key: cord-0812122-ndnqanxp authors: Semenza, Jan C.; Paz, Shlomit title: Climate change and infectious disease in Europe: Impact, projection and adaptation date: 2021-10-07 journal: Lancet Reg Health Eur DOI: 10.1016/j.lanepe.2021.100230 sha: 0ba1a026c15a2d53996ca82b37ad54290ddfbc1c doc_id: 812122 cord_uid: ndnqanxp Europeans are not only exposed to direct effects from climate change, but also vulnerable to indirect effects from infectious disease, many of which are climate sensitive, which is of concern because of their epidemic potential. Climatic conditions have facilitated vector-borne disease outbreaks like chikungunya, dengue, and West Nile fever and have contributed to a geographic range expansion of tick vectors that transmit Lyme disease and tick-borne encephalitis. Extreme precipitation events have caused waterborne outbreaks and longer summer seasons have contributed to increases in foodborne diseases. Under the Green Deal, The European Union aims to support climate change health policy, in order to be better prepared for the next health security threat, particularly in the aftermath of the traumatic COVID-19 experience. To bolster this policy process we discuss climate change-related hazards, exposures and vulnerabilities to infectious disease and describe observed impacts, projected risks, with policy entry points for adaptation to reduce these risks or avoid them altogether. Despite the COVID-19 pandemic, according to the World Health Organization (WHO) climate change may be the defining global public health threat of the 21st century 1 since it is threatening all aspects of human society including risks to human health 2 . Increasingly, a growing number of infectious health outcomes are associated with climate change that are inequitably distributed within and between European countries. Weather parameters contribute in a nonlinear way to infectious disease transmission 3 and have been shown to be one of the key drivers of the emergence, re-emergence, and spread of infectious disease 4, 5 . Moreover, they contribute to the survival, reproduction and distribution of disease pathogens and vectors, as well as to their transmission and geographical patterns 6 . While the climatic suitability for transmission may decrease in certain areas 7 , it may increase in others for a number of infectious diseases 8 . However, infectious disease impacts from climate change are not only a function of these climate hazards but also of other hazards such as pathogens or vectors (Box 1). Moreover, health impacts also depend on exposure patterns in human populations and underlying vulnerabilities ( Fig. 1 ; Box 1). Climate change impacts result in fact from dynamic interactions between hazard, exposure and vulnerability. The complexity of the nexus of these three elements of climate change impacts was recognized in the new European Union (EU) Strategy on Adaptation 9 to climate change which was adopted in February 2021 by The European Commission. The cornerstone of the strategy is to improve the knowledgebase of climate impacts and adaptation solutions by stepping up adaptation planning and climate risk assessments, by accelerating adaptation action, and by helping to strengthen climate resilience globally. Thus, the purpose of this paper is to review the observed health impacts and projected risks from infectious disease in Europe that can be attributed to climate, from the synergic perspective of hazard, exposure and vulnerability and their impacts on disease transmission (Fig. 1) . Insights from this analysis offer different policy entry points for interventions on infectious disease threats from climate change. precipitation in Southern and Eastern Europe and conversely, an increase in the frequency and severity of heavy rainstorms and floods in Northern Europe 10 , exemplified by the July 2021 record rainfall and associated flooding in Western Europe with over 200 fatalities and highlighted population exposure and vulnerability even in highly developed countries 11 . In Europe, the warmest year on record was 2020, and all the warmest years were documented during the last decade. The 2019/20 winter is infamous as the warmest recorded winter ever, and 2020 the warmest recorded autumn with a significant heatwave during the summer in the western countries 12 . Nearly twoÀthirds of European human and domestic animal pathogens are climate sensitive 13 . Some of them cause the most significant diseases, based on morbidity and mortality, which might therefore also be affected by climate change 6, 14 . Here we review the most updated scientific evidence on observed health impacts and projected risks from climate change for infectious disease in Europe and examine adaptation options for infectious disease with opportunities for preparedness and response. Of particular interest were publications since 2017 that examined the specific aims of this study, and assessed the association between climate change and disease transmission in Europe. Vector-borne diseases (VBDs) are mainly transmitted by arthropod vectors such as mosquitoes, which are particularly sensitive to changes in external climatic conditions because they are cold-blooded (ectothermic) 15 . Habitat suitability determines insect density, distribution and abundance (Table 1) . Furthermore, temperature impacts the rate of pathogen maturation and replication in mosquitoes, and increases the likelihood of infection 3, 16 . For diseases transmitted by vectors that have aquatic developmental stages, precipitation also exerts a very strong influence on VBD dynamics in various ways, depending on the differences in the ecology of mosquito vectors 17 . Analysis of the underlying drivers of infectious disease threat events detected in Europe during 2008À2013 by epidemic intelligence at the European Centre of Disease Prevention and Control revealed seventeen drivers. The most important drivers of epidemic threat events caused by VBD are the natural environment, followed by climate, travel and tourism 4 . However, attributing VBD to climate change is complicated by nonlinear feedback loops between population susceptibility and immunity 3 . Yet, climate is a well-established driver of VBD epidemiology 18 . In the EU and European Economic Area (EEA) Member States and EUneighboring countries there were 336 locally-acquired human cases of West Nile virus (WNV) infections in 2020, 463 cases in 2019, and 2083 cases in 2018 19 . WNV is a major cause of encephalitis. Migratory birds Definition of terms: hazard, exposure, vulnerability, impact and risk from climate change. Hazard: The potential incident of a natural or human-induced physical event or trend that may cause loss of life, injury, or other health impacts, as well as damage and loss to property, infrastructure, livelihoods, service provision, ecosystems and environmental resources. Can be climatic phenomena such as average temperature increase, heat waves, drought, or extreme precipitation events that can be sudden or gradual. Hazards include also sea level rise, habitat destruction, ecosystem intrusion, mobility, and the climatic/environmental suitability for vectors and pathogens, that in of themselves can be considered hazards; thus, hazard exists regardless of exposure. Exposure: The state of people, livelihoods, species, property, (eco-)systems, or other elements present in hazard zones that thereby could be adversely affected or have no protection from something harmful and are therefore subject to potential impacts. Certain types of land use, geography, flood water, contaminated drinking water supply, traffic corridors or presence of vectors and pathogens determine exposure of individuals or communities under specific circumstances. For example, global mobility contributes to the introduction of and exposure to pathogens and vectors. Vulnerability: The propensity or predisposition to be adversely affected. Vulnerability encompasses a variety of concepts and elements including sensitivity or susceptibility to harm and lack of capacity to cope and adapt; it can stem from contextual conditions, individual-level characteristics, or the socio-economic environment; it can be determined by social, human, financial, physical or natural capital or by social inequalities. Vulnerability to health can be higher among poorer, marginalized or less educated individuals/communities, migrants, the young, as well as the elderly, exposed workers or individuals with underlying medical conditions. Moreover, vulnerability is also defined by the lack of safeguards (e.g., door/window screens for vectors, flood barriers) or personal susceptibility (e.g., age, sex, education, medical predisposition). Impact: Adverse outcomes of realized risks on natural and human systems, where risks result from the interactions of climate-related hazards, exposure, and vulnerability. Impacts refer to effects on lives; livelihoods; health and well-being; ecosystems and species; economic, social and cultural assets; services (including ecosystem services); and infrastructure. Risk: The potential for adverse consequences where something of value is at stake and where the occurrence and degree of an outcome is uncertain. Source: Adapted from IPCC. Lack of food safety regulations; Breakdown of cold chain; Suboptimal processing, preparation, transport, storage, packaging, wrapping, exposure for sale, service, or delivery of food. Assure universal access to care and disease management; Improve disease surveillance for FBD; Health education and promotion for food preparation and storage in a warmer climate; Infection control of livestock (e.g., salmonella vaccine for poultry; window screens on chicken coops to prevent campylobacter infection); Improve eating habits; Better food processes and storage procedures (e.g., cold chains, conservation); Monitor of climatic conditions to prevent crop damage from droughts or floods as part of early warning system. Note: ID: infectious disease; VBD: vector-borne disease; WBD: water-borne disease; FBD: food-borne disease. on their flyway from sub-Saharan Africa, North Africa or the Middle East introduce WNV into Europe where the virus overwinters in mosquitoes 20 . The virus is then transmitted to humans, mainly by mosquito species from the genus Culex (family Culicidae) which are widely distributed in Europe, even in less vulnerable regions as Scandinavia and the United Kingdom (Fig. 2) . The early and extensive WNV circulation in Southern and Central Europe in 2018 with over 2000 cases (see above) can be explained, in part, by the very high temperatures in early spring which seems to have activated the mosquito breeding season, reduced the extrinsic incubation period and thereby accelerated virus amplification in the avian and mosquito populations. 21 Throughout the last decade, locally-acquired human cases of WNV infections, including deaths, occurred in a number of European countries in the South (e.g. Spain, Italy, Greece) East (e.g. Romania, Bulgaria, Hungary) 22 and even North (Germany) 23 . For the first time, WNV infection was detected in a bird in the Netherlands, which foreshadowed the first detection of human cases in the country in the summer of 2020 24 . The circulation of WNV has steadily expanded over the years to affect new areas in Europe. High precipitation in late winter/early spring was found as one of the key predictors of WNV outbreaks across Europe 25 . Conversely, during drought conditions the lack of wetlands concentrates mosquitoes and birds around water bodies, which in turn also favors WNV transmission 26 . For example, a wet spring followed by drought provided the most likely explanation for the observed increase in WNV activity in Europe in 2018 27 . Europe has also been plagued by recurrent autochthonous outbreaks caused by different vectors that have experienced a rapid global expansion due to international mobility: Aedes aegypti and Ae. albopictus mosquitoes. Ae. aegypti is a highly competent vector for tropical diseases like dengue, chikungunya and Zika, that is restricted to warm, urban environments, whereas Ae. albopictus is a moderately competent vector for these pathogens, far more ecologically flexible, and can be found in suburban, rural, residential, and agricultural habitats 28 . The success of the invasion of Ae. albopictus to new regions is due to a number of ecological and human-caused factors such as its ecological plasticity, increase of trade and travel, and lack of efficient control 29 . Additionally, studies indicate that climate change exacerbates the risk and burden of Aedes-transmitted viruses 28 and allows the introduction of events into new regions 30 . Based on present-day climatic conditions, there is a current potential distribution of Ae. albopictus in Europe, mainly in its southern regions 30 . This is comparable with the current known distribution of the vector, which has experienced a steady expansion, reaching Northern France and parts of Germany (Fig. 3) 6 . Indeed, a potential risk for cases of chikungunya, Zika and dengue already exists in the southwestern regions 29, 31 . In 2007, Europe was struck for the first time by a large outbreak of 330 chikungunya cases in Italy, which raised public health concerns 32 . Two smaller outbreaks of autochthonous cases of chikungunya were reported in France in 2010 and 2014 29 . Furthermore, a decade after the first outbreak in Italy, a large outbreak of 489 cases occurred during the climatically suitable season 33 . During recent years, sporadic autochthonous cases of dengue were reported in southern countries, for example in Catalonia, Spain, in France in September 2019, and in France and Italy in summer 2020. Here again, cases of dengue are expected in the southern regions in the summer and autumn due to the presence of the vector and the introduction of dengue and/or chikungunya viruses by travel-associated cases returning from epidemic/endemic countries 29 . Leishmaniasis is a vector-borne disease caused by protozoa of the genus Leishmania predominantly but not exclusively confined to tropical and sub-tropical regions. It manifests itself in different forms in humans, including cutaneous leishmaniasis which causes skin lesions. In Europe, the disease burden is relatively low due to antiretroviral therapies but Leishmania spreads by the bite of infected sandflies with the primary vectors being Phlebotomus spp., present around the Mediterranean but also further North in France and Germany (Fig. 4) . Leishmaniasis has been associated with exposure in poor living conditions and climate change which are, at present, rapidly exacerbating conditions that attract sand flies and leishmaniasis towards temperate regions 34 . Life parameters of sand flies depend mainly on temperature and, to a certain extent, on humidity. A vector population dynamic model from Greece, Cyprus and Turkey, indicated that temperature, changes in breeding habitats and in land use, do have also a strong impact on sand fly abundance 35 . Ixodes ticks can transmit bacteria from the genus Borrelia (causing Lyme disease), which is the most prevalent tick-transmitted infection in temperate areas of Europe. They also transmit the virus that causes several thousand cases per year in the EU/EEA of tickÀborne encephalitis (TBE) which can result in severe neurological sequelae in up to 10% of patients. The geographic distribution of Ixodes ricinus, the most common arthropod vector of human disease in Europe, is related to climatic factors such as humidity, soil water, and air temperature, as well as to vegetation type, land use, and disturbance 36 . Studies found that I. ricinus has shifted its seasonal activity and geographical range both on latitudinal and elevation limits as a result of the increasing temperatures 37 . This shift and increase in activity is related to milder winters and prolonged spring and autumn seasons in the 1990s, combined with other factors such as increased vegetative cover 16, 38 . The transmission pathway of food-borne pathogens from farm to fork is complex. Many of the pathogens that cause food-borne diseases (FBD) are able to persist in the environment, can sustain heat stress, and are infective at a low dose. Of those, Campylobacter is the most common bacterial cause of diarrhoeal disease in developed countries and with over 220,000 cases per year and a notification rate of 60 cases per 100,000 population. It is the most commonly reported cause of human bacterial gastroenteritis throughout the EU/EEA 39 . It shows a strong association with seasonality and climate variability, mainly with increased temperatures that may increase bacterial contamination at various points along the food chain 40, 41 (Table 1 ). Since Campylobacter cannot replicate outside of the host, hot ambient conditions may actually influence people's behavior, rather than replication rates which, in turn, may be translated into more risky patterns of food consumption 42, 43 (Table 1) . A study on Campylobacter infections in England and Wales found that the increase of infections in the late spring was significantly linked to the temperature two weeks earlier. Since the relationship with temperature was not linear, it seems that the association is likely to be indirect 44 and might be due to other seasonal factors such as fly transmission 45 (Table 1) . A study in the Nordic countries shows that the temporal and geographical distribution of Campylobacter can be associated with increases in temperature and heavy rainfall, that may increase the number of cases reported in the following week. Conversely, heat waves and winter precipitation may decrease the number of cases reported 42 . With over 87,000 cases per year in the EU/EEA, salmonellosis is the second most commonly reported gastrointestinal infection in humans after campylobacteriosis, and a significant cause of foodborne outbreaks 39 . Salmonella is climate sensitive and grows in a narrow temperature envelope with more frequent infections in the summer months 40 (Table 1 ). The incidence of human Salmonella infections (20.0 cases per 100,000 population) is higher in the summer period than in the winter period and thus highly seasonal. Studies show an increase in weekly temperatures is followed by an upsurge in incidence which indicates that warm weather accelerates Salmonella reproduction 43,46 . Climate change alters the continuous circulation of water on earth in unpredictable ways (Table 1) . Severe weather events, flooding, storm surges, and droughts are all manifestations of the hydrological cycle gone awry 47 . As opposed to gradual changes in climate, abrupt and sudden changes are even more challenging for public health practice 41 . An extreme precipitation episode can trigger a causal chain of secondary events with unexpected consequences. Such a cascading risk pathway can have a ripple effect and damage critical infrastructure 41 (Table 1) . Cascading risks depend on existing vulnerabilities in society that get exacerbated by climate change 48 . For example, a heavy rain event can flush animal pathogens from pastures into waterways and overwhelm ageing water treatment and distributions systems, which can result in waterborne outbreaks 40, 49 (Table 1 ). An alternate urban transmission pathway of a water-borne disease (WBD) triggered by extreme weather events, characterized by warm/extremely warm and wet/extremely wet has been associated with a peak in incidence of human leptospirosis, a highly infectious, emerging water-borne zoonosis, caused by Leptospira interrogans 50 . As part of a systematic literature review of infectious disease following a natural disaster in Europe, eight studies described cascading risk pathways with outbreaks following flooding, four of which were caused by leptospirosis 51 . The increase in global ambient temperature leads to elevated sea surface temperature which accelerates the replication of pathogenic Vibrio bacteria in marine waters. Anthropogenic climate change drives the emergence of Vibrio infections in the Baltic, which is associated with morbidity and mortality among recreational water users 52 . Different scenarios for Europe predict that temperature will continue to rise and exacerbate the duration, frequency and intensity of heat waves 53 . Differential temperature increases are expected in Northwest Europe and Scandinavia in the winter and in Southeast and Southern Europe in the summer. Throughout most of Europe, less precipitation during summer along with rising temperatures will result in more frequent and intense summer droughts, exacerbating water scarcity. Conversely, heavy rainstorms and flash floods such as in July 2021 in Western Europe 11 , are projected to become more frequent 10, 54 . Consequently, there is growing concern that higher temperatures and changes in precipitation patterns will affect the transmission of some VBD, WBD, and FBD, with increased and decreased projections depending on the affected region and degree of climatic change 55 . In most cases, increased transmission is predicted but contractions of the geographic distribution can also be expected. While changes in the magnitude and pattern of climate-sensitive health outcomes are likely, if thresholds are crossed, some of the changes could be significant 56 . A modelling study of WNV infection spreading in Europe under climate change scenarios predicts that in 2025, progressive expansion of areas with an elevated probability for infections is expected, particularly at the edges of the current transmission. In 2050, an increase in areas with a higher probability of expansion is projected 57 . Predictions suggest that Ae. albopictus will continue to be a successful invasive species spreading beyond its current (Fig. 3) . It is expected to spread broadly, with expanded distributional potential across much of western Europe and the Balkan region 30 . Yet, some areas are predicted to become less suitable for the species, particularly in Eastern Europe where models indicate increased aridity. Models generally project a moderate climatic suitability for chikungunya transmission, notably across France, Spain, Germany and Italy, with increased suitability in large areas by the Rhine and Rhone rivers. However, some areas by the Italian Adriatic coast are projected to experience a decline in suitability due to the increased probability of summer droughts 58 . The climatic suitability for dengue transmission predicted to improve over the next decades, particularly around the Mediterranean and Adriatic coasts and in northern Italy 29, 59 . By the end of the century increasing climatic suitability is predicted to expand into a larger part of Europe 60 . However, the current lack of a highly competent vector like Ae. Agypti in continental Europe renders the risk for sustained dengue outbreaks low 61 . Phlebotomine sandflies, the vectors of Leishmania, have the potential to expand their range (Fig. 4) , under future climatically suitable conditions, towards central and northern Europe, reaching the islands of Great Britain and Scandinavia 62 . A northward shift in climate suitability for tick species from their current distribution is predicted for the coming decades 63 . Future scenarios indicate a potential further expansion of I. ricinus in northern and eastern Europe, resulting from milder winter conditions and extended spring and fall seasons. Such changes will enable more ticks to survive the winter, and increase the probability of tick bites 16, 38 . The changing climate may impact food-borne diseases as well. According to a recent study, an overall increase in campylobacteriosis of almost 200% is estimated for the Scandinavian countries by the end of the century 42 . This means nearly 6,000 excess campylobacter cases per year which could potentially be attributed to an extension of the transmission season and other chances to the climate. Temperature-related incidence of salmonella is also projected to increase in Europe under climate change scenarios but can be offset by public health mitigation strategies 43 . Climate change risks from infectious disease can be reduced by acting on hazards, exposure and vulnerability ( Fig. 1; Table 1, Box 1) . As a result of the changing climate, health systems need to be prepared for gradual and abrupt changes in health outcomes and potential new conditions, including additional threats from infectious disease transmission. The need to prevent and reduce the severity of current and future climate change impacts in Europe (Fig. 1) highlights the necessity to develop systematic policies of vector and infectious disease control programs, health action plans, adaptation strategies and resilience measures, based on the typical regional risk factors and population health needs 64 . A number of the adaptation options for infectious disease in Europe is part of traditional public health practice (Table 1) . Regrettably, many of the infectious disease control measures have been neglected during the epidemiologic transition, but have now received renewed attention during the COVID-19 pandemic. While the core capacities in public health of the WHO International Health Regulations (IHR) have been proven to be effective to control infectious disease threat events in Europe in general 48, 65 , but they certainly did not prove to be sufficient to contain the explosive epidemic of COVID-19 . Moreover, a number of interesting developments in the field of infectious disease control have emerged that lend themselves for the management of climatesensitive infectious disease ( Table 1) . One of the most exciting new developments is the acceleration of vaccine development and the application of new technologies such as the joint BioNTech-Pfizer COVID-19 mRNA vaccine (BNT162b2) for SARS-CoV2 66 (Fig. 5) . These new technologies have proven to be a game-changer of the COVID-19 response that can now also be applied to climate-sensitive infectious disease 48 . The risk from VBD such as dengue or chikungunya in Europe, can be dissected into two phases: the risk for importation of the pathogens by viremic passengers arriving from endemic countries into Europe where a competent vector is present; and the risk for onwards transmission and dispersion of these pathogens to susceptible individuals by local mosquitoes, which is a function of the climatic suitability for transmission and population exposure during population movement (Fig. 5) . This process was examined during the 2017 Chikungunya outbreak in France and Italy, by using flight passenger data 33 . These indicators highlighted the areas at risk for importation both from endemic countries but also from the outbreak zones in southeastern France and central Italy to other areas in Europe. Subsequently, the seasonal vectorial capacity of Aedes albopictus mosquitoes was computed to estimate the risk to transmit chikungunya virus. The vectorial capacity estimates can elucidate the local climatic suitability for mosquito borne outbreaks. Moreover, repeated geolocated Twitter feeds from Twitter Streaming Application Programming Interface (API) can provide information on unidirectional population mobility from the epicentre of the epidemic to other areas at risk that need to be targeted for interventions. The use of nearÀrealtime geocoded Twitter data can help to quantify human ground movement and disentangle connectivity between outbreak hotspots 33 . Thus, the application of big data and analyses can be applied in real time to respond quickly to climate-sensitive infectious disease ( Fig. 5 ; Table 1 ). In these areas at risk, mosquito breeding sites need to be eliminated to reduce mosquito density and seasonal surveillance should be conducted for both mosquitoes and human health to identify sentinel cases. It was demonstrated that window screens and air conditioning can substantially reduce bite intensity based on survey data from mainland France 67 and by extension, exposure to infected mosquitoes ( Fig. 5 ; Table 1 ). Insecticides, larvicides, and repellents can be used for vector control to minimize exposure in human populations but in case of detection, verification and notification other intervention measures should be initiated ( Fig. 5 ; Table 1 ). For example, WNV outbreaks pose a threat to blood banks and the supply of safe blood products and increases the risk to the safety of blood transfusion 57 . Risk reduction interventions should include deferral strategies, screening strategies and triggers and also pathogen reduction technologies 68 (Table 1) . The risk from WBD is compounded by cascading climate events that trigger a sequence of secondary events that cause disruption of natural or human systems. 41 For example, extended periods of excessive precipitation can saturate soils and mobilize pathogens from fields and pastures and flush them into water treatment and distribution systems which can result in waterborne outbreaks. Such a vulnerability calls for upgrading ageing water catchment, storage, treatment and distribution infrastructure and repairing leaking pipes (Table 1) . Critical infrastructure needs to be protected from floods, storms and sea level rise. Adaptation interventions to contain cascading risk pathways entails also forecasting meteorological conditions predictive of climate-sensitive infectious disease emergence (Table 1 ). An early warning system of atmospheric forecasts can predict heavy rain events or an increase in sea surface temperature in marine waters. Monitoring sea surface temperature and salinity in real time remotely can predict the environmental suitability of pathogenic Vibrio infections in marine waters 52 . Such a system has been operationalized at the European Centre for Disease Prevention and Control and is in use with weekly alerts to state epidemiologists during hot summer months (Fig. 6 ). Beach closures, alerts to the public and notifications to health care providers can minimize the exposure of recreational water users to such marine bacteria (Table 1 ). Foodborne outbreaks have been associated with farming practices, food processing, handling, and storage that are all sensitive to climatic conditions. Outbreaks have been associated with contamination of drinking and irrigation water and along the food chain (from farm to fork) if the cold chain breaks down 69 . Thus, adaptation options for FWB require farm-level interventions to prevent food contamination, during production, processing, and distribution (Table 1) . For example, fly screens as part of biosecurity practices in broiler chicken coops can help reduce prevalence of campylobacteriosis among humans 70 . However, it also entails public education campaigns for improved eating habits, safe food preparation, and storage in a warmer climate (Table 1) . Moreover, the current food system accounts for up to 30% of greenhouse gas emissions which is another incentive to create climate-adapted, agroecological food production (circular agriculture). A number of food-and waterborne diseases are climate-sensitive through direct pathways, while vector-borne diseases are mediated by vectors through indirect pathways. Attributing the contribution of climate change to disease incidence and prevalence is difficult due to other underlying drivers and determinants 71 . Nevertheless, the magnitude of climate-sensitive disease is considerable, also in Europe, which calls for better adaptation options (Table 1) . Therefore, preparedness and response to such health security threats should be based on inter-sectorial collaboration between governmental (e.g., local, regional, national, super national) and non-governmental actors (e.g., community, commerce, faith-based organizations, civil society) and diverse scientific disciplines (e.g., biology, entomology, environment, climatology, social science) 48 . Epidemiological data should be merged, integrated, and analyzed with climatic, biological, environmental, ecological and demographic data in order to interpret complex disease patterns 5, 64, 72 . Predictive modelling of the expected impacts of climate change on disease transmission involving different climate and socioeconomic scenarios is critical in order to develop better early warning systems for disease outbreaks, to help decisionmakers understand more precisely where or when infections will emerge or spread 52, 56 . Under the European Green Deal 73 , the EU adopted proposals to reduce net greenhouse gas emissions by at least 55% by 2030, compared to 1990 levels. As part of the European Green Deal, the EU Adaptation Strategy 9 and EU4Health 74 , the European Climate and Health Observatory 75 was created to provide access to information regarding climate change impacts on human health. Specifically, the Observatory aims to support Europe in preparing for and adapting to climate change impacts through early warning systems, information systems, indicators and tools. This review can guide the Observatory in its mandate, as proposed under the European Green Deal, and direct action towards the three cogs of the wheel: hazard, exposure or vulnerability. Fig. 1 and Table 1 exemplify policy entry points how climate change risk can be reduced by acting on the nexus of hazard, exposure and vulnerability. Moreover, rising awareness of the potential risks from climate change among scientist from various disciplines, the health community, policymakers and the public is vital but not a given. Strengthening public awareness can be achieved by educational programs using the involvement of the media and community leaders. Health workers should provide useful insights for simplifying scientific knowledge to deliver climate-health messages 72 . This should include recommended prevention of negative health outcomes, such as elimination of habitats for vectors and prevention of water-borne and food-borne diseases and infections ( Table 1 ). The punishing effect of the COVID-19 pandemic on health and socio-economic wellbeing are a stark reminder of the pitfalls of insufficient preparedness 48 . The take-home message from the current crisis is that preparedness and response, risk assessment, and early warning systems, along with climate change adaptation are essential in order to mitigate the impacts of the climatic changes on the (re-) emergence of infectious disease and to prevent their negative consequences for population health. Both authors contributed equally to this manuscript. All resources for the current review appear in the reference list. The Lancet Group takes a neutral position with respect to territorial claims in published maps and institutional affiliations. The authors declare no competing interests. COVID-19): Climate change COP24 Special Report Health and Climate Change Identifying climate drivers of infectious disease dynamics: recent advances and challenges ahead Determinants and drivers of infectious disease threat events in Europe Strengthening the global response to climate change and infectious disease threats Vector-borne diseases and climate change: a European perspective Malaria transmission potential could be reduced with current and future climate change The 2020 report of The Lancet Countdown on health and climate change: responding to converging crises European Commission. EU Adaptation Strategy Climate Action -How will we be affected Germany floods-a global warming warning for extreme intensity of weather events Editorial The Lancet Regional Health warmest year on record for Europe; globally, 2020 ties with 2016 for warmest year recorded Systematic assessment of the climate sensitivity of important human and domestic animals pathogens in Environmental drivers, climate change and emergent diseases transmitted by mosquitoes and their vectors in southern Europe: A systematic review Climate change: an enduring challenge for vector-borne disease prevention and control Impact of recent and future climate change on vector-borne diseases Effects of climate change on vector-borne diseases: An updated focus on West Nile virus in humans Climate change impacts on West Nile virus transmission in a global context Historical data by year -West Nile virus seasonal surveillance West Nile virus in overwintering mosquitoes, central Europe A quantitative comparison of West Nile virus incidence from Nile virus in Europe in 2020 -infections among humans and outbreaks among equids and/or birds West Nile virus epidemic in Germany triggered by epizootic emergence First autochthonous human West Nile virus infections in the Netherlands Identifying the environmental conditions favouring West Nile Virus outbreaks in Europe Transmission dynamics of the West Nile virus in mosquito vector populations under the influence of weather factors in the Danube Delta Early start of the West Nile fever transmission season 2018 in Europe Global expansion and redistribution of Aedes-borne virus transmission risk with climate change More arboviral disease outbreaks in continental Europe due to the warming climate? Mapping the global potential distributions of two arboviral vectors Aedes aegypti and Ae. albopictus under changing climate Reviewing estimates of the basic reproduction number for dengue, Zika and chikungunya across global climate zones Infection with chikungunya virus in Italy: an outbreak in a temperate region Using big data to monitor the introduction and spread of Chikungunya Combining climatic projections and dispersal ability: a method for estimating the responses of sandfly vector species to climate change G€ urtler RE A climate-driven and field data-assimilated population dynamics model of sand flies Correlation of Borrelia burgdorferi sensu lato prevalence in questing Ixodes ricinus ticks with specific abiotic traits in the western palearctic A Retrospective Assessment of temperature trends in Northern Europe reveals a deep impact on the life cycle of Ixodes ricinus (Acari: Ixodidae) Climate change influences on the potential geographic distribution of the disease vector tick Ixodes ricinus The European Union One Health Climate change impact assessment of food-and waterborne diseases Cascading risks of waterborne diseases from climate change Campylobacter infections expected to increase due to climate change in Northern Food-borne disease and climate change in the United Kingdom Seasonality and the effects of weather on Campylobacter infections Fly transmission of Campylobacter Pathogen seasonality and links with weather in England and Wales: a big data time series analysis Changes in hydrology and its impacts on waterborne disease Lateral public health: advancing systemic resilience to climate change. The Lancet Regional Health À Europe Association between heavy precipitation events and waterborne outbreaks in four Nordic countries New trends in human and animal leptospirosis in Croatia Natural disasters and infectious disease in Europe: a literature review to identify cascading risk pathways Environmental suitability of vibrio infections in a warming climate: an early warning system Heat-health action plans in Europe: Challenges ahead and how to tackle them Trends and projections in Europe Health risks of warming of 1.5°C, 2°C, and higher, above pre-industrial temperatures Preventing and mitigating health risks of climate change Climate change projections of West Nile virus infections in Europe: Implications for blood safety practices Modelling the effects of global climate change on Chikungunya transmission in the 21st century Using global maps to predict the risk of dengue in Europe Climate change and the emergence of vector-borne diseases in Europe: Case study of dengue fever Estimating the probability of dengue virus introduction and secondary autochthonous cases in Modeling the climatic suitability of leishmaniasis vector species in Europe Climate suitability for European ticks: Assessing species distribution models against null models and projection under AR5 climate Priorities for protecting health from climate change in the WHO European Region: recent regional activities Systemic resilience to cross-border infectious disease threat events in Europe Safety and Efficacy of the BNT162b2 mRNA Covid-19 Vaccine Risk factors of exposure to Aedes albopictus bites in mainland France using an immunological biomarker Blood supply under threat Climate change and food security: health impacts in developed countries Foodborne disease prevention and broiler chickens with reduced Campylobacter infection Observed and projected drivers of emerging infectious diseases in Europe Integrating public health into climate change policy and planning: State of practice update The European Climate and Health Observatory