks occur.

Methods

Data source and setting

Spain and Portugal report cases of WNV infection in humans to the European Surveillance System (TESSy) operated by the European Centre for Disease Prevention and Control (ECDC). We listed all areas in Spain and Portugal where cases of WNV infection in horses and humans occurred during the transmission season of 2020. We used cases that were detected during passive and active surveillance: clinical cases that were serologically positive (IgM) or with the virus identified using reverse transcription (RT) [19]. For data on humans, we used the 2020 data in TESSy [20]. In Europe, case locations are reported at the NUTS (Nomenclature of Territorial Units for Statistics) level 3 [21]. However, to achieve the highest possible accuracy of the geographical location of the cases, we compared the EU data with the data collected by the National Epidemiological Surveillance Network and the Coordinating Centre of Health Alerts and Emergencies (CCAES) [22,23]. Information on findings of WNV in horses in Spain and Portugal were obtained from the Veterinary Health Alert Risk system (RASVE), developed by the Spanish Ministry of Agriculture, Fisheries and Food. This system integrates health data from national and international sources, such as the Animal Disease Information System (ADIS) [24]. The outbreak data were retrieved in February 2022 and location of the outbreaks, in humans and horses, was georeferenced at the municipal level in Spain and at the parish level in Portugal. Municipalities had an average surface area of approximately 60 km2, while the average surface area of parishes was approximately 20 km2. For the modelling, municipalities and parishes were considered the operational geographic units (OGUs) in the Iberian Peninsula.

Risk models

We elaborated separate risk models for cases of WNV infection in horses and in humans. First, using univariate score tests for the presence or absence of cases of WNV infection, we assessed the capacity of different environmental variables to explain the distribution of cases. Variables were selected on the basis of their potential predictive power and were assumed to be at least correlated with more proximal causal factors. Mosquito data were not available, therefore we used water availability and temperature as proxies of mosquito presence. The variables used comprised different factors, such as density of the human and animal population, distance to roads, production of crops, forests, river, altitude and precipitation. A list of all factors considered can be seen in the Supplementary table.

We controlled multicollinearity among variables by calculating pairwise Spearman correlation coefficients. If two variables belonging to the same factor were correlated by more than 0.8, the least explanatory variable, according to the score tests, was deleted. Moreover, we controlled the false discovery rate to avoid an increase in type I errors due to the number of variables used in the analysis [25]. Therefore, we organised the variables by importance and arranged them in descending order to better understand their influence on the occurrence of WNV infection. To determine their significance, we relied on the Rao score test [26]. To be included in subsequent steps, a variable must have a score-test probability below i*q/V, where i represents the variable's position in the order, q is the false discovery rate of 0.05, and V is the total number of variables. Consequently, we performed a multivariate forward stepwise logistic regression in which a variable was added to the null model if the resulting regression was most significantly improved by the new variable. A machine-learning algorithm, using maximum likelihood estimation, established the values of the parameters for the logistic regression. The result was a probability value of cases of WNV infection in each OGU according to its environmental and anthropic characteristics. The probability value of each OGU was transformed into a favourability value (F) using the favourability function [27]. The favourability value (ranging from 0 to 1) was calculated for each OGU, which represents the degree to which environmental conditions at that OGU favour the occurrence of WNV infection. The favourability model shows how the local probability of WNV cases differs from that expected by chance in the Iberian Peninsula and thus identifies localities with environmental conditions that favour infection with the virus. This was used for the elaboration of a risk map for cases of WNV infection in horses and humans.

Relationship between cases in horses and humans

We evaluated the classification and discrimination capacity of the horse and human risk model. The classification power of the models, using a value of F = 0.5 as classification threshold, was estimated using the sensitivity, specificity, Cohen’s kappa and correct classification rate (CCR) [28] and the over- and under-prediction rates [29]. In contrast, the discrimination power was assessed using the area under the receiver operating characteristic curve (AUC) [30]. As we also wanted to test whether there was a relationship between cases in horses and humans, we tested each model with the alternative cases, that is, the horse model was evaluated with respect to the distribution of human cases, and the human model was evaluated with the distribution of cases in horses. In this way, we could test how useful it would be to use the distribution of cases in horses to predict risk for humans, and vice versa.

Downscaling the risk models

To increase the potential utility of the cartographic model, we downscaled the model from its original OGU (municipalities or parishes) to 4 km2 squares using a direct downscaling approach [31]. We used the logistic regression equation to get probability values for 4 km2 squares according to the variable values for the same spatial resolution. In this way, we elaborated a risk map covering the entire Iberian Peninsula uniformly and at a high spatial resolution. Spatial analyses and the map display were elaborated using the geographic information systems QGIS 3.4 (www.qgis.org) and ArcGIS Desktop 10.7 (www.desktop.arcgis.com). Statistical analyses were performed using SPSS Statistics 26 (https://www.ibm.com).

Results

The occurrence of cases in horses and humans was affected by several factors (Table 1). Temperature and precipitation played an important role in the distribution of cases in horses and humans. The mean annual temperature in areas with cases in horses was 17.25 ± 0.92°C, while it was 17.52 ± 0.64°C in areas with human cases. Cases in horses were affected by a positive precipitation seasonality (64.01 ± 10.28) and mean temperature (25.53 ± 1.13°C) of the hottest month, while human cases were positively correlated by mean annual precipitation (587.03 ± 111.02 mm) and solar irradiation (5.2 ± 0.09 W/m 2). Agricultural land use also influenced the localisation of outbreaks. Infections in horses were more common in areas with rice fields and irrigated land, such as permanently irrigated land, fruit trees and pastures, while human cases were more common in areas with irrigation systems.

Table 1. Explanatory variables included in the risk model of West Nile virus infection in horses and humans, Iberian Peninsula.

Characteristics Horses Humans
B Wald Significance B Wald Significance
Climatic factors
Mean annual temperature 0.666 9.90 0.00165 0.831 6.80 0.00914
Mean temperature of the hottest month 0.284 6.14 0.0132 NA NA NA
Coefficient variation precipitation 0.107 33.15 < 0.0001 NA NA NA
Mean annual precipitation NA NA NA 0.009 30.85 < 0.0001
Surface incoming solar radiation NA NA NA 15.22 30.66 < 0.0001
Agricultural factors
Mix of agricultural land with natural vegetation -9.82 3.96 0.0466 NA NA NA
Rice fields 3.19 4.47 0.0344 NA NA NA
Irrigated land 1.41 6.40 0.0114 NA NA NA
Percentage of areas equipped with irrigation systems NA NA NA 0.06 26.09 < 0.0001
Constant -28.514 100.342 < 0.0001 -102.981 52.282 < 0.0001

NA: not applicable.

B is the coefficient that multiplies the variable values in the logit of the multivariate logistic regression.

The Wald parameter quantifies the relevance of the variable in the model.

Risk areas for WNV infection in humans were concentrated in the southern part of the Iberian Peninsula: along the coast, throughout the Guadalquivir River Basin and in two patches inland along the rivers Tagus and Guadiana (Figure). The high-risk areas for cases in horses were similar to those found in humans; however, the areas at risk were more extensive, with a wide zone in the south-western quadrant. The risk areas in the horse model also expanded northwards along the Mediterranean coast and extended inland following the river Ebro in the north-east of the peninsula (Figure).

Figure.

Risk areas for cases of West Nile virus infection in horses and humans, Iberian Peninsula

NUTS: Nomenclature of Territorial Units for Statistics; WNV: West Nile virus.

Notified cases of WNV infection in horses in blue and humans in yellow in the Iberian Peninsula at NUTS3. Bigger symbols with a white (horses) and black (humans) centre indicate cases in 2020. Star symbols indicate outbreaks in 2021 and 2022. The boundaries between Portugal and Spain are delineated by a black contour line.

Figure

Cartographically, risk models of horses and humans were very similar, although the high-risk areas for horses were more widespread. The risk areas identified by the horse model highlighted the main river basins in the Iberian Peninsula (Figure). All human cases of 2020 and all previous recorded outbreaks occurred in areas that were identified as high-risk by the horse model.

We evaluated the classification and discrimination capacity of the models. Both models showed high sensitivity, correctly detecting the cases in horses (sensitivity (Se) = 0.87) and humans (Se = 1). Equally, both models identified with high precision the absence of cases, showing a high specificity: 0.88 for horses and 0.95 for humans. Discrimination of the models was outstanding: 0.96 in horses and 0.99 in humans (Table 2). The horse model was evaluated with human cases, and the human model evaluated with the horse cases, which provided information about the utility of using cases in horses to predict risk for cases in humans, and vice versa. Both models showed a high sensitivity (> 0.81) and specificity (> 0.88). It is noteworthy that the horse model correctly classified all WNV cases in humans (Se = 1) and discriminated the human cases as effectively as the human model (Table 2).

Table 2. Comparative assessment of the classification and discrimination capacities of risk models of West Nile virus infection in horses and humans, Iberian Peninsula.

Assessment Horses Humans
Horse data Human data Human data Horse data
Kappa 0.06 0.03 0.07 0.13
Sensitivity 0.87 1 1 0.81
Specificity 0.88 0.88 0.95 0.95
CCR 0.88 0.88 0.95 0.95
Underprediction 0 0 0 0
Overprediction 0.96 0.98 0.96 0.92
AUC 0.96 0.99 0.99 0.95

AUC: area under the receiver operating characteristic curve; CCR: correct classification rate.

Data on notified cases in horses and humans in Spain and Portugal in 2020 were used. We used a favourability value of 0.5 as a cut-off point for classification purposes.

Discussion

During the last decades, the situation with WNV infection in Europe has progressed from sporadic cases to yearly outbreaks that affect both equines and humans [9,32,33]. The number of notified cases in humans has increased [34] and seroprevalence in animals in Spain has increased from < 10% to > 20% in the last years [35,36]. Understanding the environmental factors that contribute to the spread of WNV is crucial since currently a vaccine is only available for horses but not for humans [37]. The virus is transmitted through mosquitoes and certain environmental factors can increase the likelihood of transmission to equines and humans. Some environmental variables that contribute to outbreaks are high temperatures, water availability and type of agricultural areas. High temperatures increase mosquito density [38-40] and the replication [41] and transmission [13,42,43] of the virus, while precipitation facilitates mosquito reproduction [44]. Croplands [45,46], particularly paddy fields, are ideal breeding sites for mosquitoes and can increase contact rates between hosts and vectors [47,48]. Areas that meet these conditions are favourable for spillovers and can affect equines and humans.

The horse model could be used to predict high-risk areas for equine and human cases. Evaluation of the models showed that the horse model could correctly classify risk areas for WNV infection in humans. This means that equids can be used as identifiers of risk areas where the virus could occur. Equids are normally more exposed to mosquito bites than humans due to their management conditions. Therefore, if an area experiences a spillover of WNV from the enzootic cycle, equines may be the first exposed. In humans, WNV infection is usually asymptomatic and there are no specific signs; cases may go unnoticed if neurological symptoms are not seen. Diagnosed cases in humans are only the tip of the iceberg: 80% of individuals infected with WNV are estimated to be asymptomatic and less than 1% develop a severe form of the disease. In that case, WNV infection may be a life-threatening condition, leading to serious complications in people over 50 years and in immunocompromised patients [49]. However, clinical disease is more evident in equines than in humans. This susceptibility to the virus makes equids a useful WNV indicator species for the human population, especially during the transmission season, when mosquitoes are abundant, and spillovers take place.

In Europe, a relationship between the occurrence of cases in equines and in humans has been observed [33]. In other countries, such as Italy and Greece, cases have been reported in horses in areas where there have been no notified cases in humans [50]. Additionally, in southern Spain, multiple areas of Andalusia have reported cases in equines where human cases have not yet been detected. Moreover, in the north-eastern part of Spain (Catalonia), our horse model has identified risk areas, whereas the human model has not, suggesting that spillovers affecting equines may also affect humans but remain undetected. In fact, the first confirmed human case in Catalonia occurred during the summer of 2022 in an area identified by our horse model, confirming equines as possible indicators of WNV [51]. In 2018, WNV was detected for the first time in birds and horses in Germany [52]. One year later, WNV was detected for the first time in humans in the same region and adjacent regions where it had been detected in horses the previous year. Areas with cases only in horses may indicate a risk that outbreaks are occurring in humans but not being detected, which could potentially happen in the future in humans. Serological surveillance in equines would only be feasible in animals not recently vaccinated or that have acquired natural immunity from prior virus exposure [53]. Finding seronegative equines in high-risk areas is expected to become increasingly difficult. Therefore, their role as risk indicators may be limited in areas with high virus exposure.

Further studies are needed to determine the extent to which equine data can be used as indicators of a prospective outbreak risk. Maintaining surveillance on horses is crucial, and it should be combined with surveillance in mosquitoes, birds and the human population to allow a more integrated and comprehensive approach in endemic countries [50], and promoting surveillance where necessary, particularly in countries with limited resources. Equine surveillance is more cost-effective than mosquito surveillance and more efficient than avian surveillance [50,54,55]. The role of horses as early indicators of risk should not be underestimated, as cases in horses may precede those in humans by several years. A strong link between equine and human alerts must exist to provide an effective and timely response and to enable the implementation of specific measures.

The role of river basins in outbreaks of WNV infection in the Iberian Peninsula is also noteworthy, as has been reported in other countries [33,56] such as in Italy in the river Po [57] and in Greece in the rivers Axios [58] and Strimon [59]. The areas of favourability for cases in humans and more markedly in horses, show a cartographic gradient corresponding to the basins of the Guadalquivir, Guadiana Tagus and the lower part of the Ebro, and the most favourable areas are closest to the coast. Water availability is higher in the lower areas of the basins, leading to higher vector densities. In the Iberian Peninsula, wetlands are situated in the lower part of the river basins, with a permanent presence of birds that significantly increases during the migration periods, mostly in summer and autumn (post-nuptial migration). In the Iberian Peninsula, outbreaks have historically been concentrated to the coastal area of the river Guadalquivir, in the areas of Seville and Cadiz. This would also explain the smaller numbers of cases and the less favourable conditions in the higher areas of these main river basins. The WNV risk model in horses not only predicted human cases of WNV infection in 2020, but also areas of previous outbreaks in equines and humans. All cases to date have occurred in areas highlighted by our model as high risk, developed from 2020 horse outbreak data. Moreover, all cases that were detected in 2021 and 2022 also occurred in the areas marked as at-risk by our model. All outbreaks in the Iberian Peninsula have occurred in the four highlighted main river basins, except for three outbreaks that occurred in other smaller basins, but always in the lower part of the basins.

Conclusions

Based on our results, we propose river basins as-public health management units, rather than administrative units (such as municipalities or parishes). If cases are detected in horses, all health care centres within the same river basin should be alerted, as the spread can occur in neighbouring territories, even across countries like Portugal and Spain, if they share the same river basin. Decision-making would be more efficient from an ecosystem perspective, considering the environment and animal health as a whole, using in this case equines as identifiers of risk areas to ensure public health, i.e. the One Health approach. This biogeographic characterisation of the disease may help in the early identification of areas with a high potential risk, where cases in humans have not yet been detected. Our aim was to contribute to the knowledge of the viral ecology of this re-emerging pathogen in Europe and facilitate the development of surveillance programmes and preventive measures such as fumigation plans in sensitive areas or citizen awareness campaigns to reduce exposure and mosquito bites to reduce the impact of the disease and the number of people exposed to this virus.

Ethical statement

No ethical approval was required for this study since we used data in the public domain.

Acknowledgements

J.-M.G.-C. would like to thank the Ministry of Education, Culture and Sports for the FPU grant (FPU17/02834). We also would like to thank the Spanish Ministry of Science and Innovation and European Regional Development Fund (ERDF) for the Project PID2021-124063OB-I00, and Proyectos Puente Plan Propio B4, University of Malaga.

Supplementary Data

Supplementary Material

Conflict of interest: None declared.

Authors’ contributions: JMGC developed the study conception, design, performed the data analysis and wrote the original draft preparation. ARM, JO and RR supervised the process and the analysis. MS and IGB provided input on the interpretation of the work. All authors critically revised and edited the manuscript and approved its final version.

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