key: cord-0828883-6oj6glyk authors: Zhang, Dayi; Yang, Yunfeng; Li, Miao; Lu, Yun; Liu, Yi; Jiang, Jingkun; Liu, Ruiping; Liu, Jianguo; Huang, Xia; Li, Guanghe; Qu, Jiuhui title: Ecological Barrier Deterioration Driven by Human Activities Poses Fatal Threats to Public Health due to Emerging Infectious Diseases date: 2021-01-05 journal: Engineering (Beijing) DOI: 10.1016/j.eng.2020.11.002 sha: b04a1f60264a7c8787c4894d6f99f4da2221edf8 doc_id: 828883 cord_uid: 6oj6glyk The recent outbreak of coronavirus disease 2019 (COVID-19) and concerns about several other pandemics in the 21st century have attracted extensive global attention. These emerging infectious diseases threaten global public health and raise urgent studies on unraveling the underlying mechanisms of their transmission from animals to humans. Although numerous works have intensively discussed the cross-species and endemic barriers to the occurrence and spread of emerging infectious diseases, both types of barriers play synergistic roles in wildlife habitats. Thus far, there is still a lack of a complete understanding of viral diffusion, migration, and transmission in ecosystems from a macro perspective. In this review, we conceptualize the ecological barrier that represents the combined effects of cross-species and endemic barriers for either the natural or intermediate hosts of viruses. We comprehensively discuss the key influential factors affecting the ecological barrier against viral transmission from virus hosts in their natural habitats into human society, including transmission routes, contact probability, contact frequency, and viral characteristics. Considering the significant impacts of human activities and global industrialization on the strength of the ecological barrier, ecological barrier deterioration driven by human activities is critically analyzed for potential mechanisms. Global climate change can trigger and expand the range of emerging infectious diseases, and human disturbances promote higher contact frequency and greater transmission possibility. In addition, globalization drives more transmission routes and produces new high-risk regions in city areas. This review aims to provide a new concept for and comprehensive evidence of the ecological barrier blocking the transmission and spread of emerging infectious diseases. It also offers new insights into potential strategies to protect the ecological barrier and reduce the wide-ranging risks of emerging infectious diseases to public health. Since 1970, over 1500 pathogens have been identified and isolated, 70% of which come from animals. The World Health Organization (WHO) has listed 15 pathogens as global threats causing infectious diseases [1] [2] [3] [4] . In recent decades, numerous viruses such as Ebola, hydrophobia, avian influenza, dengue, Zika, and acquired immune deficiency syndrome (AIDS) have infected over 1 billion people and killed 80 million, and their area of influence and the populations affected by them are increasing (Table 1) . Important cases include: West Nile River disease, which has infected 4161 people and caused at least 277 deaths [23, 55] ; severe acute respiratory syndrome coronavirus (SARS-CoV), which infected 8422 people and caused 919 deaths in 2003 [43, 56] ; and Middle East respiratory syndrome coronavirus (MERS-CoV), which has infected 701 people and caused 249 deaths since 2012 [51] . In particular, the recent outbreak of coronavirus disease 2019 , caused by the novel severe acute respiratory syndrome coronavirus-2 (SARS-CoV-2), has infected over 43 million people and caused over 1.1 million deaths as of 25 October 2020 [57] , raising extensive attention from both scientific and social communities. [53, 54] The increasing frequency of emerging infectious diseases has raised the question of how viruses can spread from natural hosts in their wildlife habitats to human societies. As events that hypothetically correlate with viral transmission across both species [58] and physical space, pandemic outbreaks are predominantly linked to the relationship between the natural environment and humanity. Human activities have caused increasing environmental problems around the world, including intensive contamination [59] , global warming [60] , frequent natural disasters [61] , destruction of wildlife habitats [62] , loss of biodiversity [63] , and so forth. These challenges have significantly altered the global ecosystem and thereby shaped the behavior and habits of wildlife, including natural pathogens and viruses to some extent [64, 65] , consequently influencing the emergence and distribution of infectious diseases. As a result, emerging infectious diseases are appearing with high frequency, and the epidemic areas of some controlled infectious diseases are expanding or even changing, causing severe outbreaks and threatening public health [66] . New trends challenging the prevention and control of emerging infectious viruses include the increasing number of viruses, diverse infection and transmission routes, and the scope and frequency of pandemics [67, 68] . A vaccine is currently the most effective and cost-efficient strategy to prevent susceptible populations from infection. However, most RNA viruses and emerging zoonoses have no vaccines with satisfactory protection efficiency [69] . For emerging infectious diseases, prevention in advance is far more effective and economical than treatment after an outbreak has occurred [70] . It is therefore important to unravel the viral transmission routes from viruses' natural hosts to human societies and to understand the underlying mechanisms in order to design timely and long-lasting prevention strategies [71] . Many studies have addressed the cross-species (molecular) barrier or the endemic barrier against emerging infectious diseases [58, 72] ; in fact, they are the two sides of the ecological barrier that determines the possibility of emerging viruses transmitting to and spreading among human societies from both the micro and macro perspectives. The cross-species barrier represents the rarity of viruses spreading efficiently within new hosts that have not been previously exposed or susceptible [58] . Effective breakthrough of the cross-species barrier-namely, spillover infection into alternative hosts-is mainly attributed to viral mutation or evolution, which allows viruses to gradually adapt to new host cells and eventually spread into new populations [58, 73] . On the other hand, crossing the endemic barrier depends on the probability and frequency of viral spread, which is closely correlated with contacts between viruses' natural hosts and potential hosts or humans [72] . Although many studies have explored the initial outbreaks and epidemics of infectious diseases and examined how they are linked to the cross-species or endemic barriers, these studies have mainly focused on epidemiology and immunology; there is a lack of a comprehensive and systematic analysis of viral migration and transmission in ecosystems from a macro perspective. Viruses have low genetic stability, and their evolution or variation is closely related to changes in the ecological environment [74] . In addition, viral transmission is determined by interactions among viruses, environmental media, and hosts, and the influential factors vary across geographic regions [75] . It is worth noting that human activities have a significant influence on ecosystems, such as encroachment on the wild habitats of viruses' natural hosts [72] and a shifted geographical distribution of viruses' natural or intermediate hosts driven by climate change [76] . Accordingly, the increasing intensity of human activities might deteriorate ecological barriers by shaping the contacts between humans and the natural environment, and thus accelerate viral transmission into human societies. The sudden appearance and global spread of COVID-19 as a representative of emerging infectious diseases hint at the relationship between human activities and the destruction of the ecological barrier, which is a key issue for both public health and sustainable development in the future. As there is limited knowledge on the relationship between ecological barrier deterioration and human activities, it is necessary to systematically summarize the viral transmission routes in ecosystems and reveal the mechanisms of viral transmission across the ecological barrier, thereby uncovering how human activities can deteriorate the ecological barrier and accelerate viral transmission. This will assist in the prevention and control of emerging infectious diseases. Viral transmission and infection normally occur within limited species; thus, viral infection of a human must break the ecological barrier. More precisely, four key factors in the ecological barrier play critical roles in viral transmission across either the molecular or the endemic barrier: transmission routes, contact probability, contact frequency, and viral characteristics (Fig. 1) . The ecological barrier integrates all the potential challenges to viral transmission from viruses' natural or intermediate hosts to human society, and acts as a key node for emerging infectious diseases. Viral transmission across the ecological barrier primarily depends on the mechanisms of virus spillover and transmission between species, via either natural hosts, domestic hosts, or wild vectors. Natural hosts can release viruses to the surrounding environment through secretions, feces, urine, corpses, and so forth [77] . Viruses can survive in soil or water and on various surfaces in wild habitats for a prolonged period of time [78] , causing potential infection in other species including humans via direct contact or intake. Domestic animals can also be infected by viruses through contact with environmental media polluted by wild animals carrying viruses [35] , which makes it easier for viruses to break the ecological barrier and enter human societies through the excreta, fluids, or wastes of domestic animals during the life cycle of breeding, transportation, slaughter, and sale. Alternatively, wild virus vectors such as mosquitoes can directly deliver viruses by biting domestic animals and humans, thereby behaving as a key group of intermediate hosts transmitting viruses across species with a larger range and higher risk [79] . Increasing human activities in recent decades have resulted in regional and even global climate change, which significantly alters the habitats and movement trajectories of wild animals [80, 81] . Climate change can enlarge the living area of natural and intermediate hosts carrying viruses, allowing viruses to spread over greater distances; furthermore, global warming can release ancient viruses from the permafrost [82, 83] . In addition, rapid urbanization processes increase the demands placed on land resources, leading to frequent land use change and the massive destruction of wildlife habitats [84] . Ecosystems such as forests and grasslands have been gradually eroded, and the living space of wild animals has been significantly compressed to smaller scales. The improvement in human living standards and the development of agriculture and animal husbandry have increased the numbers and distribution of domestic animal populations [85] , inadvertently providing a new breeding habitat and route for zoonoses to cross the ecological barrier. These human-driven factors work together to increase the transmission routes of emerging viruses from natural environments into human society. Besides diversified transmission routes that offer opportunities for viruses to break through the ecological barrier, the possibility of viral transmission from wildlife to humans depends on the probability of contact within a given area between virus hosts and humans. The range and intensity of human activities are key factors in the possibility of transmission, especially in overlapping areas used by both humans and wildlife. Changes in wildlife habitats driven by global and regional climate change may lead to wildlife invading human residential areas, increasing the probability of direct contact between humans and natural hosts carrying viruses [76] . In fragmented areas where both wildlife and humans are active, the dynamic numbers and geographical distribution of viruses' natural hosts result in higher contact probability in comparison with closed wildlife habitats [72] . Furthermore, rapid urbanization processes produce massive human gathering areas and promote the high-density reproduction and activity of domestic animals in urban areas, which unintentionally raise the transmission possibility through breeding, transportation, slaughter, and sale [86] . The emergence of poverty, slums, and shantytowns in urban areas can result in potential centralized transmission places for emerging infectious diseases [87] . Contact frequency, which refers to the level of human exposure to hosts carrying viruses over a time scale, is another key factor in viral transmission across the ecological barrier. Given certain transmission routes and possibilities, contact frequency is strongly associated with the density and active intensity of human populations in fragmented areas that are the habitats of wildlife [72] . As for most zoonoses, contact frequencies between domestic animals and humans are closely linked to living habits and urbanization level [35] . Viral survival time, load, and infectivity are key features affecting the possibility of viruses breaking through the ecological barrier. Viruses of different types have distinct survival times and decay patterns across environmental media and conditions, and numerous studies have reported on the survival time and influential factors of classic viruses on solid surfaces or in domestic water, sewage, air, and soil. Temperature is a critical factor influencing viral activity and is generally inversely proportional to viral survival time [88] [89] [90] [91] [92] [93] . Coronaviruses lose 99.9% of their activity after 10 days in filtered water, and even survive after 100 days at 4 °C [94] . Airborne viruses mainly exist on aerosol surfaces and transmit via airflow over hundreds of meters, far beyond the range of droplets, forming an important transmission route for influenza and other respiratory diseases [95] . Soil is also an important environmental source of or carrier for viruses. Many spherical, tailless viruses and phages have been detected in the soils of deserts, farmlands, forests, wetlands, and pastures around the world at a high level (2.2 × 10 3 -5.8 × 10 9 ·g -1 ) [96] [97] [98] [99] [100] [101] [102] [103] . Viruses causing respiratory diseases such as influenza (H1N1, H9N9, and H5N1) and coronavirus (MERS-CoV, SARS-CoV, and other human coronavirus) have a relatively shorter survival time in soils. Influenza viruses can survive for several hours to 3 days on solid surfaces and to 6 days on masks, latex, and feathers [104] [105] [106] [107] [108] [109] [110] [111] [112] [113] , and coronaviruses can survive on solid surfaces or in soils for 2-6 days [114] [115] [116] [117] [118] [119] [120] . It is worth noting that soil moisture content is normally proportional to viral activity [121, 122] ; however, the mechanisms of virus inactivation differ under dry and wet conditions. Viral capsid proteins are easy to dehydrate and inactivate in dry soils, causing the virus to lose its capability to protect RNA, infect, and reproduce, whereas viral RNA may not be destroyed. In contrast, RNA lyase activity is stronger under wet conditions due to the higher microbial activity in soils, resulting in a higher rate of virus capsid dissolution and RNA degradation [123] . Viral loads in viruses' natural hosts have been reported to be affected by human invasions [124] . Wildlife habitat destruction can create extra environmental stresses on wild animals and trigger a stress response to increase the viral load in urine and saliva secretion [125] . Furthermore, viral infectivity and pathogenicity in other hosts are key factors in the frequent occurrence of emerging infectious diseases. Viruses with a longer survival time or more transmission routes have a greater possibility of transmitting from their natural hosts to others, and RNA viruses are prone to greatly mutate in response to environmental changes and to rapidly replicate, contributing to their higher chance to break through the ecological barrier and adapt to new hosts [126] . The prevalence of emerging infectious diseases crossing the ecological barrier is related to many ecological processes that are intensively affected by the consequences of human activities, such as global climate change, invasions in fragmented wildlife habitats, diverse human habitats and agricultural development, and rapid urbanization [124, 127, 128] . In this context, the ability of the ecological barrier to block viral transmission from natural hosts to human society is related to the burden of viral transmission in wild intermediate hosts, breeding animal hosts, and environmental media, respectively (Fig. 2) . Global climate change has caused a series of problems including sea level rise, extreme weather, flood, drought, and air/water quality degradation [129] . It can also affect vector ecology to promote the spread of emerging infectious diseases in many ways [130] . In general, global climate change shifts the range and distribution of the habitats of virus es' natural or intermediate hosts and releases ancient viruses from the permafrost, thereby increasing the wide-ranging risks of emerging infectious diseases. Global climate change driven by industrialization significantly alters the habitat range and movement trajectory of wild animals [80, 81] . The population and distribution of viral natural hosts or vectors that benefit from global climate change will expand, thereby increasing the possibility and frequency of contact with humans in order to transmit emerging infectious diseases across the ecological barrier [76] . The West Nile, chikungunya, Zika, and dengue viruses are all arboviruses. Although their natural hosts differ, their vectors are all arthropod mosquitoes that transmit these arboviruses in a mosquitonatural host-mosquito cycle. Humans are easily infected by mosquitoes carrying viruses [79] , among which Aedes aegypti and Aedes albopictus are two typical climate-sensitive vectors. Temperature, rainfall, and humidity are key factors in the reproduction, expansion, and activity of A. aegypti and A. albopictus [131, 132] . Outbreaks of West Nile virus disease are mostly related to high temperature, and a drop in temperature from 26 to 18 °C can decrease the infection rate of Culex pipiens from 97% to 18% [133] . As global warming can drive mosquitoes to spread in higher altitudes [134] , the Lancet Countdown to 2030: Public Health and Climate Change points out that climate change is increasing dengue fever transmissibility by A. aegypti; dengue fever has already increased by 9.4% from 1950 to 2015 [135] . Such shifting habitats and the expanding transmission of arboviruses driven by global climate change pose a serious threat to public health. Global climate change can also bring about another acknowledged risk of emerging infectious diseases, widely known as the release of ancient viruses from the melted permafrost. Giant icosahedral DNA viruses [136] and Mollivirus sibericum [82] identified in 30 000-year-old permafrost still retain their ability to infect after resuscitation. A recent study found 33 viral populations representing four known genera and likely 28 novel viral genera from about 15 000-year-old ice in the glaciers of the Tibetan Plateau [83] . In a worst-case scenario, all the ancient viruses might be released from melted permafrost or glaciers alongside global warming. The intensity of human activities determines the level of human invasion into wildlife habitats, the viral load in viruses' natural hosts, and the number and density of domestic animals, including livestock, poultry, and pets. Human activities in wildlife habitats increase the contact frequency between humans and wild animals carrying viruses and shorten the effective contact time, thereby remarkably increasing the risks of viral transmission across the ecological barrier [137] . Although habitat fragmentation isolates populations with low mobility, it provides access to mobile animals and thus changes the diversity in undisturbed areas [125] . Such impacts change both the habitats of vectors and the patterns of emerging diseases [138] . Environmental stress caused by human activities may lead to an immune response in wild animals, which changes the viral load in the viruses' natural or intermediate hosts. Stress response is reported to alter immune function and change the transmission and infection patterns among wild animals, domestic animals, and humans [139] . Although no convincing experimental data has illustrated the relationship between stress response and host viral load, two hypotheses have been raised to explain this phenomenon. The "accidental spillover" hypothesis suggests that the immune response of virus hosts suppresses the persistent infection, and replication and periodic shedding of viruses only occur when the immune response is weakened by internal or external pressure, breaking the balance between viruses and their hosts [140, 141] . This hypothesis explains one of the driving mechanisms of Hendra virus as the immune response of fruit bats induced by human-caused stress [125, 142] . In contrast, the "transient epidemic" hypothesis describes a dynamic balance between local virus extinction and re-colonization between hosts. Accordingly, an infection pulse is generated as a wave of infection across hosts. The key factor triggering a transient epidemic of non-lethal viruses is recovery after infection and subsequent immunity [125] . As time passes, the immunity of the whole population decreases, and the viral load then increases. A study on the significant correlation between land use change and the outbreak of Ebola disease reported that, among the 11 first-reported infectious cases of Ebola disease, eight cases occurred in areas with a high degree of forest destruction [72] . Such areas are all habitats of bats carrying the Ebola virus, and the viral load in bats is only detectable in the case of Ebola disease. The migration and distributions of ticks in damaged forests are strongly correlated with the case numbers and geographical features of Kyasanur forest disease [143] , Lyme disease [144] , and Crimean Congo hemorrhagic fever [145] . Besides directly coming into contact with wildlife, human infection can occur by touching environmental media containing viruses in wildlife habitats. Natural viral hosts can release viruses into the surrounding environmental media in many ways, such as through saliva on fruit, animal carcasses during feeding, feces or urine entering the water or soil, and even dead corpses. Typical examples include the Nipah [146, 147] , Ebola [33, [148] [149] [150] , Marburg, and Hanta [151] viruses. Nipah virus was first identified in 1998 in Malaysia; its natural hosts are Pteropus giganteus. The habitats of P. giganteus are close to jujube trees, and the hosts' excreta of urine and feces containing Nipah virus can contaminate the jujube juice and juice collection jars, resulting in human infection [146, 147] . Fruit bats are natural Ebola hosts, and the most recognized transmission routes from fruit bats to humans include eating bat meat with live viruses, consuming foods contaminated by bat excreta, and coming into direct contact with fruit bats in caves [33, [148] [149] [150] . Hanta virus disease can be traced back to 1913; its natural hosts are rodents, including Apodemus agrarius, Rattus norvegicus, Apodemus dahlia, and Apodemus agrarius. The main transmission route of Hanta virus is animal-derived contact through saliva, urine, and feces, which release viruses into the surrounding environment. Infection can occur through the respiratory tract due to dusts carrying viruses, the digestive tract from contaminated food and water, direct contact with rodents or their excreta, and invasion through damaged skin [ 151] . More importantly, viruses can survive in environmental media for a prolonged length of time, waiting for opportunities to infect animals and humans and cause an outbreak of an emerging infectious disease. Under suitable conditions, viruses can survive for hundreds or even thousands of days in environmental matrices. Porcine parvovirus can survive for more than 43 weeks in soil [152] , and human norovirus retains at least 10% activity after 1266 days in groundwater [153] . SARS-CoV-2 viral RNA has been detected on the floor in COVID-19 patient rooms [154] and even in the soil surrounding the outpatient department [155] . Accordingly, environmental media in wildlife habitats are hypothesized to receive and store viruses from natural virus hosts-particularly in soil, silt, or fallen leaves in caves or forest interiors, which are cold, dark, and humid, and thus allow viruses a longer survival time. These residual viruses may contaminate the surface water through rainfall and the groundwater through infiltration. Human activities that involve directly touching these media, eating contaminated fruits, or drinking contaminated water in these wildlife habitats offer opportunities for viruses to break through the ecological barrier during wilderness backpacking, mining, logging, or poaching. As SARS-CoV-2 is reported to survive on plastic surfaces for at least 3 days [156] , it is strongly suspected that virus-contaminated clothing might spread a wide range of viruses in crowdgathering areas, eventually causing an outbreak of an emerging infectious disease in human society. Outbreaks of Kyasanur forest disease are a good example of a transmission route through direct contact with environmental media containing viruses. Kyasanur forest disease is caused by the Kyasanur forest disease virus (a member of the virus family Flaviviridae). Monkeys and rodents such as Macaca mulatta and Rattus rattus are its natural hosts, and ticks (mainly Haemaphysalis, especially Haemaphysalis Spinigera) are its wild vectors [157] . Epidemics of Kyasanur forest disease exhibit an obvious seasonal behavior and are consistent with the life habits of local ticks carrying viruses. Patients or susceptible people predominantly include young farmers, herdsmen, and forestry workers, who frequently enter wildlife habitats in their daily work, resulting in increased exposure to intermediate virus hosts and a much higher chance of getting infected in comparison with other people [27, 28, 158, 159] . International trading provides new opportunities for the long-distance transmission of viruses or pathogens. Frequent international or transnational trading increases the exchange of wild or domestic animals carrying viruses, thus increasing the likelihood of a global outbreak [160] . For example, the outbreak of monkeypox in the United States in 2003 originated from the transnational pet trade [161] , and avian influenza in Asia presents a high risk to countries in other continents through the international poultry trade [162] . In addition, some crop pathogens can be transmitted by international trading and can infect humans and animals in other countries [163] -a transmission route that explains many outbreaks of foodborne diseases. A significant case is the emergence of Salmonella in the United States in 1998-2003, which was linked with imported mangoes from Brazil [164] . Natural virus hosts can transmit viruses to other wild animals (i.e., intermediate hosts), including predators (through being bitten or eaten by intermediate hosts), and parasites (ticks or fleas). After adaptation and evolution, viruses can infect and spread in the new intermediate hosts, expanding natural virus reservoirs in wider habitats. This process effectively breaks through the ecological barrier and poses a threat to human societies, as an increasing number of wild animals and parasites can cause outbreaks of emerging infectious diseases. Residents' living habits can also affect the transmission routes and infectivity of viruses, including eating wild animals, domestic breeding, farming, and personal sanitation. Some residents of East Asia and Africa consider wild animals to be nourishing foods to maintain one's health; therefore, eating wild animals is common behavior in some countries [165] . This habit sets up an industrial chain of wildlife poaching, feeding, and slaughtering, which increases the risk of viral transmission from their natural or intermediate hosts to human societies. Among all natural virus hosts, bats are an important reservoir of coronaviruses, including those related to SARS-CoV and SARS-CoV-2 [166] . A possible transmission route is through wild intermediate hosts (e.g., civets and weasels) to humans. Cooks and employees in wildlife food markets have a greater chance of being infected with such viruses due to their frequent contact with SARS-CoV or SARS-CoV-2 intermediate hosts [56, 167, 168] . Eating wild animals in restaurants further encourages the whole supply chain, exacerbating the possibility of direct or indirect contact between wild animals carrying viruses and hunters, breeders, butchers, or consumers, and offering additional opportunities for viral evolution and human infection. Besides wild intermediate hosts, domestic breeding animals such as horses, camels, chickens, and ducks can become intermediate hosts after infection. Domesticated animals can come into close contact with natural hosts carrying viruses by sharing foods in cribs or through biting and predation, which permits frequent viral transmission to occur between wild and domestic animals [85] . Livestock polyculture also accelerates viral mutation and interspecific transmission, making domesticated breeding animals into key intermediate hosts for many zoonoses [86] . These viruses can infect and spread within domestic breeding animal populations and directly enter human societies through the processes of raising, sales, and eating. Thus, breeders, transporters, farmers, and seafood market sellers are highly susceptible to infection by emerging infectious diseases including Hendra virus, MERS-CoV, and influenza (H1N1, H5N1, etc.). Hendra virus was first identified in Hendra (Brisbane, Queensland, Australia) in 1994, where it caused the deaths of 22 horses and three people; its natural hosts are fruit bats [169] . Breeding increases the horse populations close to the living habitats of fruit bats carrying Hendra virus [35] . These breeding farms provide additional habitats for fruit bats, which gives the horses more chances to touch the urine or secretions of the fruit bats, allowing the spread of Hendra virus among horses and then among farm staffs in close contact with the horses [170] [171] [172] [173] [174] . MERS-CoV was first isolated from the lung tissues of deceased cases of severe pneumonia in Saudi Arabia in 2012, and its natural hosts may be bats. The MERS outbreak is attributed to the domestic breeding of single humped camels in the Middle East, as the single humped camel is an important intermediate host of MERS-CoV. As thousands of single humped camels are imported into Saudi Arabia from African countries every year, the outbreak of MERS is strongly correlated with the traffic of camels [175] . Sufficient evidence shows that MERS-CoV is transmitted from camels to humans, as the infection rate of breeding staffs who come into close contact with camels is much higher than that of other people, and as serological studies have documented that the positive rates of MERS-CoV antibody in breeding and slaughterhouse staff members are 15 and 23 times higher, respectively, than in the general population [43, 51, 176, 177] . Influenza A viruses are mutagenic in their natural hosts, showing huge potential to infect poultry and invade humans. H5N1 is a zoonosis that started in Hong Kong, China in 1997 and spread to other countries [178] . Wild birds and poultry are considered to be the natural and intermediate hosts of H5N1, respectively [179] . Wild birds are responsible for virial longdistance transmission from Qinghai Lake in China to India, Siberia, and South-East Asia, and interspecies transmission between poultry populations has promoted the regional transmission of H5N1 into human societies [39, 40] . H1N1 started in Mexico in 2009 and affected 214 countries and regions, infecting millions of people and causing at least 18 449 deaths. Domestic pigs are considered to be the intermediate hosts in which H1N1 virus obtains the capability to infect humans [46, 180] . H7N9 virus comes from wild birds and can eventually infect humans by recombining genes with other influenza viruses in breeding chickens and ducks [181] . During the adaptation process in domestic poultry, H7N9 evolved from a low pathogenic avian influenza into a highly pathogenic one, causing a serious outbreak in China in 2017 with 1564 infected cases and more than 600 deaths [38, 182, 183] . In conclusion, domestic breeding animals including poultry and livestock are key intermediate hosts of influenza viruses and are key factors in influenza outbreaks in human society. Some traditional farming practices can increase the risk of viral transmission to human society. Untreated sewage and sludge are commonly used for irrigation or fertilization in many rural areas around the world; however, a variety of pathogens can be found in fresh sewage or feces, such as viruses (norovirus, enterovirus, hepatitis E virus, etc.) [ 184, 185] , pathogens (Salmonella, Escherichia coli, Vibrio cholera, etc.) [186] , and parasitic eggs (Ascaris eggs, Trichuris eggs, etc.) [187, 188] . Hepatitis E viruses are found in pig manure or wastewater from pig-breeding facilities [189] . Infectious hepatitis E viruses were detected in pig manure from 15 out of 22 pig farms in Iowa, USA [190] . As the fecal-oral pathway is a main transmission route of hepatitis E viruses, pig manure applications and surface wastewater runoff may contaminate agricultural products and the surrounding water sources [191, 192] . The positivity of hepatitis E viruses in untreated and concentrated sewage samples was found to be as high as 10.97% in a wastewater treatment plant in Puna, India [193] , indicating that sewage treatment workers face a higher risk of hepatitis E infection. Therefore, sewage irrigation can directly increase viral transmission from sewage to humans, or can indirectly contaminate soil, water, and food products to cause foodborne infectious diseases. Farming and storage products can also attract the active approach of wild animals, thereby increasing the transmission routes and contact frequency of some viruses, allowing them to cross the ecological barrier [72] . For example, the Ebola virus can be transmitted from fruit bats to humans through contaminated fruit; this process is aggravated by the fruit storage in villages, which draws fruit bats from caves into an area of human activity [165] . Personal sanitation is a critical way to block viral infection [194] . Inappropriate cultural norms and personal habits related to personal cleanliness can increase the exposure and infectious probability of viruses and pathogens [195] . Hand, foot, and mouth disease (HFMD) is caused by enterovirus (mainly coxsackievirus A16 and enterovirus 71); the susceptible population is mainly children with weak immunity [196] . Studies show that children who have a habit of sucking their fingers face a significant higher risk of such infection than others, whereas children who wash their hands before meals face only half the risk in comparison with others [197] . In addition, burying a corpse for several days and then touching the corpse is part of traditional funeral customs in some rural areas of West Afric a, and can increase the risk of spreading emerging infectious diseases [198] . The increasing level of urbanization has changed the global pattern of infectious diseases [199] . Although urbanization can improve the basic infrastructure and sanitation conditions to protect the public health to some extent [84] , it can also alter the numbers, diversities, and community structure of wildlife in city areas [200] . As a result, urbanization generates new hotspots that cause the outbreak of infectious diseases. Some municipal infrastructures provide new points or networks for viral transmission in human societies. For example, Zika virus is mainly transmitted by Aedes aegypti and other Aedes, which have already adapted to a densely populated urban environment [201] . Driven by both global climate change and urbanization processes, these vectors have a wider distribution and significantly contribute to the global outbreak of Zika virus disease [202] . SARS-CoV-2 has been detected in the wastewater in many countries, and wastewater-based epidemiology (WBE) not only offers a new diagnostic tool for disease prevention and control, but also highlights the signs of disease spread through the urban pipeline network [203] . Landfills are typical sources for viral transmission in urban areas. Due to the complexity of the wastes dumped in landfills, it may include animals that die of infection or contaminated medical wastes carrying many infectious viruses, making landfills a virus sink. In the United States, poultry and livestock with infectious diseases are generally disposed of in landfills; during an epidemic, some medical wastes carrying viruses are also buried. These activities increase the chance of viral secondary transmission and generate new hotspots of emerging infectious viruses in urban areas. Studies have demonstrated that avian influenza H6N2 virus in poultry carcasses remains infectable for nearly 2 years-or even for more than 30 years in municipal landfills under appropriate temperature and pH conditions-and that viruses can survive in landfill leachates for at least 30 days [204] . The prolonged survival time of infectious pathogens can result in wide distributions of bacterial pathogens (e.g., E. coli and Salmonella) and viruses causing avian influenza, HFMD, Newcastle disease, and porcine epidemic diarrhea [205, 206] . Studies have also reported that the waste treatment facilities in landfills can continuously release a variety of viruses in the form of bioaerosols, which spread emerging infectious viruses to wild animals and even to the landfill staff [207] . In addition, a large number of foraging rodents and birds in or around landfills can transport and excrete feces containing viruses as a transmission route, as they forage in groups during the day and return to their residence communities at night. Rodents living in landfills can carry and transmit viruses by ingesting organic wastes. For example, rodents living at landfill sites in the Istra peninsula are more likely than wild rodents to be infected by zoonotic viruses, such as lymphocytic choriomeningitis virus and tick-borne encephalitis virus [208] . Birds and their stools have been reported to carry over 60 types of pathogens, including bird influenza [209] and other human epidemic viruses such as H1N1, H2N1, and H3N2 [210, 211] . Mutated influenza viruses can accumulate in migratory birds until they break through the ecological barrier to infect humans [73, 212] . Studies in the United Kingdom have shown that landfills provide a wide range of foraging opportunities for rotifers such as seagulls and crows, which are known carriers of human infectious pathogens such as Salmonella, E. coli, Campylobacter, and influenza A viruses [213] . Their daily shuttle between landfills and reservoirs introduces the risk of water contamination by pathogens and viruses and challenges drinking water safety. White storks nesting in landfills carry more pathogens than those nesting naturally [214] . According to the wild migratory bird surveillance program for highly pathogenic avian influenza by the United States, wild ducks living in landfills are the birds most likely to be infected by influenza viruses [215] . By taking organic waste as a food source, American black vultures living in a Patagonia landfill (Argentina) were reported to be infected with and to spread zoonotic pathogens such as Salmonella [216] . It can be concluded that birds around landfills are potential hosts carrying and transmitting viruses to humans via stools, contaminated water, and dead bodies. As pathogen reservoirs, landfills are high-risk sites for birds and rodents to transmit emerging infectious diseases across the ecological barrier. Human agricultural activities can also provide breeding grounds and living habitats for the vectors of insect-borne infectious diseases by constructing dams, ponds, and other water-storage facilities for irrigation. The construction of the Aswan Dam in Egypt, the Jama Dam on the Senegal River, and the Manantari Dam in Mali and Guinea has intensified the outbreak frequency of schistosomiasis mansoni [217] . In addition, about 60 species of Anopheles are vectors of mosquito-borne malaria, and they can breed in the open ponds constructed close to farmlands, becoming an important reasons for the malaria epidemics in many countries [218] . Backward municipal infrastructure-such as water-supply and drainage networks, sewage treatment systems, and improper water storage-provides extra habitats in cities for some vectors carrying and spreading emerging infectious diseases ; for example, Aedes and Culex flourish in urban sewage, causing outbreaks of Rift Valley fever and other diseases [138, 218] . The occurrence of SARS-CoV-2 in wastewater and rivers has been reported in Wuhan, China [219] , Paris, France [203] , and Australia [220] . High levels of SARS-CoV-2 viral RNA in wastewater, ranging from several to thousands of copies per milliliter, suggest the potential transmission and spread of SARS-CoV-2 viruses in the urban and rural water cycle, presenting a potential threat to public health [221] . Sanitation conditions are closely related to viral transmission in urban areas, and improved sanitation conditions can protect the public health from emerging infectious diseases. The transfer of huge populations from rural areas to cities in the early stage of rapid urbanization is often accompanied by poverty caused by urban expansion and underdeveloped infrastructure [87] . From 1963 to 2010, over 110 000 cases of hemorrhagic fever renal syndrome (HFRS) caused by hantavirus were reported in Hunan province (China), and a positive correlation was detected between the number of city migrants and the incidence rate of HFRS in the initial stage of urbanization [84] . In addition, urban public health problems are a key factor in the emergence of infectious diseases [222] . Many cities have slums or shantytowns with poor sanitation conditions, and some infectious diseases are rampant in these densely populated and relatively closed areas. Some developing countries in Asia and Africa with poor sanitation conditions, limited basic medical capabilities, and insufficient vaccine coverage cannot sufficiently deal with emerging infectious diseases, which have a higher possibility of breaking out there [191] . The largescale outbreak of acute viral hepatitis (AVH) from 1955 to 1956 in New Delhi was mainly located in slums with poor sanitation conditions and a low socio-economic level [223] . In summary, the ecological barrier is the key to viral transmission from viruses' natural or intermediate hosts to human societies. The strength of the ecological barrier determines the possibility and scale of epidemics caused by emerging infectious viruses. Future studies should focus on the dynamic process of virus es crossing the ecological barrier, which is a critical step for the prevention and control of emerging infectious diseases. The main influential factors affecting the ecological barrier include transmission routes, contact probability, contact frequency, and viral characteristics; environmental media are also an important component of the ecological barrier. Emerging infectious diseases are currently exhibiting global spreading patterns owing to the deterioration of the ecological barrier by intensive human activities. Global climate change driven by industrialization and globalization processes has triggered and expanded the emergence of infectious diseases, and the increasing levels of human disturbance in fragmented wildlife habitats are significantly promoting greater contact probability and a higher frequency of emerging infectious viruses breaking through the ecological barrier. With the rapid development of the social economy, international transportation through the air and over sea and land is becoming more intensive. As a result, such transportation is advancing a cross-border exchange of emerging infectious viruses that is driving the globalization of epidemics and introducing great challenges for public health and biosafety management. The presence of diverse human habitats across countries also increases the transmission routes of viruses, and global urbanization is shaping new hotspots of poverty and poor sanitary conditions in urban areas that promote the spread of emerging infectious diseases in human societies. It is extremely urgent to further explore the quantitative effects of human activities on the strength of the ecological barrier and to understand the mechanisms by which emerging infectious diseases are transmitted and spread across the ecological barrier. As viruses are "dark matter" in many environmental media that behave as viral reservoirs, more studies should focus on building the environmental virus database for wildlife habitats. A comprehensive investigation into the interactions between viruses, their hosts, and environmental media can grant us better insight into the effects of ecological barrier deterioration on the spread of emerging infectious diseases, as well as the underlying influential factors. For the effective prevention and control of emerging infectious diseases, potential strategies should be considered to protect the ecological barrier and block the transmission of viruses from their natural reservoirs into human societies. Firstly, largescale environmental surveys on viruses in wildlife habitats are suggested in order to map the origin and distribution of emerging infectious viruses and visualize "hot" or weakened spots in the ecological barrier. Secondly, dynamic monitoring of natural (e.g., bats, pangolins, birds) or intermediate (e.g., camels, mosquitoes, ticks) hosts of zoonoses should focus on fragmented wildlife habitats being invaded by human activities. In addition, we propose a biosafety "skynet" as a novel strategic concept for preventing and controlling the rapid outbreak of emerging infectious diseases in urban areas. It consists of online diagnostic devices for monitoring viral load in environmental media like aerosol and water, and a real-time big data management system for early warning and emergency management. Regular biosafety management and emergency measures are necessary to enable the ecological barrier in either the natural environment or human societies to effectively control emerging infectious viruses of great concern. Lastly, but most importantly, in following a path of sustainable development, human society must reconsider the correlation between human and global ecology and pay more attention to the protection of the ecological barrier. 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