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What Human Diseases Have No Animal Vectors

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The Brute Origin of Major Human Infectious Diseases: What Can Past Epidemics Teach Usa Nigh Preventing the Next Pandemic?

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Zoonoses

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affliction environmental, emerging infectious disease, pathogen, parasite, zoonoses

Emerging infectious diseases are one of the greatest public health challenges. Approximately three-quarters of these diseases are of animal origin. These diseases include classical zoonoses maintained in humans only via transmission from other vertebrates (e.g., rabies) and those initiated by a successful i-off zoonotic consequence (host-switch) in conjunction with efficient human-to-human transmission (east.g., H1N1 influenza). Here, we provide a systematic review, in conjunction with a meta-analysis and spatial hazard modeling, to identify the major characteristics of past epidemics of animal origin and predict areas with high future disease emergence risk. Countermeasures against time to come pandemics of animal origin must focus on several fundamental mechanisms. First, the eco-epidemiological contexts favoring spillover events must exist clearly plant. Second, pathogen surveillance must be scaled up, particularly in taxa and/or eco-geographic areas with high disease emergence adventure. Third, successful spillover take a chance must be mitigated through proactive strategies to interrupt animate being-to-homo transmission chains. Quaternary, to decrease epidemic potential and preclude epidemics from becoming pandemics, improved source identification and real-time spatial tracking of diseases are crucial. Finally, because pandemics practice not respect international borders, enhancing international collaboration is critical to improving preparedness and response.

INTRODUCTION

Human history has been punctuated by many pandemics, including the bubonic plague (fourteenth century), the Spanish flu (20th century), HIV/AIDS (twentythursday and 21st centuries), and coronavirus disease 2019 (COVID-19). Having infected more than than 238 million people and caused more than iv.eight million deaths since its emergence in Dec 2019 [i] (Fig 1), COVID-19 has underscored the devastating, long-lasting societal and economical consequences of emerging infectious diseases. Peculiarly alarmingly, the risk of novel disease emergence in human populations is increasing because of the confluence of numerous drivers of global ecology change, including those associated with climate, land-use (e.g., urbanization), and the agronomical industry (e.g., large commercial beast farms). Moreover, this risk is aggravated by the e'er-increasing resistance to antimicrobial drugs and insecticides used for disease vector control [2,3], and the growing potential for the rapid spread of diseases with increased global transport [four–7].

Figure 1 |

Major diseases of animal-origin affecting human health.

A timeline of emergence of diseases of animal-origin which are considered to be a threat to global wellness or which require urgent research as identified by the Globe Health System, including: (a) Crimean-Congo hemorrhagic fever; (b) Dengue fever; (c) Marburg virus disease; (d) Lassa fever; (eastward) Rift Valley fever; (f) Hendra virus disease; (g) Highly Pathogenic Asian Avian Influenza A subtype H5N1; (h) Nipah virus disease; (i) HIV/AIDS; (j) Zika fever; (thousand) Ebola virus illness; (l) Sudden Acute Respiratory Syndrome (SARS); (chiliad) Flu A virus subtype H1N1; (north) Middle E Respiratory Syndrome (MERS); (o) Coronavirus Disease 2019 (COVID-19). For each disease the yr of initial identification (round symbols on time line) or declaration of a public health emergency of international business concern (square symbols on time line) are shown. The spatial extent of each disease is besides given as a map highlighting with areas where transmission is reported (red areas) and the location from where the pathogen was first reported (blueish symbol). Also, depicted are the major routes of transmission in the zoonotic source population (dark-green arrows), master zoonotic event (red arrows) and manner of maintenance in the human population (light-green arrows). Diseases include those that are strictly zoonotic and maintained in the homo population only through transmission from a vertebrate animal host (e.grand., Rift Valley fever and Hendra virus illness), diseases that are primarily maintained past zoonotic spillover but which can also exist transmitted directly betwixt humans (eastward.g., Ebola/Marburg virus diseases and MERS), and diseases of animal-origin which show very efficient human-to-human transmission (e.chiliad., HIV infection, H5N1/H1N1 influenza). Several diseases are suspected to be of zoonotic origin but the vertebrate brute reservoir remains unconfirmed (e.m., Ebola virus affliction, SARS and COVID-xix). See Supplemental Cloth for references to source information used to produce the figure.

From a public health perspective, considering approximately three-quarters of all emerging infectious diseases are caused past pathogens originating from domestic or wild animal species [viii], concerns regarding the threat of human being infectious diseases of beast origin have grown. These pathogens vary considerably in terms of the conditions favoring spillover events and the resultant public health consequences. For instance, strictly zoonotic diseases cannot be maintained in human populations without new spillover events from a vertebrate reservoir, because human-to-human transmission does not occur (e.g., echinococcosis, toxoplasmosis, and rabies). Other infections, such as bubonic plague (caused by Yersinia pestis), Lyme affliction (acquired by Borrelia burgdorferi), and West Nile fever (acquired past the W Nile virus) are transmitted by arthropod vectors but do not show long-term man-to-human transmission. Other diseases are primarily maintained in human populations through spillover from vertebrate reservoirs, but exercise bear witness rare (e.chiliad., hantavirus affliction and hepatitis-E infection) or inefficient (due east.g., pneumonic plague) human-to-homo transmission. Finally, some diseases are initiated by a successful ane-off zoonotic event (host-switch) with such efficacious rates of long-term human-to-human transmission that a new human pathogen is created de facto, and the original animal reservoir is no longer essential to maintaining recurring infections in humans. Many recent emerging infectious diseases have been caused by pathogens whose ancestors were maintained in vertebrate reservoirs but at present are efficiently transmitted between humans via aerosol/respiratory droplets (e.g., H1N1 flu), exchange of bodily fluids (e.chiliad., HIV/AIDS), or arthropod vectors (e.g., Zika virus fever). Although SARS-CoV-2 may also exist a virus of animate being origin, the bodily source of the virus in human populations remains enigmatic [9]. Interestingly, many modern human pathogens take zoonotic origin. One classical example of such a affliction is measles, which probably diverged from rinderpest approximately 900 years ago [x]. Additionally, human malaria caused by both Plasmodium falciparum and P. vivax is the consequence of successful historical host switching between African apes and humans [11]. Currently, macaque monkeys are a major reservoir of P. knowlesi, an of import emerging man malaria pathogen in parts of southeast Asia [12,13].

Host switching events leading to the creation of a new homo pathogen tin occur directly from the original fauna reservoir (e.grand., non-human primates in the case of HIV) or via an intermediate step with amplification/adaption (e.one thousand., recombination) in other species, including domestic animals (east.g., domestic swine for H1N1 influenza) [14]. Although whatsoever zoonotic disease tin accept serious public wellness consequences, the risk of a pandemic is profoundly enhanced after efficient man-human transmission is established. The currently high connection among human populations [15] farther facilitates the geographical spread of novel viruses, particularly respiratory syndrome diseases such every bit COVID-19 [ane]. The potential for geographical spread of novel viruses in human populations is exemplified by the emergence of respiratory syndrome diseases in the 21st century, particularly coronaviruses, such as those causing sudden acute respiratory syndrome (SARS), Heart Eastward respiratory syndrome (MERS), and COVID-nineteen (Fig 1). Epidemics of these diseases have shown rapid spatial and temporal spread. For example, SARS (2002–2003) affected countries across five continents (Africa, Asia, Australia, Europe, and Northward America), MERS (2012–2020) affected four continents (Africa, Asia, Europe, and Due north America), and COVID-nineteen has spread to all continents [1].

To mitigate the persistent threat of emerging and re-emerging diseases, several global wellness security frameworks have been established, such as the International Heath Regulations [16]. These frameworks aim to protect individuals and societies from acute public health events and to support global preparedness and responses to emerging infectious diseases [17]. For instance, in the past few decades, the Globe Health Organization (WHO) has declared six Public Health Emergencies of International Concern—health emergencies that "potentially require a coordinated international response" [16]. 5 of the six have been associated with pathogens of animal origin: the H1N1 influenza virus in 2009, Ebola virus in 2014 and 2018, Zika virus in 2016, and SARS-CoV-ii in 2020 (Fig 1). To advance the power to fight futurity pandemics, identifying the major characteristics, sources and conditions for emergence of previous diseases of fauna origin is critical. To this aim, we performed a systematic review in conjunction with a meta-analysis and spatial modeling to identify the major characteristics associated with by epidemic outbreaks of animal origin and to predict areas with high future affliction emergence gamble (details on the methods used to identify, extract, and analyze these data are described in the Supplementary Online Materials).

Discussion

Key drivers of pathogen spillover

The initial transmission of pathogens originating from animals to humans requires specific ecological barriers to be overcome (Fig ii). The manual route acts every bit an initial barrier by limiting the pathogens that humans can run into from specific vertebrate animals. Zoonotic diseases can be maintained in human populations through manual of a pathogen from a vertebrate animal host through various routes [4], including direct contact with infected animal tissues or body fluids through wounds or abraded skin; animal bites and scratches (due east.g., Brucella abortus and rabies virus); indirect contact with a contaminated environment or fomites (e.thou., Burkholderia pseudomallei and Leptospira interrogans); air-borne transmission via aerosols or grit particles (e.m., MERS-COV and H1N1 influenza viruses); oral manual (e.thousand., Toxoplasma gondii and Giardia spp.); and vector-borne manual (e.1000., Yersinia pestis and Borrelia burgdorferi). Diseases of creature origin with efficient human-to-homo manual can too initially enter the man population through any of the routes described to a higher place. However, zoonotic events introducing infections into humans may issue from unusual manual routes that differ from the normal transmission route in the animal reservoir as well as the normal manual route in humans. For example, HIV is efficiently transmitted through sexual contact among humans, but the original spillover was probable to accept occurred through repeated exposure of humans to simian immunodeficiency virus through cuts received during butchering meat or contact with the blood of infected wild primates [eighteen–20]. Similarly, plague is transmitted among rodents and from rodents to humans by flea bites or sometimes the consumption of infected meat [21,22]; however, man-human manual occurs through pneumonic manual or lice [23].

FIGURE two |

An eco-evolutionary risk assessment framework of zoonotic disease emergence.

Risk of zoonotic disease emergence (EID risk) can be viewed every bit a function of threats (the animal host and pathogen pool), vulnerabilities (the ecological barriers that pathogens need to overcome to sally in human populations) and the focal asset (i.e., homo health). To emerge a pathogen first needs to overcome manual barriers, which depend on the pathogen transmission road, and include: (A) Directly contact; (B) Indirect contact; (C) Airborne transmission; (D) Oral ingestion; (East) through bites of arthropod vectors. The pathogen then has to overcome species barriers, which can be influenced by: (F) Phylogenetic distance between the brute species and humans; (One thousand) Spatial distance between the animal species and humans; (H) Pathogen multifariousness hosted by the animal species. In each panel, the histograms betoken the overall pool of pathogen propagules hosted by the animal with pathogens with higher risk of emergence in humans being depicted past increased numbers. The zoonotic pool indicates the sample of propagule pool that can emerge in humans, and is afflicted past the overall frequency of the pathogen in the propagule pool and the pathogen'south risk of emergence.

For a novel pathogen to emerge in humans from some other vertebrate species, the pathogen must too successfully overcome the species barrier (Fig 2). Although host switching events are inherently stochastic, past zoonoses have revealed that creature species with a high take a chance of harboring potentially zoonotic pathogens are characterized past at least one of three key features. Kickoff, hosts that are phylogenetically related are more than likely to share pathogens [24–26]. Thus, not-homo primates (specifically great apes) are a major source of potential zoonotic diseases [24,27,28], and 21% of non-human primate species (77/365) have been identified every bit hosts [6] for zoonotic pathogens. This increased risk of pathogen sharing between humans and non-human primates is likely to be driven past the underlying coevolutionary relationships between primates and their pathogens [29–31].

Second, spatial overlap with humans appears to exist an even more important driver than phylogenetic proximity in influencing the extent of pathogen sharing betwixt humans and non-human primates [32]. Indeed, species in close contact with humans are more than likely to be sources of emerging zoonotic pathogens, because a higher frequency of interspecific contacts leads to greater pathogen transmission risk. High contact rates with domestic animals, which are regularly near humans, are besides expected [33]. The number of diseases that these species share with humans increases with the time after domestication [34]. Additionally, synanthropic species (e.one thousand., brown rats, Rattus norvegicus) accept been estimated to be 15 times more than likely to be sources of emerging infectious diseases than other species [35]. Critically, contempo evidence has demonstrated that hosts that tend to thrive in human being-modified landscapes also tend to harbor a higher diversity of zoonotic pathogens [36]. This relationship is likely to be driven by specific traits (e.one thousand., fast pace of life) that increment susceptibility to infection and facilitate survival in man-dominated landscapes [36].

Third, the risk of emergence of novel pathogens is expected to be greater with increasing multifariousness of the pathogens harbored by a particular species [25]. This relationship occurs considering a diverse "zoonotic pool" [37] has a college probability of harboring specific pathogen lineages that tin potentially infect humans (with or without boosted mutations). A recent written report has revealed that the zoonotic viral diversity of a particular taxonomic guild is proportional to the total viral richness, which in turn depends on the species richness of the order [31]. Thus, the 2 almost specious orders of mammals, Rodentia (2020 species) and Chiroptera (1100 species), harbor the highest proportion of zoonotic viruses [6,28,33]. Rodents and bats can transmit various viruses (due east.g., Ebola, Hendra, Nipah, and Lassa fever viruses) and bacteria (e.g., Y. pestis and Francisella tularensis). Thus, these 2 taxa are of special interest from a human disease perspective, considering of the diversity of pathogens that they harbor [28,38–45] and because they commonly are constitute in homo-modified landscapes [36].

Importantly, host and vector ecology and host physiology (e.g., immune strategies) can regulate the genetic diversity of pathogens [46] and thus the zoonotic risk posed past a host species [43,47–49]. For example, the transmission efficiency of plague (Y. pestis) appears to be affected past the bacterium'due south ability to grade a biofilm blockage in the flea gut, thus causing fleas to bite more frequently. This extended flea phenotype is caused past selection for mutations in the rpoZ gene in the bacterium under wet and common cold climate conditions [45]. Some other critical attribute affecting the "zoonotic pool" is the blazon (i.e., genetic variability) of pathogens harbored by a specific host species. For instance, the standing genetic variation (associated with population size) and mutation charge per unit of the pathogen critically affect the risk of a zoonotic event. Thus, RNA-viruses, which mutate more quickly than DNA-viruses, can adapt more chop-chop to a novel host [50,51]. Interestingly, pathogen evolution rates may themselves be affected by host immune responses, and increased selection for mutations tin can evolve under stressful environments of immunity accelerating the rate of adaptation [52,53]. For example, the stomach bacterium Helicobacter pylori produces mutation bursts during the astute phase of infection, which facilitate faster accommodation against host immunity [54].

What will drive the next pandemic of animal origin?

An understanding of past zoonoses enables informed predictions to exist made regarding where the side by side pandemic of animate being origin is likely to originate. For example, climate is recognized to critically influence illness dynamics in multiple ways. Climate tin affect the seasonal dynamics of many diseases [55,56] by influencing electric current and future pathogen [57], host [58,59], and vector [60] distributions [61–63]. Additionally, climate, in conjunction with anthropogenic disturbances, too affects host species diversity [64] and is some other critical driver of zoonotic disease spillover risk worldwide. Host species diversity affects disease risk because high pathogen diversity provides a larger genetic pool of novel pathogen lineages with the potential to spill over into human populations [65]. Thus, illness spillover has been hypothesized to be more mutual in relatively undisturbed areas of the world with high biodiversity [8,66]. Still, the preponderance of empirical testify indicates that illness spillover adventure is mostly elevated in areas with high levels of anthropogenic disturbance and thus relatively depression levels of biodiversity [5,half dozen,36,67–72].

The enhanced adventure of illness spillover in disturbed areas may exist driven by two mechanisms interim independently or in concert. Outset, anthropogenic disturbance tin increment spillover by increasing the spatial overlap between wildlife and humans, as humans invade natural habitats or wild species invade anthropogenic habitats [73,74]. Second, human being disturbance can affect illness adventure by negatively influencing biodiversity—a response termed the "dilution effect," which occurs because diversity in many systems increases the proportion of hosts with depression pathogen competence, thus "diluting" the adventure of infection beyond the entire host customs [75,76]. Although not universal [77,78], recent meta-analyses have revealed wide testify of the dilution effect in many host-pathogen systems [79,fourscore] and at multiple spatial scales [81]. Critically, both species richness and composition are probable to play roles in disease spillover dynamics [36]. For example, anthropogenic disturbance can pb to the biotic homogenization of natural communities in which many highly specialized species are replaced by several widespread generalists [82,83], because generalist species are relatively less sensitive to disturbance and tend to exist "r-selected" (i.e., their populations are governed past their reproductive ability) [73,84]. Additionally, rapid reproduction favors the epidemic spread of disease, because a constant supply of susceptible individuals hinders adequate herd immunity in these populations [85]. Importantly, as described above, generalist species that are more than likely to invade anthropogenic habitats may also be more competent hosts for pathogens [86], particularly zoonotic pathogens [36,72,87].

At finer spatial scales (i.e., at the private host level), host switching, as with any invasion process, is facilitated past propagule pressure [88,89], and the affliction spillover risk increases as interspecific contacts increase. In such situations, ample opportunities exist for spillover infections that originate in the reservoir host (off-the-shelf) or that successfully adapt to humans and thus undergo a true host-switch (i.eastward., tailor-fabricated) [90]. Consequently, commercial farms housing many animals in restricted spaces can be major sources of novel pathogens [91]. For case, the 2009 "swine flu" epidemic was caused by a novel influenza virus (H1N1) that was a product of reassortment amidst three viruses (H3N2, H1N2, and Eurasian avian-like swine viruses) circulating in domestic pigs [14]. As large-scale commercial animal operations increase globally, these "melting pots" are likely to go along to be major sources of novel pathogens [92]. High spillover risk besides exists at alive-beast markets (often referred to as "moisture markets"), which sell wild and/or domestic animals [93,94]. The recent SARS epidemics associated with novel coronaviruses (SARS-CoV-ane in 2002–2003 and SARS-CoV-2 in 2019–2021) have been suspected to be associated with such markets in China at the kickoff of the outbreaks [93,95,96]. Notwithstanding, solid prove of the specific sources remains elusive [97]. Although SARS-CoV-2 itself does not appear to exist a recombinant of any currently known sarbecoviruses [98], coronaviruses by and large do show high recombination rates [99], and such viral recombination tin can increase the risk of emergence of novel zoonotic pathogens. Consequently, the real run a risk associated with live-fauna markets might exist that they provide opportunities for viruses, particularly generalist viruses, from unlike animals to meet and recombine, thus enhancing the gamble of emergence of novel viruses.

Future countermeasures

Most emerging and novel zoonoses are due to stochastic host switching (or spillover) events that are inherently unpredictable. Therefore, numerous challenges exist in understanding the emergence and control of diseases of animal origin (Box 1). Preventing spillover into human populations will primarily depend on establishing the association betwixt eco-epidemiological contexts and transmission mechanisms. We contend that the prevention of future pandemics must be based on a holistic approach comprising the following countermeasures:

  1. Establish eco-epidemiological contexts: Spillover events are inherently stochastic and unpredictable, given the complex eco-epidemiological contexts in which diseases are transmitted via multiple mechanisms and are modulated by various drivers. In this example, clarifying the eco-epidemiological contexts in which these stochastic events are almost likely to occur is a key scientific countermeasure. As indicated in a higher place, the development of a pandemic episode is highly associated with a sequential probability of pathogen-human see, infection, and transmission. These probabilities are essentially determined by several factors that modulate human exposure to novel pathogens. Amongst these factors, agricultural intensification dramatically increases disease emergence risk in human populations through the increased use of chemicals (due east.chiliad., antibiotics, pesticides, and fertilizer), changes in land use (e.g., conversion of forest to agronomical or pastural lands), and increased contact between humans and domestic animals. Indeed, agricultural drivers have been estimated to be associated with approximately 25% of all diseases and fifty% of zoonotic diseases that accept emerged in human populations [3]. Understanding the complex and interacting effects of such eco-epidemiological drivers in affecting disease spillover risk is of import, and modern modeling approaches can provide robust predictive risk cess frameworks [100,101]. Additionally, recent advances in model-inference frameworks are expected to substantially contribute to contextualizing disease dynamics in diverse eco-epidemiological settings and to provide powerful assessment tools to identify regions with loftier affliction spillover gamble [102,103].

  2. Scale up surveillance at human-animal interface: Scaling up active surveillance at human-domestic creature interface, with a focus on high-hazard human populations (e.g., veterinarians, subcontract workers, and workers in dairy or meat processing plants), is critical to rapidly identify spillover events. With respect to wildlife, the selection of species and locations for surveillance may be more challenging. Kress et al. [104] have argued that, with the advent of modern genomic tools, merely a small fraction of the resources allocated to suppressing COVID-19 would be needed to identify every zoonotic pathogen hosted past birds and mammals. However, surveillance efforts are likely to need to exist focused in terms of both the species surveyed and the geographic regions targeted. We propose that species could be targeted according to underlying ecological traits that bear upon their potential to harbor zoonotic pathogens. For example, in wild mammals, three variables are significantly associated with a species harboring at least one zoonotic pathogen, as explained above: the phylogenetic proximity to humans, the spatial overlap between the species distribution and human populations, and the diversity of non-man pathogens that the species harbors (Fig 3A). This framework should enable the identification of species that accept a loftier likelihood of harboring zoonotic or potentially zoonotic pathogens but are poorly surveilled. Unfortunately, a disquisitional weakness in the to a higher place approach is that the number of host species with good data on pathogen variety remains limited. This limitation could be addressed through modeling approaches using phylogenetic data to predict zoonotic pathogen risk in poorly surveyed species, on the basis of information from well surveyed species (for example, ref. [36]). Alternatively, wildlife surveillance programs could besides focus on specific eco-geographic areas according to the chance of transmission of pathogens between wild animals and humans. One way to effectively target geographic areas for surveillance is to prioritize them according to both the diverseness of hosts known to harbor zoonotic pathogens and human density. Thus, for mammals, poorly surveyed areas in eastern and southeastern Asia would take college priority than poorly surveyed areas in Australia (Fig 3B). Additionally, this framework could also help inform which taxa should be prioritized in unlike geographic regions (Fig 3C-F). For example, this framework indicates a need to prioritize the surveillance of bats beyond much of India and Prc. Critically, as in previous studies [5,36], our framework emphasizes the need to focus surveillance on global regions undergoing rapid land-utilise change. In many cases, these regions are too the most socio-economic challenged and therefore the virtually vulnerable to the effects of outbreaks [8]. Recently, researchers take advocated for a "pandemic interception" platform to proactively address pandemic risks, consisting of global genomics-based bio-surveillance programs [104], such as the Earth BioGenome Projection, the Global Virome Projection, BIOSCAN, and the PREDICT project [105,106]. Critically, the interaction of these international programs with regional programs focusing on biodiversity and ecological change (e.g., Mexico's Commission for Biodiversity) tin help develop a global surveillance synergy well poised to accost the urgent need for proactive measures, in low-cal of the pandemic risks in the Anthropocene.

  3. Reduce spillover frequency: The current arroyo to combat zoonotic pandemics is reactive, focusing on successful host switching events (i.east., pathogens that have already emerged in the homo population). Withal, successful host switching events represent merely a small-scale proportion of the preceding unsuccessful host switching opportunities. Thus, a more proactive approach to preventing futurity pandemics would be to subtract host switching opportunities by shifting focus toward interrupting animal-human spillover and subsequent transmission chains. The successful interruption of such transmission chains critically depends on decreasing the contact rates betwixt humans and zoonotic reservoirs, on the basis of a better understanding of illness environmental and pathogen transmission dynamics. For example, to decrease the risk of spillover of pathogens transmitted by straight contact or droplets transmission, focus must be placed on high-run a risk locations where close contact betwixt humans and potentially infected animal tissue or alive animals is common (e.1000., locations where hunted wildlife are trafficked or traded, live animal markets, or high-intensity commercial livestock farms) [74,92,107]. Alternatively, in the example of orally transmitted diseases, attention should be focused on populations at high risk of exposure to these pathogens, such as local communities that consume bush meat [108–111]. Finally, integrated vector management (e.one thousand., WHO's Global Vector Command Response 2017–2030) remains a key strategy to disrupt the manual, and thus combat the ever-increasing burden, of vector borne diseases [112–114].

  4. Decrease epidemic potential: For newly emerging infectious diseases, identification of the pathogen and manual routes remain critical for constructive epidemic control. Although the identification of the animal source of a pathogen is disquisitional to prevent future spillover events, it often is a highly challenging undertaking [115]. For example, more than xl years afterwards the discovery of the Ebola virus, the actual natural reservoir remains unknown, although strong evidence supports the interest of bats [116]. For the SARS outbreak in 2002–2003, researchers took several months to identify the pathogen just did not identify the potential source for more than a decade [117]. For the COVID-nineteen pandemic, in 2019–2020, scientists took but several weeks to identify the pathogen, and have identified horseshoe bats as a potential source of the ancestral virus; other intermediate host(s) are suspected only remain unconfirmed [97]. In many cases, the potential source of novel pathogens has been identified through spatial associations. For example, live creature markets selling domesticated species have been identified every bit sources of numerous pathogens in humans (e.g., swine-origin flu A viruses) [118]. However, the risks of novel zoonoses are particularly high in live animal markets that sell wildlife, because these markets bring humans and wild animals into proximity, frequently under conditions of poor hygiene [106,119]. In the case of the recent SARS-CoV-2 outbreak, the Chinese Center for Disease Command and Prevention detected SARS-CoV-two RNA in 33 of 585 environmental samples from the Huanan Seafood Market in Wuhan. Moreover, 93.9% (31/33) of the positive samples were from the western end of the market, where booths selling wildlife were concentrated [120]. However, the exact role of wildlife in maintaining or amplifying the virus in the Huanan Seafood Market remains unclear; for example, the market environment might accept amplified the pathogen subsequently it had already entered the human population [121]. Given the existent risks of novel zoonoses entering homo populations through live animate being markets selling wild animals, governments worldwide must decrease the nutritional dependency of local populations on meat procured from wild animals and ban the merchandise of wildlife species [122]. The regulation of live creature markets must as well be improved to subtract the risks of zoonotic disease transmission by segregating live animals of unlike species from 1 another and from humans, improving slaughter techniques to meet international standards of ideals and safety, and improving sanitation and hygiene [107,123]. Still, until these biosecurity measures are in place, improved surveillance of potentially loftier-take chances locations, such every bit alive animal markets, will be disquisitional [122].

    Genetic and genomic analyses have demonstrated highly efficient in surveillance, and the identification of origins and routes for the spread of pathogens [110,124,125]. Surveillance of known pathogens is easily performed with PCR tests (to find ongoing infections) or antibiotic-based tests (to test for past infections) in the human population. Because viruses and leaner have small genomes, complete genomic studies of many samples tin exist performed at loftier speed and depression cost with NGS techniques [110,126]. This capability has provided unprecedented access to detailed information on the origin, migratory routes, and critical mutations, all of which are crucial for understanding the changes in pathogen transmission efficiency [110]. Genomic information tin also be effectively leveraged to develop improved diagnostics (due east.one thousand., PCR-based assays) and control measures (e.m., vaccines) [127]. Genomics has provided an unparalleled ability to place the causative agents of by pandemics through emerging ancient Deoxyribonucleic acid approaches [128], as well equally to finer track affliction outbreaks, better empathise manual chains and elucidate population dynamics, as seen in the COVID-19 pandemic [129].

  5. Meliorate time to come preventive measures: Effective inter-sectoral collaboration and mutual benefits of joint actions of international communities with respect to the Sustainable Development Goals tin be leveraged for constructive preparedness and response to epidemics. A particularly urgent need exists for global governments to recognize the value of biodiversity protection in pandemic prevention [130]. Consideration of environmental determinants, climate changes and related risks to man health, and ecosystem integrity and relevant direction systems will exist critical. In proactively addressing future emergencies, a disquisitional need exists to understand that human being health is inextricably associated with animal health, equally well every bit ecosystem structure and role (eastward.g., OneHealth). Thus, cross-sector collaboration must exist strengthened, specially as it relates to emergency preparedness and response, including the harmonized translation of policy guidance (WHO, OIE, and FAO) into action. Specific programs such as the Global Virome Project and BIOSCAN (described to a higher place) are examples of such collaborations. International collaboration is also highly of import for source tracing [131]. For example, in the 2002–2003 SARS epidemic, civets were initially suspected as the source; however, continual international collaborations determined that the source of SARS-CoV was most probable to be bats [117]. COVID-xix is a disease currently straining international political relationships and economic development, and international and multi-disciplinary collaborative teams are urgently needed to mitigate the pandemic's effects, such as the team mobilized past the WHO to place the source of SARS-CoV-2 [121]. The unprecedented rapid response to SARS-CoV-two has demonstrated that international collaborations have facilitated the 2 pillars of disease direction: non-pharmaceutical interventions and vaccine development. Non-pharmaceutical interventions, such as case isolation, contact tracing, travel restrictions, and cancellation of mass gatherings, were crucial in the early response to the rapid diffusion of the pandemic [132–136]. These measures have collectively decreased the manual, and the fourth dimension required for vaccine development and for designing general intervention frameworks [137] and prototypical pathogen approaches [138] to pandemic preparedness. Indeed, as the hazard of zoonotic disease emergence increases globally, an urgent need remains for strategies to forbid future zoonotic pandemics. Such strategies volition crave an interdisciplinary inquiry agenda, as well as robust intra- and international collaboration at the interface of science, policy and society.

BOX 1 | Major challenges relating to the emergence and control of diseases of beast origin.

I. Structure and dynamics of disease systems: For all systems, the following must be better understood:

  1. The combined roles of diverse drivers of global change (e.g., climate, land use, global transport, and socio-economical factors) on zoonotic risks, particularly in landscapes undergoing rapid climatic (due east.chiliad., high elevation areas) and/or habitat (e.chiliad., peri-urban areas) modifications.

  2. The relative pandemic potential of endemic pathogens (i.e., emergence driven by local country-employ and/or socio-economic factors) vs. exotic pathogens (i.e., emergence driven past alterations in global send and/or altered distribution due to climate change).

  3. How the interaction betwixt host and pathogen diversity affects disease gamble across ecological systems and spatial scales. For instance, exercise macroecological differences in host and/or pathogen diverseness beyond ecosystems bear on infection gamble in like ways to human-mediated alterations in biodiversity inside ecosystems?

  4. How do the population size and density of hosts and pathogens influence the emergence of new host-pathogen combinations, and what are the relative effects of human population density vs. altered host community construction in anthropogenic habitats?

2. Surveillance and command: For all zoonotic systems, the following must exist developed:

  1. Effective surveillance efforts directed at both at-risk human populations and high-risk animal populations

  2. Reliable techniques to identify "competent" vs. "non-competent" hosts of zoonotic pathogens in a community, and better frameworks to narrate how community competence varies with human-mediated changes to the environment

  3. Optimal measures to minimize zoonotic disease emergence (due east.m., ban of wildlife sale and improved sanitation in live-animal markets) and spread (e.g., contact tracing and improved border control), respecting socio-cultural norms and economical needs at the local and global scales

Figure 3 |

A framework to prioritize species and geographical areas for zoonotic disease surveillance.

(a) The likelihood of a wildlife species being a zoonotic host (equally measured past the binomial odds ratio) significantly depends on various species characteristics, including the phylogenetic distance betwixt the animal species and humans (Phylogeny), hazard of spatial overlap betwixt the host species and humans (Spatial) and the richness of the pathogen community hosted by the species (Patho. Rich.). Analyses restricted to mammalian species simply and error bars are 67% (red lines) and 95% (black lines) quantiles obtained from non-parametric bootstrap or Bayesian regression analyses (see Supplementary Online Methods for details). (b) Zoonotic disease emergence adventure depends on the diversity of hosts that harbor zoonotic pathogens and the density of humans in the area. The map shows the joint distribution of zoonotic mammalian host diverseness and human being population density. Areas with high diversity of zoonotic hosts and high human density (black areas) need to exist prioritized over those with simply high zoonotic host multifariousness (light light-green areas) or high human being density (light blue areas), which in plough need to exist prioritized over areas with low zoonotic host diversity and human density (low-cal cyan areas). Priority areas for surveillance also depend on the specific mammalian orders considered. Maps are shown for four major orders that accept loftier numbers of zoonotic hosts: (c) Non-homo primates; (d) Rodentia; (eastward) Chiroptera; (f) Carnivora. Encounter Supplemental Material for details.

The authors declare they have no actual or potential competing interests.

  1. WHO. Coronavirus illness (COVID-19) pandemic. Geneva, Switzerland: WHO. 2020 cited 2020 June 27, 2020 https://www.who.int/emergencies/diseases/novel-coronavirus-2019

  2. malERA Refresh Consultative Panel on Insecticide and Drug Resistance. malERA: An updated enquiry calendar for insecticide and drug resistance in malaria elimination and eradication. PLoS Med. 2017. Vol. 14(11):e1002450

  3. Rohr JR, Barrett CB, Civitello DJ, Craft ME, Delius B, DeLeo GA, et al.. Emerging man infectious diseases and the links to global nutrient production. Nat Sustain. 2019. Vol. 2(half-dozen):445–456

  4. Loh EH, Zambrana-Torrelio C, Olival KJ, Bogich TL, Johnson CK, Mazet JA, et al.. Targeting transmission pathways for emerging zoonotic disease surveillance and control. Vector Borne Zoonotic Dis. 2015. Vol. 15(seven):432–437

  5. Allen T, Murray KA, Zambrana-Torrelio C, Morse SS, Rondinini C, Di Marco M, et al.. Global hotspots and correlates of emerging zoonotic diseases. Nat Commun. 2017. Vol. 8(1):1124

  6. Han BA, Kramer AM, Drake JM. Global patterns of zoonotic affliction in mammals. Trends Parasitol. 2016. Vol. 32(7):565–577

  7. Nunez MA, Pauchard A, Ricciardi A. Invasion Scientific discipline and the Global Spread of SARS-CoV-2. Trends Ecol Evol. 2020. Vol. 35(8):642–645

  8. Jones KE, Patel NG, Levy MA, Storeygard A, Balk D, Gittleman JL, et al.. Global trends in emerging infectious diseases. Nature. 2008. Vol. 451(7181):990–993

  9. Haider N, Rothman-Ostrow P, Osman AY, Arruda LB, Macfarlane-Berry L, Elton L, et al.. COVID-19 – Zoonosis or emerging communicable diseases? Front Public Health. 2020. Vol. 8:596944

  10. Furuse Y, Suzuki A, Oshitani H. Origin of measles virus: difference from rinderpest virus between the 11th and 12th centuries. Virol J. 2010. Vol. seven:52

  11. Loy DE, Liu W, Li Y, Learn GH, Plenderleith LJ, Sundararaman SA, et al.. Out of Africa: origins and evolution of the man malaria parasites Plasmodium falciparum and Plasmodium vivax. Int J Parasitol. 2017. Vol. 47(two-3):87–97

  12. Antinori S, Galimberti Fifty, Milazzo Fifty, Corbellino Thou. Plasmodium knowlesi: the emerging zoonotic malaria parasite. Acta Trop. 2013. Vol. 125(2):191–201

  13. Cooper DJ, Rajahram GS, William T, Jelip J, Mohammad R, Bridegroom J, et al.. Plasmodium knowlesi Malaria in Sabah, Malaysia, 2015–2017: ongoing increment in incidence despite near-elimination of the man-only plasmodium species. Clin Infect Dis. 2020. Vol. 70(three):361–367

  14. Neumann Thou, Noda T, Kawaoka Y. Emergence and pandemic potential of swine-origin H1N1 flu virus. Nature. 2009. Vol. 459(7249):931–939

  15. Kraemer MUG, Yang CH, Gutierrez B, Wu CH, Klein B, Pigott DM, et al.. The effect of man mobility and command measures on the COVID-nineteen epidemic in People's republic of china. Science. 2020. Vol. 368(6490):493–497

  16. WHO. International Health Regulations. Geneva, Switzerland: World Health Organisation. 2008

  17. Flahault A, Wernli D, Zylberman P, Tanner One thousand. From global wellness security to global health solidarity, security and sustainability. Bull World Health Organ. 2016. Vol. 94(12):863

  18. Hahn BH, Shaw GM, De Erect KM, Sharp PM. AIDS as a zoonosis: scientific and public wellness implications. Science. 2000. Vol. 287(5453):607–614

  19. Holmes EC. On the origin and evolution of the homo immunodeficiency virus (HIV). Biol Rev Camb Philos Soc. 2001. Vol. 76(2):239–254

  20. Peeters Thou, Courgnaud Five, Abela B, Auzel P, Pourrut X, Bibollet-Ruche F, et al.. Risk to human health from a plethora of simian immunodeficiency viruses in primate bushmeat. Emerg Infect Dis. 2002. Vol. eight(5):451–457

  21. Arbaji A, Kharabsheh South, Al-Azab S, Al-Kayed One thousand, Amr ZS, Abu Baker M, et al.. A 12-case outbreak of pharyngeal plague following the consumption of camel meat, in north-eastern Jordan. Ann Trop Med Parasitol. 2005. Vol. 99(8):789–793

  22. Bin Saeed AA, Al-Hamdan NA, Fontaine RE. Plague from eating raw camel liver. Emerg Infect Dis. 2005. Vol. eleven(ix):1456–1457

  23. Dean KR, Krauer F, Walloe 50, Lingjaerde OC, Bramanti B, Stenseth NC, et al.. Human ectoparasites and the spread of plague in Europe during the Second Pandemic. Proc Natl Acad Sci U S A. 2018. Vol. 115(6):1304–1309

  24. Pedersen AB, Davies TJ. Cross-species pathogen manual and disease emergence in primates. Ecohealth. 2009. Vol. half-dozen(4):496–508

  25. Wolfe ND, Dunavan CP, Diamond J. Origins of major human infectious diseases. Nature. 2007. Vol. 447(7142):279–283

  26. Shaw LP, Wang Advert, Dylus D, Meier M, Pogacnik Yard, Dessimoz C, et al.. The phylogenetic range of bacterial and viral pathogens of vertebrates. Mol Ecol. 2020. Vol. 29(17):3361–3379

  27. Gomez JM, Nunn CL, Verdu M. Centrality in primate-parasite networks reveals the potential for the transmission of emerging infectious diseases to humans. Proc Natl Acad Sci U S A. 2013. Vol. 110(xix):7738–7741

  28. Olival KJ, Hosseini PR, Zambrana-Torrelio C, Ross North, Bogich TL, Daszak P. Host and viral traits predict zoonotic spillover from mammals. Nature. 2017. Vol. 546(7660):646–650

  29. Nunn CL, Altizer S, Sechrest W, Jones KE, Barton RA, Gittleman JL. Parasites and the evolutionary diversification of primate clades. Am Nat. 2004. Vol. 164 Suppl five:S90–S103

  30. Garamszegi LZ. Patterns of co-speciation and host switching in primate malaria parasites. Malar J. 2009. Vol. eight:110

  31. Mollentze N, Streicker DG. Viral zoonotic adventure is homogenous among taxonomic orders of mammalian and avian reservoir hosts. Proc Natl Acad Sci U S A. 2020. Vol. 117(17):9423–9430

  32. Davies TJ, Pedersen AB. Phylogeny and geography predict pathogen community similarity in wild primates and humans. Proc Biol Sci. 2008. Vol. 275(1643):1695–1701

  33. Johnson CK, Hitchens PL, Pandit PS, Rushmore J, Evans TS, Young CCW, et al.. Global shifts in mammalian population trends reveal key predictors of virus spillover take chances. Proc Biol Sci. 2020. Vol. 287(1924):20192736

  34. Morand South, McIntyre KM, Baylis G. Domesticated animals and human infectious diseases of zoonotic origins: domestication time matters. Infect Genet Evol. 2014. Vol. 24:76–81

  35. McFarlane R, Sleigh A, McMichael T. Synanthropy of wild mammals as a determinant of emerging infectious diseases in the Asian-Australasian region. Ecohealth. 2012. Vol. nine(1):24–35

  36. Gibb R, Redding DW, Chin KQ, Donnelly CA, Blackburn TM, Newbold T, et al.. Zoonotic host diverseness increases in human-dominated ecosystems. Nature. 2020. Vol. 584:398–402

  37. Morse SS. Factors and determinants of illness emergence. Rev Sci Tech. 2004. Vol. 23(two):443–451

  38. Luis AD, Hayman DT, O'Shea TJ, Cryan PM, Gilbert AT, Pulliam JR, et al.. A comparison of bats and rodents as reservoirs of zoonotic viruses: are bats special? Proc Biol Sci. 2013. Vol. 280(1756):20122753

  39. Turmelle AS, Olival KJ. Correlates of viral richness in bats (club Chiroptera). Ecohealth. 2009. Vol. 6(4):522–539

  40. Han BA, Park AW, Jolles AE, Altizer S. Infectious affliction transmission and behavioural allometry in wild mammals. J Anim Ecol. 2015. Vol. 84(3):637–646

  41. Hahn MB, Jarnevich CS, Monaghan AJ, Eisen RJ. Modeling the Geographic Distribution of Ixodes scapularis and Ixodes pacificus (Acari: Ixodidae) in the Contiguous United States. J Med Entomol. 2016. Vol. 53(5):1176–1191

  42. Beck CE, Dobson AP. Bats as 'special' reservoirs for emerging zoonotic pathogens. Trends Microbiol. 2015. Vol. 23(three):172–180

  43. Bordes F, Blasdell Chiliad, Morand Southward. Transmission ecology of rodent-borne diseases: new frontiers. Integr Zool. 2015. Vol. x(5):424–435

  44. Guy C, Thiagavel J, Mideo N, Ratcliffe JM. Phylogeny matters: revisiting 'a comparing of bats and rodents as reservoirs of zoonotic viruses'. R Soc Open Sci. 2019. Vol. half dozen(two):181182

  45. Cui Y, Schmid BV, Cao H, Dai Ten, Du Z, Ryan Easterday W, et al.. Evolutionary choice of biofilm-mediated extended phenotypes in Yersinia pestis in response to a fluctuating surroundings. Nat Commun. 2020. Vol. 11(1):281

  46. Tian H, Cui Y, Dong L, Zhou S, Li Ten, Huang S, et al.. Spatial, temporal and genetic dynamics of highly pathogenic avian flu A (H5N1) virus in Mainland china. BMC Infect Dis. 2015. Vol. 15:54

  47. Mandl JN, Ahmed R, Barreiro LB, Daszak P, Epstein JH, Virgin HW, et al.. Reservoir host immune responses to emerging zoonotic viruses. Cell. 2015. Vol. 160(1-ii):xx–35

  48. Bordes F, Caron A, Blasdell Chiliad, de Garine-Wichatitsky M, Morand South, du Toit J. Forecasting potential emergence of zoonotic diseases in Southward-Eastern asia: network analysis identifies key rodent hosts. J Appl Ecol. 2016. Vol. 54(iii):691–700

  49. Morand S, Blasdell 1000, Bordes F, Buchy P, Carcy B, Chaisiri Yard, et al.. Changing landscapes of Southeast Asia and rodent-borne diseases: decreased diversity but increased transmission risks. Ecol Appl. 2019. Vol. 29(4):e01886

  50. Moya A, Holmes EC, Gonzalez-Candelas F. The population genetics and evolutionary epidemiology of RNA viruses. Nat Rev Microbiol. 2004. Vol. 2(4):279–288

  51. Garcia-Sastre A, Richt JA. Editorial overview: emerging viruses: interspecies transmission: await the unexpected. Curr Opin Virol. 2019. Vol. 34:iii–vi

  52. Galhardo RS, Hastings PJ, Rosenberg SM. Mutation as a stress response and the regulation of evolvability. Crit Rev Biochem Mol Biol. 2007. Vol. 42(5):399–435

  53. Kang JM, Iovine NM, Blaser MJ. A paradigm for direct stress-induced mutation in prokaryotes. FASEB J. 2006. Vol. 20(fourteen):2476–2485

  54. Linz B, Windsor HM, McGraw JJ, Hansen LM, Gajewski JP, Tomsho LP, et al.. A mutation outburst during the acute phase of Helicobacter pylori infection in humans and rhesus macaques. Nat Commun. 2014. Vol. 5:4165

  55. Olsen B, Munster VJ, Wallensten A, Waldenstrom J, Osterhaus AD, Fouchier RA. Global patterns of flu a virus in wild birds. Science. 2006. Vol. 312(5772):384–348

  56. Martinez ME. The calendar of epidemics: Seasonal cycles of infectious diseases. PLoS Pathog. 2018. Vol. 14(11):e1007327

  57. Stenseth NC, Samia NI, Viljugrein H, Kausrud KL, Begon Thou, Davis S, et al.. Plague dynamics are driven by climate variation. Proc Natl Acad Sci U S A. 2006. Vol. 103(35):13110–131105

  58. Ostfeld RS, Canham CD, Oggenfuss K, Winchcombe RJ, Keesing F. Climate, deer, rodents, and acorns as determinants of variation in lyme-illness risk. PLoS Biol. 2006. Vol. 4(6):e145

  59. Hjelle B, Drinking glass GE. Outbreak of hantavirus infection in the Four Corners region of the United states of america in the wake of the 1997-1998 El Nino-southern oscillation. J Infect Dis. 2000. Vol. 181(5):1569–1573

  60. Ogden NH. Climate change and vector-borne diseases of public health significance. FEMS Microbiol Lett. 2017. Vol. 364(19)

  61. Tjaden NB, Caminade C, Beierkuhnlein C, Thomas SM. Mosquito-Borne Diseases: Advances in Modelling Climate-Change Impacts. Trends Parasitol. 2018. Vol. 34(3):227–245

  62. Kraemer MUGG, Hay SI, Pigott DM, Smith DL, Wint GRW, Golding North. Progress and Challenges in Infectious Affliction Cartography. Trends in Parasitology. 2016. Vol. 32:19–29

  63. Messina JP, Brady OJ, Pigott DM, Golding N, Kraemer MUG, Scott TW, et al.. The many projected futures of dengue. Nat Rev Microbiol. 2015. Vol. 13:230–239

  64. Dirzo R, Young HS, Galetti M, Ceballos G, Isaac NJ, Collen B. Defaunation in the Anthropocene. Science. 2014. Vol. 345(6195):401–406

  65. Wolfe ND, Daszak P, Kilpatrick AM, Burke DS. Bushmeat hunting, deforestation, and prediction of zoonoses emergence. Emerg Infect Dis. 2005. Vol. 11(12):1822–1827

  66. Rogalski MA, Gowler CD, Shaw CL, Hufbauer RA, Duffy MA. Homo drivers of ecological and evolutionary dynamics in emerging and disappearing infectious affliction systems. Philos Trans R Soc Lond Ser B Biol Sci. 2017. Vol. 372(1712):20160043

  67. Han BA, Schmidt JP, Bowden SE, Drake JM. Rodent reservoirs of time to come zoonotic diseases. Proc Natl Acad Sci U S A. 2015. Vol. 112(22):7039–7044

  68. Hosseini PR, Mills JN, Prieur-Richard AH, Ezenwa VO, Bailly 10, Rizzoli A, et al.. Does the bear upon of biodiversity differ between emerging and endemic pathogens? The need to separate the concepts of take chances and risk. Philos Trans R Soc Lond B Biol Sci. 2017. Vol. 372(1722):20160129

  69. Plowright RK, Foley P, Field HE, Dobson AP, Foley JE, Eby P, et al.. Urban habituation, ecological connectivity and epidemic dampening: the emergence of Hendra virus from flying foxes (Pteropus spp.). Proc Biol Sci. 2011. Vol. 278(1725):3703–3712

  70. Muyembe-Tamfum JJ, Mulangu S, Masumu J, Kayembe JM, Kemp A, Paweska JT. Ebola virus outbreaks in Africa: by and present. Onderstepoort J Vet Res. 2012. Vol. 79(2):451

  71. Pulliam JR, Epstein JH, Dushoff J, Rahman SA, Bunning M, Jamaluddin AA, et al.. Agricultural intensification, priming for persistence and the emergence of Nipah virus: a lethal bat-borne zoonosis. J R Soc Interface. 2012. Vol. 9(66):89–101

  72. Keesing F, Ostfeld RS. Impacts of biodiversity and biodiversity loss on zoonotic diseases. Proc Natl Acad Sci U S A. 2021. Vol. 118(17):e2023540118

  73. Hassell JM, Begon M, Ward MJ, Fevre EM. Urbanization and disease emergence: dynamics at the wild animals-livestock-human being interface. Trends Ecol Evol. 2017. Vol. 32(1):55–67

  74. Magouras I, Brookes VJ, Jori F, Martin A, Pfeiffer DU, Durr Due south. Emerging zoonotic diseases: should nosotros rethink the animal-human interface? Front Vet Sci. 2020. Vol. 7:582743

  75. LoGiudice K, Ostfeld RS, Schmidt KA, Keesing F. The ecology of infectious illness: effects of host diverseness and customs composition on Lyme affliction hazard. Proc Natl Acad Sci U S A. 2003. Vol. 100(2):567–571

  76. Keesing F, Belden LK, Daszak P, Dobson A, Harvell CD, Holt RD, et al.. Impacts of biodiversity on the emergence and manual of infectious diseases. Nature. 2010. Vol. 468:647–652

  77. Randolph SE, Dobson AD. Pangloss revisited: a critique of the dilution effect and the biodiversity-buffers-illness paradigm. Parasitology. 2012. Vol. 139(vii):847–863

  78. Salkeld DJ, Padgett KA, Jones JH. A meta-analysis suggesting that the human relationship betwixt biodiversity and adventure of zoonotic pathogen transmission is idiosyncratic. Ecol Lett. 2013. Vol. 16(5):679–686

  79. Civitello DJ, Cohen J, Fatima H, Halstead NT, Liriano J, McMahon TA, et al.. Biodiversity inhibits parasites: Broad evidence for the dilution outcome. Proc Natl Acad Sci U South A. 2015. Vol. 112(28):8667–8671

  80. Halliday FW, Rohr JR. Measuring the shape of the biodiversity-disease relationship across systems reveals new findings and primal gaps. Nat Commun. 2019. Vol. ten(i):5032

  81. Magnusson 1000, Fischhoff IR, Ecke F, Hornfeldt B, Ostfeld RS. Effect of spatial calibration and latitude on variety-disease relationships. Ecology. 2020. Vol. 101(3):e02955

  82. McKinney ML, Lockwood JL. Biotic homogenization: a few winners replacing many losers in the side by side mass extinction. Trends Ecol Evol. 1999. Vol. 14(11):450–453

  83. Newbold T, Hudson LN, Contu S, Colina SLL, Beck J, Liu Y, et al.. Widespread winners and narrow-ranged losers: land use homogenizes biodiversity in local assemblages worldwide. PLoS Biol. 2018. Vol. 16(12):e2006841

  84. Ostfeld RS, Keesing F. Species that tin can make us ill thrive in human habitats. Nature. 2020. Vol. 584:346–347

  85. Metcalf CJE, Ferrari G, Graham AL, Grenfell BT. Understanding herd amnesty. Trends Immunol. 2015. Vol. 36(12):753–755

  86. Johnson PT, Preston DL, Hoverman JT, Richgels KL. Biodiversity decreases disease through predictable changes in host customs competence. Nature. 2013. Vol. 494(7436):230–233

  87. Ostfeld RS, Levi T, Jolles AE, Martin LB, Hosseini PR, Keesing F. Life History and demographic drivers of reservoir competence for three tick-borne zoonotic pathogens. PLoS One. 2014. Vol. 9:e107387

  88. Hatcher MJ, Dick JTA, Dunn AM. Illness emergence and invasions. Funct Ecol. 2012. Vol. 26(half-dozen):1275–87

  89. Ogden NH, Wilson JRU, Richardson DM, Hui C, Davies SJ, Kumschick S, et al.. Emerging infectious diseases and biological invasions: a telephone call for a One Wellness collaboration in science and direction. R Soc Open Sci. 2019. Vol. 6(3):181577

  90. Pepin KM, Lass S, Pulliam JR, Read AF, Lloyd-Smith JO. Identifying genetic markers of adaptation for surveillance of viral host jumps. Nat Rev Microbiol. 2010. Vol. viii(11):802–813

  91. Jones BA, Grace D, Kock R, Alonso S, Rushton J, Said MY, et al.. Zoonosis emergence linked to agricultural intensification and environmental alter. Proc Natl Acad Sci U S A. 2013. Vol. 110(21):8399–8404

  92. Hollenbeck JE. Interaction of the role of concentrated animal feeding operations (CAFOs) in emerging infectious diseases (EIDS). Infect Genet Evol. 2016. Vol. 38:44–46

  93. Webster RG. Wet markets—a continuing source of severe acute respiratory syndrome and influenza? Lancet. 2004. Vol. 363(9404):234–236

  94. Bachand N, Ravel A, Onanga R, Arsenault J, Gonzalez JP. Public wellness significance of zoonotic bacterial pathogens from bushmeat sold in urban markets of Gabon, Primal Africa. J Wildl Dis. 2012. Vol. 48(three):785–789

  95. Zhu North, Zhang D, Wang W, Li X, Yang B, Song J, et al.. A novel coronavirus from patients with pneumonia in China, 2019. North Engl J Med. 2020. Vol. 382(8):727–733

  96. Li J, Li JJ, Xie Ten, Cai Ten, Huang J, Tian X, et al.. Game consumption and the 2019 novel coronavirus. Lancet Infect Dis. 2020. Vol. 20(three):275–276

  97. Stenseth NC, Dharmarajan G, Li R, Shi ZL, Yang R, Gao GF. Lessons learnt from the COVID-nineteen pandemic. Front end Public Health. 2021. Vol. ix:694705

  98. Boni MF, Lemey P, Jiang X, Lam TT, Perry BW, Castoe TA, et al.. Evolutionary origins of the SARS-CoV-2 sarbecovirus lineage responsible for the COVID-19 pandemic. Nat Microbiol. 2020. Vol. 5:1408–1417

  99. Forni D, Cagliani R, Clerici M, Sironi Grand. Molecular evolution of human coronavirus genomes. Trends Microbiol. 2017. Vol. 25(i):35–48

  100. Carlson CJ, Farrell MJ, Grange Z, Han BA, Mollentze N, Phelan AL, et al.. The future of zoonotic chance prediction. Philos Trans R Soc Lond B Biol Sci. 2021. Vol. 376(1837):20200358

  101. Grange ZL, Goldstein T, Johnson CK, Anthony S, Gilardi K, Daszak P, et al.. Ranking the risk of animal-to-human spillover for newly discovered viruses. Proc Natl Acad Sci U S A. 2021. Vol. 118(15):e2002324118

  102. Li R, Xu Fifty, Bjornstad ON, Liu K, Song T, Chen A, et al.. Climate-driven variation in musquito density predicts the spatiotemporal dynamics of dengue. Proc Natl Acad Sci U S A. 2019. Vol. 116(9):3624–3629

  103. Hamlet A, Ramos DG, Gaythorpe KAM, Romano APM, Garske T, Ferguson NM. Seasonality of agricultural exposure as an important predictor of seasonal yellow fever spillover in Brazil. Nat Commun. 2021. Vol. 12(1):3647

  104. Kress WJ, Mazet JAK, Hebert PDN. Stance: Intercepting pandemics through genomics. Proc Natl Acad Sci U S A. 2020. Vol. 117(25):13852–13855

  105. Lewin HA, Robinson GE, Kress WJ, Baker WJ, Coddington J, Crandall KA, et al.. Earth BioGenome Project: sequencing life for the hereafter of life. Proc Natl Acad Sci U Due south A. 2018. Vol. 115(17):4325–4333

  106. Gruber Thou. Predicting zoonoses. Nat Ecol Evol. 2017. Vol. ane(4):98

  107. Nadimpalli ML, Pickering AJ. A call for global monitoring of Launder in wet markets. Lancet Planet Health. 2020. Vol. four(10):e439–e440

  108. Childs JE, Gordon ER. Surveillance and command of zoonotic agents prior to disease detection in humans. Mt Sinai J Med. 2009. Vol. 76(5):421–428

  109. Bird BH, Mazet JAK. Detection of emerging zoonotic pathogens: an integrated One Health approach. Annu Rev Anim Biosci. 2018. Vol. six:121–139

  110. Gardy JL, Loman NJ. Towards a genomics-informed, real-fourth dimension, global pathogen surveillance system. Nat Rev Genet. 2018. Vol. xix(1):9–twenty

  111. Tambo E, Ugwu EC, Ngogang JY. Demand of surveillance response systems to combat Ebola outbreaks and other emerging infectious diseases in African countries. Infect Dis Poverty. 2014. Vol. 3:29

  112. Alonso P, Engels D, Reeder J. Renewed push to strengthen vector command globally. Lancet. 2017. Vol. 389(10086):2270–2271

  113. WHO. Global vector control response 2017-2030. Geneva, Switzerland: World Health Organization. 2017

  114. WHO. Managing epidemics: Fundamental facts almost major deadly diseases. Geneva, Switzerland: Earth Health Organisation. 2018

  115. Relman DA. Opinion: To stop the next pandemic, we demand to unravel the origins of COVID-19. Proc Natl Acad Sci U Due south A. 2020. Vol. 117(47):29246–29248

  116. Gryseels S, Mbala-Kingebeni P, Akonda I, Angoyo R, Ayouba A, Baelo P, et al.. Role of Wild animals in Emergence of Ebola Virus, Kaigbono (Likati), Congo-kinshasa, 2017. Emerg Infect Dis. 2020. Vol. 26:2205–2209

  117. Ge XY, Li JL, Yang 40, Chmura AA, Zhu 1000, Epstein JH, et al.. Isolation and characterization of a bat SARS-like coronavirus that uses the ACE2 receptor. Nature. 2013. Vol. 503(7477):535–538

  118. Choi MJ, Morin CA, Scheftel J, Vetter SM, Smith K, Lynfield R, et al.. Variant flu associated with alive beast markets, minnesota. Zoonoses Public Health. 2015. Vol. 62(5):326–330

  119. Woo PC, Lau SK, Yuen KY. Infectious diseases emerging from Chinese wet-markets: zoonotic origins of astringent respiratory viral infections. Curr Opin Infect Dis. 2006. Vol. 19(v):401–407

  120. CCDC. The Chinese Heart for Disease Command detects a large number of new coronaviruses in the South China seafood market in Wuhan Beijing, China: Chinese Center for Disease Control and Prevention. 2020 2020 July 8 www.chinacdc.cn/yw_9324/202001/t20200127_211469.html

  121. WHO. Origin of SARS-CoV-two. Geneva, Switzerland: World Health System. 2020 cited 2020 December 12, 2020 https://apps.who.int/iris/bitstream/handle/10665/332197/WHO-2019-nCoV-FAQ-Virus_origin-2020.1-eng.pdf

  122. Anonymous. Editorial: Prevent and predict. Nat Ecol Evol. 2020. Vol. 4(three):283

  123. WHO. WHO recommendations to reduce risk of manual of emerging pathogens from animals to humans in alive animal markets or animal product markets. Geneva, Switzerland: Earth Health Organization. 2020 cited 2020 December 12, 2020 https://apps.who.int/iris/bitstream/handle/10665/332217/WHO-2019-nCoV-Human_animal_risk-2020.two-eng.pdf?sequence=1&isAllowed=y

  124. Gupta P, Robin VV, Dharmarajan 1000. Towards a more good for you conservation paradigm: integrating disease and molecular environmental to help biological conservation. J Genet. 2020. Vol. 99(1):65

  125. Namouchi A, Guellil M, Kersten O, Hansch S, Ottoni C, Schmid BV, et al.. Integrative approach using Yersinia pestis genomes to revisit the historical landscape of plague during the Medieval Period. Proc Natl Acad Sci U S A. 2018. Vol. 115(50):E11790–E11797

  126. Gwinn M, MacCannell D, Armstrong GL. Next-generation sequencing of infectious pathogens. JAMA. 2019. Vol. 321(9):893–894

  127. Davies MR, McIntyre L, Mutreja A, Lacey JA, Lees JA, Towers RJ, et al.. Atlas of group A streptococcal vaccine candidates compiled using large-scale comparative genomics. Nat Genet. 2019. Vol. 51(six):1035–1043

  128. Spyrou MA, Bos KI, Herbig A, Krause J. Ancient pathogen genomics as an emerging tool for infectious disease inquiry. Nat Rev Genet. 2019. Vol. 20(6):323–340

  129. Black A, MacCannell DR, Sibley TR, Bedford T. 10 recommendations for supporting open pathogen genomic analysis in public health. Nat Med. 2020. Vol. 26(6):832–841

  130. Anonymous. Editorial: Iii-pronged pandemic prevention. Nat Ecol Evol. 2020. Vol. four(ix):1149

  131. Morse SS, Mazet JA, Woolhouse 1000, Parrish CR, Carroll D, Karesh WB, et al.. Prediction and prevention of the next pandemic zoonosis. Lancet. 2012. Vol. 380(9857):1956–1965

  132. Cowling BJ, Ali ST, Ng TWY, Tsang TK, Li JCM, Fong MW, et al.. Bear upon cess of non-pharmaceutical interventions against coronavirus disease 2019 and flu in Hong Kong: an observational study. Lancet Public Health. 2020. Vol. 5(5):e279–e288

  133. Jarvis CI, Van Zandvoort M, Gimma A, Prem Chiliad, Klepac P, Rubin GJ, et al.. Quantifying the affect of physical distance measures on the transmission of COVID-19 in the United kingdom. BMC Med. 2020. Vol. 18(1):124

  134. Lai South, Ruktanonchai NW, Zhou L, Prosper O, Luo W, Floyd JR, et al.. Effect of non-pharmaceutical interventions to contain COVID-19 in China. Nature. 2020. Vol. 585(7825):410–413

  135. Li R, Pei S, Chen B, Song Y, Zhang T, Yang W, et al.. Substantial undocumented infection facilitates the rapid dissemination of novel coronavirus (SARS-CoV-2). Science. 2020. Vol. 368(6490):489–493

  136. Prem G, Liu Y, Russell TW, Kucharski AJ, Eggo RM, Davies N, et al.. The effect of control strategies to reduce social mixing on outcomes of the COVID-19 epidemic in Wuhan, China: a modelling report. Lancet Public Wellness. 2020. Vol. 5(5):e261–e270

  137. Li R, Chen B, Zhang T, Ren Z, Song Y, Xiao Y, et al.. Global COVID-19 pandemic demands joint interventions for the suppression of future waves. Proc Natl Acad Sci U S A. 2020. Vol. 117(42):26151–26157

  138. Corbett KS, Edwards DK, Leist SR, Abiona OM, Boyoglu-Barnum S, Gillespie RA, et al.. SARS-CoV-two mRNA vaccine design enabled by image pathogen preparedness. Nature. 2020. Vol. 586(7830):567–571

Contributors

Journal

Zoonoses

Zoonoses

Zoonoses

Compuscript (Shannon, Ireland )

2737-7466

2737-7474

01 April 2022

: two

: ane

Affiliations

[1 ]Segmentation of Science, Schoolhouse of Interwoven Arts and Sciences, Krea University, Sri Urban center, Andhra Pradesh, India

[2 ]Centre for Ecological and Evolutionary Synthesis, Department of Biosciences, University of Oslo, Oslo, Norway

[iii ]Catching and Non-Infectious disease Cluster, World Wellness Organization Regional Role for Africa, Brazzaville, Republic of Congo

[4 ]Norwegian Veterinarian Institute, Oslo, Kingdom of norway

[five ]Department of Biology and Woods Institute for the Environs, Stanford Academy, Stanford, CA, U.s.a.

[6 ]Section of Biology, Ashoka Academy, Sonepat, India

[7 ]Evolutionary Ecology Grouping, Department of Biological science, University of Antwerp, Wilrijk, Kingdom of belgium

[8 ]CAS Primal Laboratory of Special Pathogens, Wuhan Constitute of Virology, Wuhan, China

[9 ]Metabiota, 425 California Street, Suite 1200, San Francisco, CA, USA

[10 ]State Central Laboratory of Pathogen and Biosecurity, Beijing Institute of Microbiology and Epidemiology, Beijing, China

Author notes

Edited past: Wei Wang, Jiangsu Institute of Parasitic Diseases, China

Reviewed by: Cao Chen, National Institute for Viral Disease Control and Prevention, China

Aaron Irving, Zhejiang Academy-University of Edinburgh Institute, China

The third reviewer chose to remain anonymous.

Article

10.15212/ZOONOSES-2021-0028

75a8204b-8825-4f76-a51d-b505bb891885

Copyright © 2022 The Authors.

This is an open access commodity distributed nether the terms of the Creative Eatables Attribution License (CC BY) 4.0, which permits unrestricted use, distribution and reproduction in any medium, provided the original writer and source are credited.

Page count

Figures: 3, References: 138, Pages: xiii

Product
Funding

Funded by: "Researcher Project for Young Talents" from Research Quango of Kingdom of norway (RCN)

Award ID: 325041

Funded by: "COVIDOSE - Determining infectious dose for SARS-CoV-2 and assessing contact/proximity adventure"

Accolade ID: 312751

Funded past: Ministry of Science and Engineering science of China

Honor ID: 2020YFC0848900

Funded by: "COVID-nineteen Seasonality Project"

Award ID: 312740

We give thanks L.S. Shashidhara and members of the International Union of Biological Sciences (IUBS) for initial discussions and ideas. R.50. acknowledges funding from "Researcher Project for Young Talents" from Research Council of Norway (RCN) (reference number 325041). E.C. acknowledges support from the World Health Organization Regional Office for Africa. R.D. was supported by Stanford'south H&Southward and Woods Constitute for the Environment. M.S.J. acknowledges funding from "COVIDOSE - Determining infectious dose for SARS-CoV-2 and assessing contact/proximity take a chance" (reference number 312751) from RCN. I.K. acknowledges support from Ashoka University and Early Career Research (ECR) Laurels, Science and Applied science Research Board (SERB), India. H.50. acknowledges support from the VAX-413 IDEA Consortium of Excellence at the University of Antwerp and the BiodivERsA BIODIV-AFREID and BioRodDis projects. R.Y. acknowledges support from Ministry of Science and Technology of China (no. 2020YFC0848900). N.C.S. acknowledges support from the "COVID-nineteen Seasonality Projection" (reference number 312740) from RCN. The other authors declare no specific funding back up for this research. The funders had no role in the study pattern, information collection and analysis, decision to publish, or grooming of the manuscript.

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