Abstract
Background
Temperature, precipitation, and humidity are important factors that can influence the spread, reproduction, and survival of pathogens. Climate change affects these factors, resulting in higher air and water temperatures, increased precipitation, or water scarcity. Climate change may thus have an increasing impact on many infectious diseases.
Methods
The present review considers those foodborne pathogens and toxins in animal and plant foods that are most relevant in Germany, on the basis of a selective literature review: the bacterial pathogens of the genera Salmonella, Campylobacter and Vibrio, parasites of the genera Cryptosporidium and Giardia, and marine biotoxins.
Results
As climate change continues to progress, all infections and intoxications discussed here can be expected to increase in Germany.
Conclusions
The expected increase in foodborne infections and intoxications presents a growing public health risk in Germany.
Keywords: CAMPYLOBACTER, SALMONELLA, VIBRIO, CRYPTOSPORIDIUM, GIARDIA, MARINE BIOTOXINS, ONE HEALTH
1. Introduction
Temperature, precipitation, humidity, and soil properties are important environmental factors that influence the spread and survival of zoonotic pathogens. Changes in these environmental factors as a result of climate change, such as permanently elevated ambient temperatures, increasing precipitation, but also water scarcity, may contribute to the spread and survival of pathogens. Climate change may thus exert an increasing influence on more than half of all infectious diseases [1]. This is not only true for already existing, i. e. endemic, infectious agents; climatic changes also favour the establishment of novel infectious agents (emergence) as well as the return of pathogens suppressed in the past (re-emergence). For example, in the future, agriculture may have to rely more frequently on treated wastewater due to water scarcity, which will be exacerbated by climate change. This poses a number of risks to food safety, including contamination of irrigated produce by various types of pathogens [2].
This review addresses hazards to human health posed by the most important foodborne bacteria, parasites and marine biotoxins in Germany and presents recommendations for reducing the risks. For example, the risk of all infections discussed here can be reduced by observing good hygiene during food preparation (kitchen hygiene) and adherence to cold chains.
Since viruses play a minor role in the impact of climatic changes on foodborne infections, they are not further discussed in this article. Their importance in the context of climate change is discussed in detail in other parts of this status report, e. g. in connection with vector-borne infectious diseases (Beermann et al. [3]).
2. Bacteria
2.1 Campylobacter
Bacteria of the genus Campylobacter (C.) cause an intestinal infection typically associated with abdominal pain and watery, occasionally bloody diarrhoea. Rare complications may include joint inflammation and Guillain-Barré syndrome, a nerve disease associated with paralysis. Even a low infectious dose of ≥500 germs can trigger a Campylobacter infection. Approximately 50,000 to 70,000 cases are reported to the Robert Koch Institute (RKI, Germany’s national public health institute) annually. For years, Campylobacter enteritis has been the most common bacterial diarrhoeal disease in Germany that has a mandatory notification requirement as per the German Protection against Infection Act (IfSG). The most important Campylobacter species pathogenic to humans are C. jejuni and C. coli. Transmission to humans occurs primarily via contaminated food of animal origin. In particular, consumption of contaminated chicken meat is a significant risk factor for Campylobacter infection [4–6]. Transmission to humans is also possible via other foods like non-pasteurised milk. Unlike Salmonella, Campylobacter is considered unlikely to multiply in food because of its microbiological characteristics (growth under microaerobic conditions, i. e. reduced oxygen concentration in the atmosphere, and at temperatures of 30°C to 42°C) [7]. Campylobacter infections via contaminated drinking water or bathing water contaminated with animal faeces have also been described [8, 9].
Climate influence on Campylobacter infections
Campylobacter enteritis infections typically follow a seasonal course, with the highest number of cases occurring in the summer months from July to September, including non-travel-associated infections. With progressive warming as a result of climate change and the associated prolonged warm periods, an increase in Campylobacter cases in humans is therefore expected.
It is conceivable that during the summer months, increased temperatures lead to higher Campylobacter prevalence in poultry flocks and thus higher exposure of consumers via consumption of poultry meat, although data on this are not consistent [10–14].
Altered consumption and recreational behaviours during the summer months have an important indirect effect on the increase in human infections, if they are associated with increased exposure, thus promoting infections, such as more frequent barbecuing of poultry and other meats, or swimming in surface waters [14, 15].
An association of human Campylobacter infections has been linked not only to temperature [16, 17] but also to the amount of precipitation in the days preceding the onset of illness [18, 19]. An increase in Campylobacter infections and Campylobacter enteritis outbreaks has been observed after heavy rains and flooding, likely due to increased exposure via faecal-contaminated surface water or contaminated drinking water [9, 20]. In contrast, Campylobacter cases are expected to decrease after periods of drought [18, 19].
With increasing water scarcity as a result of climate change, it is conceivable that treated wastewater, which may be contaminated with pathogens from animal or human faeces, will be used more frequently for irrigation of plant-based foods [21]. Increasing contamination of plantbased foods with gastrointestinal pathogens, including Campylobacter, would be expected via this route, thus compromising food safety [21]. European Union (EU) Regulation 2020/741 is intended to counteract this and regulates minimum standards for the use of treated wastewater in agricultural irrigation (Info box).
In a model calculation, the effect of increasing temperature and precipitation on the number of Campylobacter cases in Scandinavia was estimated. A doubling of Campylobacter cases by the year 2080 was predicted for Denmark, Finland, Norway, and Sweden [19]. Further scientific studies are needed to better understand the multifactorial, direct and indirect relationships between climatic changes and Campylobacter disease cases.
Info box: EU regulation on water reuse.
Climatic changes are increasing the pressure on water resources in Germany and Europe. To counter this pressure, Regulation (EU) 2020/741 established minimum requirements for the use of treated wastewater in agricultural irrigation. It came into effect on June 26, 2020, and will apply to all member states of the European Union from June 26, 2023.
The regulation is intended to reduce water scarcity in the European Union as a result of climate change by reusing water for agricultural irrigation and to facilitate implementation by the member states with uniform requirements. The aim is to achieve a high level of protection for the environment and for human and animal health, and to promote the circular economy [22]. The regulation on minimum requirements for water reuse is limited to agricultural irrigation. In addition to uniform minimum requirements for water quality and monitoring, risk management and provisions for data transparency are the main elements of the regulation [22]. In this context, the German Federal Institute for Risk Assessment (BfR) published opinions on possible risks associated with the reuse of treated wastewater for irrigation of edible crops [23–25]. Even wastewater that has already been treated may still contain parasites, bacteria and viruses in pathogenic concentrations. Therefore, particular care should be taken to ensure that plant parts that are usually consumed raw do not come into direct contact with irrigation water or, if this cannot be safely avoided, should continue to be irrigated with potable water. Persons belonging to risk groups are advised against consumption of such raw foods.
2.2 Salmonella
The bacteria of the genus Salmonella are zoonotic agents that can be transmitted directly or indirectly between humans and animals. They are widely distributed in nature. The main reservoir for Salmonella is warm-blooded animals, including livestock and wildlife. Salmonella also occurs in cold-blooded animals, such as reptiles or insects, which can act as vectors and transmit Salmonella to warm-blooded animals or humans. Although most salmonellae do not usually cause symptoms in animals, they can cause mild to severe health problems in humans. Human salmonellosis is often accompanied by fever, nausea, vomiting, abdominal pain, and headache, but signs of illness may be completely absent.
In Germany, salmonellosis is the second most frequently reported bacterial foodborne infection in humans after campylobacteriosis; Salmonella (S.) enterica is an important cause of foodborne outbreaks. Among these, S. Enteritidis and S. Typhimurium are the most common serovars, together accounting for approximately 75% of all reported salmonellosis cases [26]. Poultry is presumed the most important source of Salmonella infections in humans. In particular, eggs and egg products play a predominant role. Pork and pork products represent another important source [27, 28]. Increasingly, Salmonella infections are also reported to be associated with the consumption of foods of non-animal origin [27, 29]. Among these, raw leafy vegetables, onion and stem vegetables, tomatoes, and melons were the most commonly affected products. Contamination of these products with Salmonella can occur both before harvest (through faecal matter, irrigation water, dust, insects, etc.) and after harvest (through harvesting equipment, transport containers, insects, dust, rinsing water, ice, transport vehicles, processing equipment) [30].
Climate influence on Salmonella infections
In Europe, most salmonellosis cases are reported during the summer months [28]. The incidence of Salmonella is often lower in northern countries than in countries located in warmer climates.
Ambient temperature can influence the development of Salmonella at different stages of the food chain: e. g. bacterial contamination during raw food production, transport, and improper storage [31]. The optimal temperature for Salmonella growth is between 35°C and 37°C; below 15°C, growth of Salmonella is greatly reduced. Consequently, Salmonella multiply faster at higher temperatures. The significant correlation between outdoor temperatures and outbreaks caused by Salmonella has been known for some time. Studies have reported the increase of salmonellosis, as well as other bacterial enteric diseases, with increasing temperatures [32]. According to Zhang et al. [31], an increase of 8.8% in the number of weekly cases can be expected for a 1°C increase in the mean weekly maximum temperature. With a 1°C increase in the mean weekly minimum temperature, a 5.8% increase in the weekly number of cases can be expected.
Temperature can affect the transmission of Salmonella to humans through several pathways; by directly affecting the multiplication of Salmonella and by indirectly affecting eating habits during hot days. The favoured growth of Salmonella at higher temperatures leads to higher concentrations of Salmonella in contaminated foods during the warmer months. Among other things, this has to do with poor food preparation and refrigeration during barbecues or picnics, which are also more common during these months. Elevated ambient temperatures increase the risk of cold chain disruption, which can have a significant impact on the microbiological status of food.
Zhang et al. [33] found a strong correlation between drinking water quality, precipitation and gastroenteritis, where maximum and minimum temperatures, relative humidity and precipitation correlated positively with the number of salmonellosis cases.
In areas with increased rainfall, water quality could deteriorate. Heavy rains can increase run-off in rivers and lakes, washing sediment, pollutants, refuse, animal waste, and other materials into water supplies. Severe flooding can inundate wastewater treatment plants. This can lead to contamination of human, animal, and farm environments by bacteria in human sewage that are not only infectious, but can also be resistant to antimicrobial agents. Another article in this status report discusses this issue separately in the context of climate change impacts on health due to extreme weather events (Butsch et al. [34]).
2.3 Vibrio
Vibrio are environmental bacteria that colonise saline and brackish water bodies as well as wetlands worldwide, but can also occur in the microbial flora of aquatic animals. For humans, water contact and ingestion of Vibrio (V.)-containing seafood (fish, marine animals) can be problematic. As bacterial contaminants, V. cholerae, V. vulnificus, and V. parahaemolyticus in particular can cause infections [35, 36]. The significance of each species for humans varies regionally and is linked to area-specific factors, such as the salinity of water bodies, air and water temperatures, and fluctuations to which they are subject [37]. The genus Vibrio includes more than 135 species [38], three of which are largely causative of intestinal (e. g. gastroenteritis) or extraintestinal infections (e. g. middle ear infection) [35]. V. cholerae serotypes O1/O139, which produce the cholera toxin, are significant worldwide, as they can lead to pandemic cholera outbreaks in tropical and subtropical regions with poor water hygiene. In Europe, the only endemic Vibrio types are V. cholerae non-O1/non-O139 serogroups and other Vibrio species, collectively called non-cholera Vibrio (NCV). V. cholerae non-O1/non-O139 can lead to self-limiting infections with moderate diarrhoeal symptoms, but are rarely associated with food consumption. Gastrointestinal illness in Europe is mainly associated with haemolysin (trh/ tdh)-encoding V. parahaemolyticus isolates and consumption of raw or undercooked seafood. V. vulnificus, on the other hand, plays an important role in severe wound infections, which is discussed in another article in this status report that looks more closely at effects of climate change on waterborne infections and intoxications (Dupke et al. [39]). This species is common in coastal waters of moderate salinity worldwide and has been associated with fatal infections from consumption of contaminated oysters, with mortality rates for primary septicaemia (blood poisoning) sometimes exceeding 50% [37]. Accurate information on foodborne Vibrio infections is not yet available, as pathogen detection in diarrhoeal diseases is often not part of risk-based diagnostics, and a mandatory notification requirement for human Vibrio infections does not exist throughout Europe. In Germany, only isolated cases of gastrointestinal NCV infections have been recorded since the introduction of mandatory notification according to the IfSG in 2020, which may indicate either low exposure to Vibrio-containing products or that a large proportion of the illnesses are not detected and thus not reported [40].
The importance of seafood has increased due to its high protein, vitamin and mineral content. For many years, the annual per capita consumption in Germany was covered by wild catch, but now increasingly comes from aquacultures. Usually, seafood is offered in processed form (e. g. heated, marinated, smoked) and should thus contain no or hardly any Vibrio. However, raw and insufficiently heated products pose a risk [40]. Mussels and oysters in particular are predestined to enrich even small amounts of Vibrio due to their way of filtering of nutrients from the water. Thus, they pose a health risk, especially for people with weakened immune systems or pre-existing conditions.
In mussels and oysters, V. alginolyticus (sometimes associated with middle ear infections in humans) and V. parahaemolyticus are frequently detected, and rarely V. cholerae non-O1/non-O139 and V. vulnificus have been reported, with V. alginolyticus occurring year-round and the other species occurring exclusively during the warm summer and fall months [41]. Within Europe, several countries (e. g. Spain, France, United Kingdom) cultivate mussels and oysters, some of which are heavily contaminated with toxigenic Vibrio (up to 25% toxigenic V. parahaemolyticus ) [40].
There are hardly any reliable data available on the probability of occurrence of a health impairment after exposure to Vibrio species pathogenic to humans. In principle, the risk of health impairment correlates with the amount of ingested pathogenic Vibrio and is also dependent on the respective species. In addition, the probability of occurrence of a health impairment is increased in vulnerable groups of people (YOPI: young, old, pregnant, immunocompromised people).
Climate influence on Vibrio infections
Compared to the rest of the world, foodborne Vibrio infections have been rare in Europe so far, which may change in the future in the course of climate change. In general, water temperatures above 12°C and low or moderate salinity (1–25 g/L) have a favourable effect on the occurrence of Vibrio spp. [36]. Optimal growth conditions already occur in Europe during the summer months on the Atlantic coast and in inland seas [42]. The occurrence of Vibrio spp. is favoured by global warming and the increase of heatwaves and may lead to the spread of endemic Vibrio and possibly also to the establishment of new pathotypes in Europe, so that the human infection incidence may increase in the future, especially in coastal areas and estuaries [42, 43]. The continuous increase in water temperature will lead to an amplification of Vibrio contamination in European seafood catching, harvesting, and farming areas, and will also expand beyond the summer and autumn months. Currently, the occurrence of pathogenic Vibrio is low in bodies of water with fluctuating temperatures, such as the North Sea and the Baltic Sea, whereas toxigenic NCV are increasingly detected in waters with consistently warm temperatures, from which seafood is partly imported [41]. In seafood, the occurrence of species pathogenic to humans correlates directly with water temperatures as well [36, 40].
Minimisation of risk to humans, especially in relation to contact with and consumption of seafood, is possible by avoiding exposure to pathogenic species, e. g. through appropriate product processing strategies, thermal treatments, adherence to hygienic measures, a strict cold chain, and good and rapid monitoring immediately after capture, harvest, or import [40].
3. Parasites
Climate change can also influence infections by parasites, especially if these are characterised by a significant environmental presence and high environmental stability. This applies in particular to protozoa, unicellular organisms that live as parasites. Even if profound knowledge is lacking, recent research data (German Federal Institute for Risk Assessment (BfR); data not published) indicate that a changing climate also has a direct impact on the prevalence and virulence of these pathogens, which are already very stable in the environment. A risk of transmission to humans through food is usually associated with those foods that are consumed raw or inadequately cooked. Food contamination can occur via vectors (e. g. insects, mammals including those providing food to humans) but also via contaminated irrigation systems. In addition, food can be affected by cross-contamination, such as when hygiene is poor during food preparation.
3.1 Cryptosporidia
More than 40 different species of the protozoan genus Cryptosporidium have been described to date, which can infect a large number of different animal species and humans. Here, we focus on the species Cryptosporidium (C.) parvum and C. hominis, as they are responsible for the largest proportion of human infections [44]. C. hominis occurs almost exclusively in humans, while the primary hosts for C. parvum are cattle, horses, goats, and sheep, and, to a lesser extent, dogs, cats, and birds [45]. Infection occurs via the faecal-oral route by ingestion of the infective developmental stages (oocysts); transmissions from animal to animal, human to human, animal to human, and vice versa are possible [46]. However, infection can also occur through ingestion of contaminated water (e. g. swimming pool, river, lake, or spring water). Another source of infection can be plant-based foods that have been contaminated with infested water.
Cryptosporidiosis is one of the most common diarrhoeal diseases associated with the ingestion of contaminated water. In 2013, an outbreak with 167 cases was recorded in Germany in association with flooding after a heavy rain event [47]. Foodborne illnesses have also been described in Europe, which have been attributed to the consumption of lettuce [24].
In Germany, there is a mandatory notification requirement for detection of cryptosporidia in connection with an illness in accordance with the IfSG. Between 900 and 2,000 cases are reported to the RKI annually; in Europe, there are 8,000 to 14,000 cases annually. Data from the European Centre for Disease Prevention and Control (ECDC) show that cryptosporidiosis in Europe has seasonal increases in late spring and late summer to early autumn, respectively [48].
Young children, people with weakened immune systems, travellers to developing countries, and people who drink untreated water are at increased risk of infection.
Infection may be asymptomatic or symptomatic. Symptoms described include prolonged watery diarrhoea with weight loss, severe abdominal pain or cramps, nausea, vomiting, and headaches [49]. After infection, further complications (e. g. inflammation of the pancreas, appendicitis, impairment of the lungs) and even death may occur. After the symptoms have subsided, the oocysts continue to be excreted in the stool for many weeks. The infectious dose of cryptosporidia is low, ranging from 10 to 1,000 oocysts, depending on the species [50]. However, it is suspected that one oocyst may be sufficient for infection in humans [51].
3.2 Giardia
Parasites of the protozoan genus Giardia can also be affected by climate change. Giardia are currently classified into eight species [52]. However, the species Giardia (G.) duodenalis (synonyms: G. lamblia, G. intestinalis) is the only species of this genus that can infect humans as well as numerous mammalian species. G. duodenalis is distributed worldwide; humans are considered the main reservoir. Infection occurs faecal-orally by ingestion of the infectious developmental stages of the parasite (1 to 10 cysts are sufficient) with contaminated tap water or untreated fresh water from lakes or streams. However, Giardia cysts can also be transmitted by eating contaminated food or by close contact with infected persons or animals [53].
Giardiasis caused by G. duodenalis is one of the most common intestinal parasitoses in humans worldwide [54]. Prevalence rates are significantly higher in developing countries than in developed countries. For example, 3,296 travel-associated cases of the disease were reported to the RKI in 2019; the most frequently cited country of infection was India [26]. However, as warming due to climate change continues, increased local infections will also be expected. Infants and young children, older persons, travellers, and immunocompromised persons are among the high-risk groups [55]. In more than 50% of cases, the disease is asymptomatic, but the course can be severe in infants and older persons [56].
In Germany, detection of this pathogen in connection with an illness is notifiable.
Globally, G. duodenalis is estimated to cause 28.2 million cases of diarrhoeal disease per year due to food contamination [52]. The European Food Safety Authority (EFSA) recorded 14 foodborne outbreaks and 3 outbreaks due to water consumption in Europe in 2019 [57]. Data on foodborne outbreaks in Germany are not yet available.
3.3 Climate influence on parasites
Cryptosporidium and Giardia can remain infectious for a long period of time and cause disease, especially after consumption of raw contaminated food.
Their high stability against environmental influences, in particular the long survivability in aqueous environments, suggests that these parasites could appear more frequently as pathogens in the future. Extreme weather such as heavy rainfall and flooding, which are also expected to increase in our latitudes as a result of climate change, increase the risk of infectious oocysts/cysts entering bodies of water, as well as the risk of contamination of plant-based foods. The risk for humans can be minimised by good kitchen hygiene.
4. Biogenic toxins of marine origin
More than 20% of the protein requirements of over 3 billion people worldwide are met by seafood. Consumption of fish as food has increased by 3.1% annually over the last 50 years [58]. Climate change is increasingly causing warming, acidification, and oxygen depletion of the oceans, altered water salinity, and sea level rise. The temperature of the oceans’ surface water has increased greatly, as more than 90% of the global temperature increase has been absorbed by the oceans [59]. These changes are affecting marine biodiversity, which in turn can significantly impact the availability of food, animal protein, and essential micronutrients for billions of people around the world [60, 61].
The above factors can also affect the abundance and composition of marine phytoplankton. Planktonic microalgae form the basis of the aquatic food web, but can have harmful effects if they occur in large abundance. The phenomenon of sudden, explosive growth of algae is called an algal bloom. When these algal blooms have negative consequences, such as creating hypoxic or anoxic conditions (lack of oxygen or complete absence of oxygen) or producing toxins, they are referred to as harmful algal blooms (HABs). HABs have the potential to disrupt fish communities and food webs, and can even lead to massive species extinctions [62]. Currently, approximately 300 microalgal species are known to be involved in the formation of such algal blooms. Of these, about 100 species can produce toxins that can lead to specific toxic syndromes in animals and humans.
Marine biotoxins enter the food chain through organisms that filter water or feed on algae, such as shellfish and fish, and thus may pose a threat to human health due to their toxic properties [63, 64]. Furthermore, exposure to toxins produced by marine phytoplankton can occur through inhalation or through the skin, via aerosols that contain toxins and cell fragments and can cause skin irritation and respiratory symptoms [65, 66].
Climate change is altering the geographic distribution of some algal species that may be involved in the formation of HABs. Warm-water species, for example, may be expanding poleward and appearing in areas where they were not previously native. In this context, identifying and studying the geographic distribution of toxin-producing organisms is critical for implementing appropriate preventive and control measures prior to harvest or during the distribution and sale of seafood. This is particularly important because marine biotoxins are not normally detectable by odour, taste, or appearance and are not usually destroyed by cooking, freezing, or other food preparation processes.
In the interests of preventive consumer health protection, maximum levels have been set within the EU for five different toxin groups in live bivalve molluscs. Furthermore, products containing compounds of the ciguatoxin group that can cause mild to severe poisoning (ciguatera) in humans [67] may not be marketed within the EU [68, 69].
5. Conclusion and recommendations
Climate change affects various habitats, which can be altered by weather events such as prolonged droughts, temperature increases, and heavy rains. These changes also affect the foods derived from these habitats and micro- organisms or toxins that may be associated with these foods. For example, foods may be more heavily contaminated with pathogens or contain germs that were not previously present in a region. But climate-related events also affect food indirectly. For example, ever-increasing water scarcity means more frequent use of treated wastewater for food irrigation. Because such wastewater may still contain parasites, bacteria, and viruses in disease-causing concentrations, plant parts that are commonly consumed raw should not come into contact with treated wastewater, or should continue to be irrigated with potable water [23–25]. Progressive climate change in Germany is expected to lead to an increase of the infections and intoxications discussed here, making them a growing public health concern.
Our main recommendations for minimising the health risk from foodborne infections and intoxications lie in the area of kitchen hygiene, which should always be applied when preparing food. This includes thorough hand washing and the use of fresh kitchen utensils after handling raw meat and fish, as well as avoidance of cross-contamination, i. e. direct or indirect pathogen transmission from one food to another. Wearing gloves can prevent the entry of pathogens via unnoticed skin lesions. Food safety is also highly dependent on maintaining the cold chain. In addition, most microbiological pathogens can be safely killed by a sufficient heating process; for example, a core temperature of 70°C for at least two minutes must be maintained when preparing seafood. In contrast, biogenic toxins associated with food are largely insensitive to temperature [40, 70, 71].
We also recommend the use of new technologies to track supply chains. Given a globalised food distribution network and the use of different processing and preservation techniques, it can be difficult to track a product’s supply chain to identify potential risks. Technological advances have produced digital solutions for this; knowledge of fish stocks, seafood traceability and supply chain transparency can benefit from innovative approaches. These include blockchain or radio frequency identification device tags for product authentication (including species and catch data), as well as applications of machine learning, data mining, artificial intelligence, and other digital technologies [72]. These methods of digitally-enabled food supply chains can support sustainable development in the food industry, which aims to reward responsible and ethical producers and keep illegal or unethically produced food products out of supply chains [73].
Further research is needed on the links between climatic changes and disease incidence, and on the geographic distribution of toxin-producing organisms.
Key statement
The number of infections with germs such as Salmonella or Campylobacter correlates positively with maximum temperature and precipitation amounts.
Environmentally associated germs such as waterborne Vibrio are increasingly finding their way into food, especially seafood, and causing an increase in infections.
Rising temperatures and humidity favour fitness and possibly virulence of parasites such as Cryptosporidium and Giardia.
An increase in infections due to Cryptosporidium and Giardia is to be expected.
Ocean warming is leading to increased growth of toxinproducing algae, whose toxins can enter the food chain via marine animals.
Acknowledgement
The KlimGesundAkt coordination team at Robert Koch Institute would like to thank the following persons for their work on the project’s advisory board: Sophie Gepp, Elke Hertig, Claudia Hornberg, Tanja-Maria Kessel, Andreas Matzarakis, Odile Mekel, Susanne Moebus, Jonas Schmidt-Chanasit, Alexandra Schneider, Klaus Stark, Wolfgang Straff and Maike Voss.
Funding Statement
The publication was coordinated through the project KlimGesundAkt, which is funded by the Federal Ministry of Health (chapter 1504; title 54401 HJ2021; duration 07/2021–06/2024).
Footnotes
The German version of the article is available at: www.rki.de/jhealthmonit
Data protection and ethics
This article contains information on the authors’ own research results, which were carried out in compliance with ethical guidelines and the General Data Protection Regulation (GDPR).
Conflicts of interest
The authors declared no conflicts of interest.
Authors’ contributions
Campylobacter: Rosner B
Salmonella: Szabo I
Vibrions: Hammerl JA, Richter MH
Parasites: Johne A, Nöckler K, Richter MH
Biogenic toxins: Dietrich J, Spielmeyer A, Loeffler C, Kappenstein O
All authors have made comparable contributions.
Disclaimer
Note: External contributions do not necessarily reflect the opinions of the Robert Koch Institute.
References
- 1.Mora C, McKenzie T, Gaw IM, et al. (2022) Over half of known human pathogenic diseases can be aggravated by climate change. Nat Clim Chang 12(9):869–875 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 2.Thebo AL, Drechsel P, Lambin EF, et al. (2017) A global, spatiallyexplicit assessment of irrigated croplands influenced by urban wastewater flows. Environ Res Lett 12(7):074008 [Google Scholar]
- 3.Beermann S, Dobler G, Faber M, et al. (2023) Impact of climate change on vector- and rodent-borne infectious diseases. J Health Monit 8(S3): 33–61. www.rki.de/jhealthmonit-en (As at 01.06.2023) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 4.Wingstrand A, Neimann J, Engberg J, et al. (2006) Fresh chicken as main risk factor for campylobacteriosis, Denmark. Emerg Infect Dis 12(2):280–285 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 5.European Food Safety Authority (2010) Scientific opinion on quantification of the risk posed by broiler meat to human campylobacteriosis in the EU. EFSA Journal 8(1):1437 [Google Scholar]
- 6.Rosner BM, Schielke A, Didelot X, et al. (2017) A combined case-control and molecular source attribution study of human Campylobacter infections in Germany, 2011–2014. Sci Rep 7(1):5139. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7.Stingl K, Knuver MT, Vogt P, et al. (2012) Quo vadis? – Monitoring Campylobacter in Germany. Eur J Microbiol Immunol (Bp) 2(1):88–96 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 8.Schonberg-Norio D, Takkinen J, Hanninen ML, et al. (2004) Swimming and Campylobacter infections. Emerg Infect Dis 10(8):1474–1477 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 9.Hyllestad S, Iversen A, MacDonald E, et al. (2020) Large waterborne Campylobacter outbreak: Use of multiple approaches to investigate contamination of the drinking water supply system, Norway, June 2019. Euro Surveill 25(35):2000011. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 10.Patrick ME, Christiansen LE, Waino M, et al. (2004) Effects of climate on incidence of Campylobacter spp. in humans and prevalence in broiler flocks in Denmark. Appl Environ Microbiol 70(12):7474–7480 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 11.Ishihara K, Takahashi R, Andoh M, et al. (2012) Effects of climatic elements on Campylobacter-contaminated chicken products in Japan. Epidemiol Infect 140(6):991–996 [DOI] [PubMed] [Google Scholar]
- 12.Williams MS, Golden NJ, Ebel ED, et al. (2015) Temporal patterns of Campylobacter contamination on chicken and their relationship to campylobacteriosis cases in the United States. Int J Food Microbiol 208:114–121 [DOI] [PubMed] [Google Scholar]
- 13.Meldrum RJ, Griffiths JK, Smith RM, et al. (2005) The seasonality of human Campylobacter infection and Campylobacter isolates from fresh, retail chicken in Wales. Epidemiol Infect 133(1):49–52 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 14.David JM, Pollari F, Pintar KD, et al. (2017) Do contamination of and exposure to chicken meat and water drive the temporal dynamics of Campylobacter cases? Epidemiol Infect 145(15):3191–3203 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 15.Rushton SP, Sanderson RA, Diggle PJ, et al. (2019) Climate, human behaviour or environment: Individual-based modelling of Campylobacter seasonality and strategies to reduce disease burden. J Transl Med 17(1):34. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 16.Louis VR, Gillespie IA, O’Brien SJ, et al. (2005) Temperaturedriven Campylobacter seasonality in England and Wales. Appl Environ Microbiol 71(1):85–92 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 17.Oberheim J, Hoser C, Luchters G, et al. (2020) Small-scaled association between ambient temperature and campylobacteriosis incidence in Germany. Sci Rep 10(1):17191. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18.Soneja S, Jiang C, Romeo Upperman C, et al. (2016) Extreme precipitation events and increased risk of campylobacteriosis in Maryland, U.S.A. Environ Res 149:216–221 [DOI] [PubMed] [Google Scholar]
- 19.Kuhn KG, Nygard KM, Guzman-Herrador B, et al. (2020) Campylobacter infections expected to increase due to climate change in Northern Europe. Sci Rep 10(1):13874. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 20.Sterk A, Schijven J, de Roda Husman AM, et al. (2016) Effect of climate change on runoff of Campylobacter and Cryptosporidium from land to surface water. Water Res 95:90–102 [DOI] [PubMed] [Google Scholar]
- 21.Duchenne-Moutien RA, Neetoo H. (2021) Climate change and emerging food safety issues: A Review. J Food Prot 84(11):1884–1897 [DOI] [PubMed] [Google Scholar]
- 22.Umweltbundesamt (2021) Neue EU-Verordnung zu Wasserwiederverwendung. https://www.umweltbundesamt.de/themen/wasser/wasser-bewirtschaften/wasserwiederverwendung/neue-eu-verord-nung-zu-wasserwiederverwendung (As at 15.01.2023)
- 23.Bundesinstitut für Risikobewertung (BfR) (2020) Reclaimed waste water: Preventing bacterial pathogens on fresh fruit and vegetables. https://www.bfr.bund.de/cm/349/reclaimed-waste-water-prevent-ing-bacterial-pathogens-on-fresh-fruit-and-vegetables.pdf (As at 23.01.2023)
- 24.BfR (2022) Reclaimed waste water: Preventing protozoa on plant foods. https://www.bfr.bund.de/cm/349/reclaimed-wastewater-preventing-protozoa-on-plant-foods.pdf (As at 23.01.2023)
- 25.BfR (2022) Reclaimed waste water: Preventing viral pathogens on plant foods. https://zenodo.org/record/7346234 (As at 12.05.2023)
- 26.Falkenhorst G, Enkelmann J, Frank C, et al. (2020) Zur Situation bei wichtigen Infektionskrankheiten – Reiseassoziierte Krankheiten 2019. Epid Bull 50:7–20 [Google Scholar]
- 27.Interagency Food Safety Analytics Collaboration (2021) Foodborne illness source attribution estimates for 2019 for Salmonella, Escherichia coli O157, Listeria monocytogenes and Campylobacter using multi-year outbreak surveillance data, United States. Department of Health and Human Services’ Centers for Disease Control and Prevention and U.S. Food and Drug Administration; U.S. Department of Agriculture’s Food Safety and Inspection Service. https://www.cdc.gov/foodsafety/ifsac/pdf/P19-2019-report-TriAgency-508.pdf (As at 15.01.2023)
- 28.EFSA, ECDC (2021) The European Union One Health 2020 zoonoses report. EFSA Journal 19(12):6971. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 29.Olaimat AN, Holley RA. (2012) Factors influencing the microbial safety of fresh produce: A review. Food Microbiol 32(1):1–19 [DOI] [PubMed] [Google Scholar]
- 30.Beuchat LR. (2002) Ecological factors influencing survival and growth of human pathogens on raw fruits and vegetables. Microbes Infect 4(4):413–423 [DOI] [PubMed] [Google Scholar]
- 31.Zhang Y, Bi P, Hiller JE. (2010) Climate variations and Salmonella infection in Australian subtropical and tropical regions. Sci Total Environ 408(3):524–530 [DOI] [PubMed] [Google Scholar]
- 32.Akil L, Ahmad HA, Reddy RS. (2014) Effects of climate change on Salmonella infections. Foodborne Pathog Dis 11(12):974–980 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 33.Zhang Y, Bi P, Hiller J. (2008) Climate variations and salmonellosis transmission in Adelaide, South Australia: A comparison between regression models. Int J Biometeorol 52(3):179–187 [DOI] [PubMed] [Google Scholar]
- 34.Butsch C, Beckers LM, Nilson E, et al. (forthcoming) Health impacts of extreme weather events – Cascading risks in a changing climate. J Health Monit. www.rki.de/jhealthmonit-en [DOI] [PMC free article] [PubMed]
- 35.Farmer JJ, III, Janda JM, Brenner FW, et al. (2015) Vibrio. In: Whitman WB. (Ed) Bergey’s manual of systematics of archaea and bacteria. John Wiley & Sons, Inc., in association with Bergey’s Manual Trust, P. 1–79 [Google Scholar]
- 36.Food and Agriculture Organization of the United Nations (FAO), WHO (2020) Risk assessment tools for Vibrio parahaemolyticus and Vibrio vulnificus associated with seafood. Microbiological risk assessment series;20. Rome. https://apps.who.int/iris/handle/10665/330867 (As at 15.01.2023)
- 37.Centers for Disease Control and Prevention (2019) Vibrio and food. https://www.cdc.gov/vibrio/food.html (As at 15.01.2023)
- 38.DSMZ (2022) LPSN - List of Prokaryotic names with Standing in Nomenclature. Genus Vibrio. https://lpsn.dsmz.de/genus/vibrio (As at 15.01.2023) [DOI] [PMC free article] [PubMed]
- 39.Dupke S, Buchholz U, Fastner J, et al. (2023) Impact of climate change on waterborne infections and intoxications. J Health Monit 8(S3): 62–77. www.rki.de/jhealthmonit-en (As at 01.06.2023) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 40.BfR (2022) Bacterial foodborne Vibrio infections: Health risk assessment of the occurrence of Vibrio spp. (non-cholera vibrios) in food. https://www.bfr.bund.de/cm/349/bacterial-foodborne-vibrio-in-fections-health-risk-assessment-of-the-occurrence-of-vibrio-spp-in-food.pdf (As at 23.01.2023)
- 41.Martinez-Urtaza J, Bowers JC, Trinanes J, et al. (2010) Climate anomalies and the increasing risk of Vibrio parahaemolyticus and Vibrio vulnificus illnesses. Food Res Int 43(7):1780–1790 [Google Scholar]
- 42.Baker-Austin C, Oliver JD, Alam M, et al. (2018) Vibrio spp. infections. Nat Rev Dis Primers 4(1):8. [DOI] [PubMed] [Google Scholar]
- 43.Vezzulli L, Baker-Austin C, Kirschner A, et al. (2020) Global emergence of environmental non-O1/O139 Vibrio cholerae infections linked with climate change: A neglected research field? Environ Microbiol 22(10):4342–4355 [DOI] [PubMed] [Google Scholar]
- 44.O’Leary JK, Blake L, Corcoran GD, et al. (2021) Development of a novel, high resolution melting analysis based genotyping method for Cryptosporidium parvum. Eur J Protistol 79:125799. [DOI] [PubMed] [Google Scholar]
- 45.Bouzid M, Hunter PR, Chalmers RM, et al. (2013) Cryptosporidium pathogenicity and virulence. Clin Microbiol Rev 26(1):115–134 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 46.Davies AP, Chalmers RM. (2009) Cryptosporidiosis. BMJ 339:b4168. [DOI] [PubMed] [Google Scholar]
- 47.Gertler M, Durr M, Renner P, et al. (2015) Outbreak of Cryptosporidium hominis following river flooding in the city of Halle (Saale), Germany, August 2013. BMC Infect Dis 15:88. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 48.Caccio SM, Chalmers RM. (2016) Human cryptosporidiosis in Europe. Clin Microbiol Infect 22(6):471–480 [DOI] [PubMed] [Google Scholar]
- 49.Carter BL, Chalmers RM, Davies AP. (2020) Health sequelae of human cryptosporidiosis in industrialised countries: A systematic review. Parasit Vectors 13(1):443. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 50.RKI (2004) RKI-Ratgeber Infektionskrankheiten – Merkblätter für Ärzte. Kryptosporidiose. Epid Bull 34:279–281 [Google Scholar]
- 51.Hamilton KA, Waso M, Reyneke B, et al. (2018) Cryptosporidium and Giardia in wastewater and surface water environments. J Environ Qual 47(5):1006–1023 [DOI] [PubMed] [Google Scholar]
- 52.Ryan U, Hijjawi N, Feng Y, et al. (2019) Giardia: An underreported foodborne parasite. Int J Parasitol 49(1):1–11 [DOI] [PubMed] [Google Scholar]
- 53.Burnett MW. (2018) Giardiasis. J Spec Oper Med 18(1):106–107 [DOI] [PubMed] [Google Scholar]
- 54.Certad G, Viscogliosi E, Chabe M, et al. (2017) Pathogenic mechanisms of Cryptosporidium and Giardia. Trends Parasitol 33(7):561–576 [DOI] [PubMed] [Google Scholar]
- 55.Leung AKC, Leung AAM, Wong AHC, et al. (2019) Giardiasis: An overview. Recent Pat Inflamm Allergy Drug Discov 13(2):134–143 [DOI] [PubMed] [Google Scholar]
- 56.Rumsey P, Waseem M. (2021) Giardia Lamblia Enteritis. In: Stat-Pearls. StatPearls Publishing, Treasure Island (FL) [PubMed] [Google Scholar]
- 57.EFSA, ECDC (2021) The European Union One Health 2019 zoonoses report. EFSA Journal 19(2):6406. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 58.FAO (2020) The state of world fisheries and aquaculture 2020. Sustainability in action. Rome. https://www.fao.org/documents/card/en/c/ca9229en/ (As at 15.01.2023)
- 59.IPCC (2019) Summary for Policymakers. In: Pörtner HO, Roberts DC, Masson-Delmotte V, et al. (Eds) Intergovernmental Panel on Climate Change special report on the ocean and cryosphere in a changing climate. Cambridge University Press, Cambridge, UK und New York, NY, USA, P. 3–35. https://www.cambridge.org/core/services/aop-cambridge-core/content/view/097A895553D86981DFE6195ADFD3DDA4/stamped-9781009157971pre2_3-36.pdf/summary_for_policymak-ers.pdf (As at 16.01.2023) [Google Scholar]
- 60.Hicks CC, Cohen PJ, Graham NAJ, et al. (2019) Harnessing global fisheries to tackle micronutrient deficiencies. Nature 574(7776):95–98 [DOI] [PubMed] [Google Scholar]
- 61.Falkenberg LJ, Bellerby RGJ, Connell SD, et al. (2020) Ocean acidification and human health. Int J Environ Res Public Health 17(12):4563. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 62.Kudela RM, Berdalet E, Bernard S, et al. (2015) Harmful algal blooms: A scientific summary for policy makers. Intergovernmental Oceanographic Commission, Scientific Committee on Oceanic Research, Paris. https://unesdoc.unesco.org/ark:/48223/pf0000233419 (As at 15.01.2023)
- 63.Friedman MA, Fernandez M, Backer LC, et al. (2017) An updated review of ciguatera fish poisoning: Clinical, epidemiological, environmental, and public health management. Mar Drugs 15(3):72. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 64.Food and Drug Administration (2020) Fish and fishery products hazards and controls guidance. Fourth Edition U.S. Food Drug Administration. https://www.fda.gov/media/80637/download (As at 15.01.2023)
- 65.Ciminiello P, Dell’Aversano C, Iacovo ED, et al. (2014) First finding of Ostreopsis cf. ovata toxins in marine aerosols. Environ Sci Technol 48(6):3532–3540 [DOI] [PubMed] [Google Scholar]
- 66.Pierce R, Henry M, Blum P, et al. (2003) Brevetoxin concentrations in marine aerosol: Human exposure levels during a Karenia brevis harmful algal bloom. Bull Environ Contam Toxicol 70(1):161. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 67.FAO, WHO (2020) Report of the expert meeting on ciguatera poisoning: Rome, 19–23 November 2018. Food safety and quality series; 9. Rome. https://apps.who.int/iris/handle/10665/332640 (As at 15.01.2023)
- 68.EFSA Panel on Contaminants in the Food Chain (2010) Scientific opinion on marine biotoxins in shellfish – Emerging toxins: Ciguatoxin group. EFSA Journal 8(6):1627 [Google Scholar]
- 69.Regulation (EC) No 853/2004 of the European Parliament and of the Council of 29 April 2004 laying down specific hygiene rules for food of animal origin. Official Journal of the European Union L 139/55, Vol 47. https://eur-lex.europa.eu/legal-content/EN/TXT/PDF/?uri=CEL-EX:32004R0853R(01)&from=EN (As at 16.01.2023)
- 70.BfR (2018) Game meat: Health assessment of human-pathogenic parasites. https://www.bfr.bund.de/cm/349/game-meat-health-assess-ment-of-human-pathogenic-parasites.pdf (As at 23.01.2023)
- 71.BfR (2019) Schutz vor lebensmittelbedingten Infektionen mit Campylobacter. https://www.bfr.bund.de/cm/350/verbrauchertipps-schutz-vor-lebensmittelbedingten-infektionen-mit-campylobacter.pdf (As at 15.01.2023)
- 72.Loeffler CR, Tartaglione L, Friedemann M, et al. (2021) Ciguatera mini review: 21st century environmental challenges and the interdisciplinary research efforts rising to meet them. Int J Environ Res Public Health 18(6):3027. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 73.Tsolakis N, Niedenzu D, Simonetto M, et al. (2020) Supply network design to address United Nations Sustainable Development Goals: A case study of blockchain implementation in Thai fish industry. J Bus Res 131:495–519 [Google Scholar]