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Korean J. Vet. Serv. 2022; 45(4): 285-292
Published online December 30, 2022
https://doi.org/10.7853/kjvs.2022.45.4.285
© The Korean Socitety of Veterinary Service
Correspondence to : Jae-Ku Oem
E-mail: jku0623@jbnu.ac.kr
https://orcid.org/0000-0002-4298-0604
This is an Open Access article distributed under the terms of the Creative Commons Attribution Non-Commercial License (http://creativecommons.org/licenses/by-nc/4.0). which permits unrestricted non-commercial use, distribution, and reproduction in any medium, provided the original work is properly cited.
Avian influenza viruses (AIVs) cause contagious diseases and have the potential to infect not only birds but also mammals. Wild birds are the natural reservoir of AIVs and spread them worldwide while migrating. Here we collected active AIV surveillance data from wild bird habitats during the 2019 to 2022 winter seasons (from September to March of the following year) in South Korea. We isolated 97 AIVs from a total of 7,590 fecal samples and found the yearly prevalence of AIVs was 0.83, 1.48, and 1.27, respectively. The prevalence of AIVs were generally higher from September to November. These findings demonstrate that a high number of wild birds that carry AIVs migrate into South Korea during the autumn season. The highest virus numbers were isolated from the species Anas platyrhynchos (72%; n=70), followed by Anas poecilorhyncha (15.4%; n=15), suggesting that each is an important host for these pathogens. Twenty-five hemagglutinin-neuraminidase subtypes were isolated, and all AIVs except the H5N8 subtype were found to be low-pathogenic avian influenza viruses (LPAIVs). Active surveillance of AIVs in wild birds could benefit public health because it could help to estimate their risk for introduction into animals and humans. Moreover, considering that 132 cases of human AIV infections have been reported worldwide within the last 5 years, active surveillance of AIVs is necessary to avoid outbreaks.
Keywords Avian influenza viruses, Wild birds, Surveillance
Avian influenza viruses (AIVs) belong to the
Wild aquatic birds, especially those in the
The migration of wild birds along nine major global migratory flyways has been suggested to facilitate the circulation of AIVs (Hill et al, 2012; Hansen et al, 2022). South Korea is located on the largest of these avian routes, the East Asian-Australasian Flyway (EAAF) (Hansen et al, 2022), which brings many migratory birds to South Korea during the cold season to overwinter and breed (Choi et al, 2022). Such migratory birds were found to have played a critical role in the global spread of the H5N8 subtype of HPAIVs in 2014, which had first been detected in South Korea and later caused worldwide economic damage (Samantha et al, 2016). Routine monitoring of wild birds in South Korea is therefore necessary to prevent such outbreaks in the future. In this study, we collected active AIV surveillance data from wild bird habitats and identified AIVs prevalence in South Korea from 2019 to 2022.
Fresh fecal samples of wild birds were collected every Korean winter season from 2019 to 2022 from a total of 100 wild bird habitats located near Ganwolho, Gamcheon, Gokgyocheon, Geumgang, Geumgangho, Geumhogang, Dongrimj, Dongjingang, Mangyeonggang, Bonggangcheon, Bongseonji, Bunamho, Sapgyocheon, Seongamji, Ansim Wetland, Yedangji, Joenjucheon, Cheongmicheon, Pungseocheon and Pungjeonji (Fig. 1). The study sites where large numbers of wild birds have used and antigen of AIVs were frequently detected were selected. We collected only fresh and well-distinguished single samples. Specimens were transported to our laboratory facilities immediately and stored at 4℃ until analyses.
Each fecal sample was suspended in phosphate-buffered saline (PBS, pH 7.4) containing antibiotics (100 U/μL of penicillin and 100 U/μL of streptomycin) and centrifuged at 2,800 g for 10 min. Supernatants of five samples were pooled and filtered through a sterile 0.45-μm filter (GVS, USA). The resulting solutions were inoculated into 9∼11-day-old specific pathogen-free (SPF) embryonated chicken eggs, incubated at 37℃ for 3∼4 days, and chilled at 4℃ to harvest allantoic fluids. An HA test was conducted according to the World Organization for Animal Health (OIE) recommendations (Stear, 2005). The HA-positive pooling fecal samples were inoculated individually into SPF embryonated chicken egg using the method previously described and further processed for viral extraction.
Viral RNA was extracted from HA-positive allantoic fluids using a Miracle-AutoXT Automated Nucleic Acid Extraction System (iNtRON Biotechnology, South Korea). A LiliFⓇ AIV M Real-time RT-PCR Kit (iNtRON Biotechnology, Korea) protocol was applied to detect AIVs. Subtypes were determined by RT-qPCR using the TOP-real™ One-step RT qPCR Kit (Enzynomics, South Korea) with previously described primers (Hoffmann et al, 2016). Host DNA was extracted from the fecal samples and species were identified using mitochondrial cytochrome C oxidase I gene, as previously described (Gao et al, 2009).
We isolated 97 AIVs from a total of 7,590 fecal samples (Table 1). The yearly prevalence of AIVs was 0.83% (27/3,248), 1.48% (37/2,499), and 1.27% (33/1,843) from 2019 to 2022, respectively. The prevalence was higher in winter 2020/2021 than during the same months 1 year before and after. We detected higher prevalence in the samples from September to November than in those collected during the remaining months of every year during the study period. The AIVs were isolated from Pungseocheon, Sapgyocheon, Bonggangcheon, Gokgyocheon, Bunamho, Joenjucheon, Mangyeonggang, Dongjingang and Geumgang and the prevalence was 2.22%, 4.40%, 1.28%, 2.37%, 1.66%, 1.37%, 1.81%, 1.38% and 0.64%, respectively (Table 2). The highest rate of AIVs isolation showed in Sapgyocheon (4.40%).
Table 1 . Prevalence of AIVs from 2019 to 2022 in South Korea
Year | Number of collected samples | Number of AIV isolates | Prevalence of AIV (%) |
---|---|---|---|
2019.10 | 944 | 10 | 1.05 |
2019.11 | 932 | 11 | 1.18 |
2019.12 | 740 | 2 | 0.27 |
2020.01 | 130 | 0 | 0.00 |
2020.02 | 330 | 3 | 0.90 |
2020.03 | 172 | 1 | 0.58 |
2019.10∼2020.03 | 3,248 | 27 | 0.83 |
2020.09 | 100 | 18 | 18 |
2020.10 | 229 | 9 | 3.93 |
2020.11 | 200 | 1 | 0.5 |
2020.12 | 650 | 4 | 0.61 |
2021.01 | 640 | 3 | 0.46 |
2021.02 | 630 | 1 | 0.16 |
2021.03 | 50 | 1 | 2 |
2020.09∼2021.02 | 2,499 | 37 | 1.48 |
2021.11 | 708 | 28 | 3.95 |
2021.12 | 635 | 5 | 0.78 |
2021.11∼2022.01 | 1,843 | 33 | 1.79 |
Total | 7,590 | 97 | 1.27 |
Table 2 . Numbers of AIVs detected in wild bird species
Location | Chungcheong-do | Jeolla-do | Total | |||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
Pungseo-cheon | Sapgyo-cheon | Bonggang-cheon | Gokgyo-cheon | Bunam-ho | Jeonju-cheon | Mangyeong-gang | Dongjin-gang | Geum-gang | ||||
Number of collected samples | 90 | 454 | 233 | 253 | 120 | 290 | 2,422 | 576 | 1,243 | |||
Number of AIVs isolates (Prevalence of AIV, %) | 2 (2.22) | 20 (4.40) | 3 (1.28) 33 (2.86) | 6 (2.37) | 2 (1.66) | 4 (1.37) | 44 (1.81) | 8 (1.38) 64 (1.41) | 8 (0.64) | 97 | ||
Numbers of host | 14 | 2 | 5 | 1 | 3 | 39 | 5 | 1 | 70 | |||
2 | 5 | 1 | 1 | 1 | 3 | 2 | 15 | |||||
1 | 1 | 4 | 6 | |||||||||
2 | 2 | |||||||||||
2 | 2 | |||||||||||
1 | 1 | |||||||||||
1 | 1 |
The hosts of all identified AIVs belonged to the order Anseriformes. Most were detected in the species
We isolated 25 HA-NA subtypes of AIVs, including nine HA (H3, H4, H5, H6, H7, H8, H9, H10 and H11) and eight NA (N1, N2, N3, N4, N6, N7, N8 and N9) (Table 3). The most frequently detected HA and NA subtypes was H5 (16.49%; n=16) and N6 (20.62%; n=20), respectively, except mixed subtypes. Both H4N6 (12.37%; n=12) and H5N3 (12.37%; n=12) were the most prevalent subtypes. Fig. 2 also shows yearly distributions of subtypes from 2019 to 2022. H4, H5 and H6 subtype identified in all seasons. The most diverse subtypes of AIVs were detected in Mangyeonggang.
Table 3 . Numbers of haemagglutinin (HA) and neuraminidase (NA) subtypes during AIVs surveillance in wild birds in South Korea, 2019∼2022
Location | Chungcheong-do | Jeolla-do | Total (prevalence, %) | |||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
Pungseo-cheon | Sapgyo-cheon | Bonggang-cheon | Gokgyo-cheon | Bunam-ho | Jeonju-cheon | Mangyeong-gang | Dongjin-gang | Geum-gang | ||||
Numbers of subtypes | ||||||||||||
H3 | N6 | 3 | 3 (3.09) | |||||||||
N8 | 3 | 3 (3.09) | ||||||||||
N9 | 1 | 1 (1.03) | ||||||||||
H4 | N2 | 1 | 1 (1.03) | |||||||||
N3 | 1 | 1 (1.03) | ||||||||||
N6 | 2 | 1 | 1 | 1 | 7 | 12 (12.37) | ||||||
H5 | N2 | 3 | 3 (3.09) | |||||||||
N3 | 1 | 11 | 12 (12.37) | |||||||||
N8 | 1 | 1 (1.03) | ||||||||||
H6 | N1 | 2 | 1 | 1 | 4 (4.12) | |||||||
N2 | 7 | 1 | 8 (8.24) | |||||||||
N6 | 3 | 3 (3.09) | ||||||||||
N8 | 1 | 1 | 2 (2.06) | |||||||||
H7 | N1 | 1 | 1 (1.03) | |||||||||
N6 | 1 | 1 (1.03) | ||||||||||
N7 | 1 | 1 | 2 (2.06) | |||||||||
N9 | 1 | 1 (1.03) | ||||||||||
H8 | N4 | 1 | 1 (1.03) | |||||||||
H9 | N2 | 1 | 2 | 3 (3.09) | ||||||||
H10 | N4 | 1 | 1 | 2 (2.06) | ||||||||
N7 | 1 | 1 (1.03) | ||||||||||
H11 | N2 | 2 | 2 (2.06) | |||||||||
N3 | 4 | 4 (4.12) | ||||||||||
N8 | 1 | 1 (1.03) | ||||||||||
N9 | 5 | 5 (5.15) | ||||||||||
Mixed subtypes | 5 | 4 | 2 | 3 | 1 | 15 (15.4) | ||||||
HxNx | 2 | 1 | 1 | 4 (4.12) |
Global prevalence of AIV was 0.06% (0.30∼1.21%) (Barbara et al, 2017). However, the prevalence of AIVs in wild birds depends on host species, seasonality and locations (Munster et al, 2007). The higher prevalence of AIVs compared to that of global showed in this study (1.27%) and this result was thought to be due to active surveillance conducted in winter season and wild bird habitats.
In 2019/2020, HPAIVs were neither detected in wild bird feces nor at any poultry farms in South Korea (Jeong et al, 2020). However, in 2020/2021, the H5N8 subtype was identified at 109 poultry farms, and the novel H5N1 virus entered the country in late 2021 (Sagong et al, 2022). The higher prevalence of AIVs recorded in 2020/2021 might be explained by the fact that more active surveillance systems were implemented in wild bird habitats to prevent HPAIV outbreaks.
Most migratory birds returned to mid-central and western provinces of South Korea (Jeolla-do and Chungcheong-do) (Lee et al, 2020). We isolated AIVs in Chungcheong-do and Jeolla-do province and this result shows high population of wild birds is related to high isolation rates of AIVs. According to the National Institute of Biological Resources in South Korea, the migration season of wild birds can be divided into four stages: October to November, December to January, February to March, and April to August (Lee et al, 2020). Stage 1 represents autumn migration, and during this season, most migratory wild birds arrive in South Korea from China or Russia (Lee et al, 2020). In an earlier study conducted in South Korea, isolation rates of AIVs in wild bird feces increased during stage 1 but decreased during stage 2, which is consistent with the results of the current study (Shin et al, 2015). These findings suggest that many wild birds that are infected with AIVs migrate to South Korea during the autumn season. AIV surveillance is therefore particularly needed from October to November to prevent the spread of AIVs from wild birds to poultry farms.
The isolation rate of AIVs was especially high in the mallard (
The H4 subtype was distributed worldwide and showed high prevalence in wild birds (Tang et al, 2020). The H4N6 subtype was detected yearly during the study period, which is consistent with previous research. The H5 and H7 subtypes were also isolated, but except for the H5N8 virus, all other H5 and H7 subtypes were LPAIVs. In 2019/2020 and 2020/2021 mixed subtypes of AIVs were isolated in a single wild bird fecal sample, suggesting that coinfection with multiple subtypes of AIVs occurred in wild birds. Coinfection of wild birds by AIVs is important source of reassortment events that generate novel strains of AIVs (Fuller et al, 2010). Thus, even if LPAIVs, continuous genetic analysis of AIVs is required.
AIVs have zoonotic potential, with some subtypes able to infect mammals including humans (Mostafa et al, 2018). The US Centers for Disease Control and Prevention (CDC) have reported that most AIVs that cause severe symptoms and lead to death in humans belong to the H7N9 and H5N1 subtypes of HPAIVs. Human infections with AIVs have occurred, albeit not in South Korea. The World Health Organization International Health Regulations (WHO IHR) recorded 132 such cases from January 1, 2018 to April 4, 2022, and H9N2 LPAIV was identified as the most common virus subtype. Thus, since human infections caused by not only HPAIVs but also LPAIVs have been confirmed continuously and considering that H9N2 LPAIVs are frequently detected in wild birds in South Korea, continuous and active surveillance of AIVs in wild birds is essential to prevent their spread to mammals.
This research was supported by the Basic Science Research Program through the National Research Foundation of Korea (NRF), funded by the Ministry of Education (2019R1A6A1A03033084), as well as by a Government-sponsored R&D Fund for infectious disease research (GFID; HG18C0084). We would also like to express our gratitude to the editors of the Writing Center at Jeonbuk National University for their skilled English-language assistance.
No potential conflict of interest relevant to this article was reported.
Korean J. Vet. Serv. 2022; 45(4): 285-292
Published online December 30, 2022 https://doi.org/10.7853/kjvs.2022.45.4.285
Copyright © The Korean Socitety of Veterinary Service.
Eun-Jee Na , Su-Beom Chae , Jun-Soo Park , Yoon-Ji Kim , Young-Sik Kim , Jae-Ku Oem *
Laboratory of Veterinary Infectious Disease, College of Veterinary of Medicine, Jeonbuk National University, Iksan 54596, Korea
Correspondence to:Jae-Ku Oem
E-mail: jku0623@jbnu.ac.kr
https://orcid.org/0000-0002-4298-0604
This is an Open Access article distributed under the terms of the Creative Commons Attribution Non-Commercial License (http://creativecommons.org/licenses/by-nc/4.0). which permits unrestricted non-commercial use, distribution, and reproduction in any medium, provided the original work is properly cited.
Avian influenza viruses (AIVs) cause contagious diseases and have the potential to infect not only birds but also mammals. Wild birds are the natural reservoir of AIVs and spread them worldwide while migrating. Here we collected active AIV surveillance data from wild bird habitats during the 2019 to 2022 winter seasons (from September to March of the following year) in South Korea. We isolated 97 AIVs from a total of 7,590 fecal samples and found the yearly prevalence of AIVs was 0.83, 1.48, and 1.27, respectively. The prevalence of AIVs were generally higher from September to November. These findings demonstrate that a high number of wild birds that carry AIVs migrate into South Korea during the autumn season. The highest virus numbers were isolated from the species Anas platyrhynchos (72%; n=70), followed by Anas poecilorhyncha (15.4%; n=15), suggesting that each is an important host for these pathogens. Twenty-five hemagglutinin-neuraminidase subtypes were isolated, and all AIVs except the H5N8 subtype were found to be low-pathogenic avian influenza viruses (LPAIVs). Active surveillance of AIVs in wild birds could benefit public health because it could help to estimate their risk for introduction into animals and humans. Moreover, considering that 132 cases of human AIV infections have been reported worldwide within the last 5 years, active surveillance of AIVs is necessary to avoid outbreaks.
Keywords: Avian influenza viruses, Wild birds, Surveillance
Avian influenza viruses (AIVs) belong to the
Wild aquatic birds, especially those in the
The migration of wild birds along nine major global migratory flyways has been suggested to facilitate the circulation of AIVs (Hill et al, 2012; Hansen et al, 2022). South Korea is located on the largest of these avian routes, the East Asian-Australasian Flyway (EAAF) (Hansen et al, 2022), which brings many migratory birds to South Korea during the cold season to overwinter and breed (Choi et al, 2022). Such migratory birds were found to have played a critical role in the global spread of the H5N8 subtype of HPAIVs in 2014, which had first been detected in South Korea and later caused worldwide economic damage (Samantha et al, 2016). Routine monitoring of wild birds in South Korea is therefore necessary to prevent such outbreaks in the future. In this study, we collected active AIV surveillance data from wild bird habitats and identified AIVs prevalence in South Korea from 2019 to 2022.
Fresh fecal samples of wild birds were collected every Korean winter season from 2019 to 2022 from a total of 100 wild bird habitats located near Ganwolho, Gamcheon, Gokgyocheon, Geumgang, Geumgangho, Geumhogang, Dongrimj, Dongjingang, Mangyeonggang, Bonggangcheon, Bongseonji, Bunamho, Sapgyocheon, Seongamji, Ansim Wetland, Yedangji, Joenjucheon, Cheongmicheon, Pungseocheon and Pungjeonji (Fig. 1). The study sites where large numbers of wild birds have used and antigen of AIVs were frequently detected were selected. We collected only fresh and well-distinguished single samples. Specimens were transported to our laboratory facilities immediately and stored at 4℃ until analyses.
Each fecal sample was suspended in phosphate-buffered saline (PBS, pH 7.4) containing antibiotics (100 U/μL of penicillin and 100 U/μL of streptomycin) and centrifuged at 2,800 g for 10 min. Supernatants of five samples were pooled and filtered through a sterile 0.45-μm filter (GVS, USA). The resulting solutions were inoculated into 9∼11-day-old specific pathogen-free (SPF) embryonated chicken eggs, incubated at 37℃ for 3∼4 days, and chilled at 4℃ to harvest allantoic fluids. An HA test was conducted according to the World Organization for Animal Health (OIE) recommendations (Stear, 2005). The HA-positive pooling fecal samples were inoculated individually into SPF embryonated chicken egg using the method previously described and further processed for viral extraction.
Viral RNA was extracted from HA-positive allantoic fluids using a Miracle-AutoXT Automated Nucleic Acid Extraction System (iNtRON Biotechnology, South Korea). A LiliFⓇ AIV M Real-time RT-PCR Kit (iNtRON Biotechnology, Korea) protocol was applied to detect AIVs. Subtypes were determined by RT-qPCR using the TOP-real™ One-step RT qPCR Kit (Enzynomics, South Korea) with previously described primers (Hoffmann et al, 2016). Host DNA was extracted from the fecal samples and species were identified using mitochondrial cytochrome C oxidase I gene, as previously described (Gao et al, 2009).
We isolated 97 AIVs from a total of 7,590 fecal samples (Table 1). The yearly prevalence of AIVs was 0.83% (27/3,248), 1.48% (37/2,499), and 1.27% (33/1,843) from 2019 to 2022, respectively. The prevalence was higher in winter 2020/2021 than during the same months 1 year before and after. We detected higher prevalence in the samples from September to November than in those collected during the remaining months of every year during the study period. The AIVs were isolated from Pungseocheon, Sapgyocheon, Bonggangcheon, Gokgyocheon, Bunamho, Joenjucheon, Mangyeonggang, Dongjingang and Geumgang and the prevalence was 2.22%, 4.40%, 1.28%, 2.37%, 1.66%, 1.37%, 1.81%, 1.38% and 0.64%, respectively (Table 2). The highest rate of AIVs isolation showed in Sapgyocheon (4.40%).
Table 1 . Prevalence of AIVs from 2019 to 2022 in South Korea.
Year | Number of collected samples | Number of AIV isolates | Prevalence of AIV (%) |
---|---|---|---|
2019.10 | 944 | 10 | 1.05 |
2019.11 | 932 | 11 | 1.18 |
2019.12 | 740 | 2 | 0.27 |
2020.01 | 130 | 0 | 0.00 |
2020.02 | 330 | 3 | 0.90 |
2020.03 | 172 | 1 | 0.58 |
2019.10∼2020.03 | 3,248 | 27 | 0.83 |
2020.09 | 100 | 18 | 18 |
2020.10 | 229 | 9 | 3.93 |
2020.11 | 200 | 1 | 0.5 |
2020.12 | 650 | 4 | 0.61 |
2021.01 | 640 | 3 | 0.46 |
2021.02 | 630 | 1 | 0.16 |
2021.03 | 50 | 1 | 2 |
2020.09∼2021.02 | 2,499 | 37 | 1.48 |
2021.11 | 708 | 28 | 3.95 |
2021.12 | 635 | 5 | 0.78 |
2021.11∼2022.01 | 1,843 | 33 | 1.79 |
Total | 7,590 | 97 | 1.27 |
Table 2 . Numbers of AIVs detected in wild bird species.
Location | Chungcheong-do | Jeolla-do | Total | |||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
Pungseo-cheon | Sapgyo-cheon | Bonggang-cheon | Gokgyo-cheon | Bunam-ho | Jeonju-cheon | Mangyeong-gang | Dongjin-gang | Geum-gang | ||||
Number of collected samples | 90 | 454 | 233 | 253 | 120 | 290 | 2,422 | 576 | 1,243 | |||
Number of AIVs isolates (Prevalence of AIV, %) | 2 (2.22) | 20 (4.40) | 3 (1.28) 33 (2.86) | 6 (2.37) | 2 (1.66) | 4 (1.37) | 44 (1.81) | 8 (1.38) 64 (1.41) | 8 (0.64) | 97 | ||
Numbers of host | 14 | 2 | 5 | 1 | 3 | 39 | 5 | 1 | 70 | |||
2 | 5 | 1 | 1 | 1 | 3 | 2 | 15 | |||||
1 | 1 | 4 | 6 | |||||||||
2 | 2 | |||||||||||
2 | 2 | |||||||||||
1 | 1 | |||||||||||
1 | 1 |
The hosts of all identified AIVs belonged to the order Anseriformes. Most were detected in the species
We isolated 25 HA-NA subtypes of AIVs, including nine HA (H3, H4, H5, H6, H7, H8, H9, H10 and H11) and eight NA (N1, N2, N3, N4, N6, N7, N8 and N9) (Table 3). The most frequently detected HA and NA subtypes was H5 (16.49%; n=16) and N6 (20.62%; n=20), respectively, except mixed subtypes. Both H4N6 (12.37%; n=12) and H5N3 (12.37%; n=12) were the most prevalent subtypes. Fig. 2 also shows yearly distributions of subtypes from 2019 to 2022. H4, H5 and H6 subtype identified in all seasons. The most diverse subtypes of AIVs were detected in Mangyeonggang.
Table 3 . Numbers of haemagglutinin (HA) and neuraminidase (NA) subtypes during AIVs surveillance in wild birds in South Korea, 2019∼2022.
Location | Chungcheong-do | Jeolla-do | Total (prevalence, %) | |||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
Pungseo-cheon | Sapgyo-cheon | Bonggang-cheon | Gokgyo-cheon | Bunam-ho | Jeonju-cheon | Mangyeong-gang | Dongjin-gang | Geum-gang | ||||
Numbers of subtypes | ||||||||||||
H3 | N6 | 3 | 3 (3.09) | |||||||||
N8 | 3 | 3 (3.09) | ||||||||||
N9 | 1 | 1 (1.03) | ||||||||||
H4 | N2 | 1 | 1 (1.03) | |||||||||
N3 | 1 | 1 (1.03) | ||||||||||
N6 | 2 | 1 | 1 | 1 | 7 | 12 (12.37) | ||||||
H5 | N2 | 3 | 3 (3.09) | |||||||||
N3 | 1 | 11 | 12 (12.37) | |||||||||
N8 | 1 | 1 (1.03) | ||||||||||
H6 | N1 | 2 | 1 | 1 | 4 (4.12) | |||||||
N2 | 7 | 1 | 8 (8.24) | |||||||||
N6 | 3 | 3 (3.09) | ||||||||||
N8 | 1 | 1 | 2 (2.06) | |||||||||
H7 | N1 | 1 | 1 (1.03) | |||||||||
N6 | 1 | 1 (1.03) | ||||||||||
N7 | 1 | 1 | 2 (2.06) | |||||||||
N9 | 1 | 1 (1.03) | ||||||||||
H8 | N4 | 1 | 1 (1.03) | |||||||||
H9 | N2 | 1 | 2 | 3 (3.09) | ||||||||
H10 | N4 | 1 | 1 | 2 (2.06) | ||||||||
N7 | 1 | 1 (1.03) | ||||||||||
H11 | N2 | 2 | 2 (2.06) | |||||||||
N3 | 4 | 4 (4.12) | ||||||||||
N8 | 1 | 1 (1.03) | ||||||||||
N9 | 5 | 5 (5.15) | ||||||||||
Mixed subtypes | 5 | 4 | 2 | 3 | 1 | 15 (15.4) | ||||||
HxNx | 2 | 1 | 1 | 4 (4.12) |
Global prevalence of AIV was 0.06% (0.30∼1.21%) (Barbara et al, 2017). However, the prevalence of AIVs in wild birds depends on host species, seasonality and locations (Munster et al, 2007). The higher prevalence of AIVs compared to that of global showed in this study (1.27%) and this result was thought to be due to active surveillance conducted in winter season and wild bird habitats.
In 2019/2020, HPAIVs were neither detected in wild bird feces nor at any poultry farms in South Korea (Jeong et al, 2020). However, in 2020/2021, the H5N8 subtype was identified at 109 poultry farms, and the novel H5N1 virus entered the country in late 2021 (Sagong et al, 2022). The higher prevalence of AIVs recorded in 2020/2021 might be explained by the fact that more active surveillance systems were implemented in wild bird habitats to prevent HPAIV outbreaks.
Most migratory birds returned to mid-central and western provinces of South Korea (Jeolla-do and Chungcheong-do) (Lee et al, 2020). We isolated AIVs in Chungcheong-do and Jeolla-do province and this result shows high population of wild birds is related to high isolation rates of AIVs. According to the National Institute of Biological Resources in South Korea, the migration season of wild birds can be divided into four stages: October to November, December to January, February to March, and April to August (Lee et al, 2020). Stage 1 represents autumn migration, and during this season, most migratory wild birds arrive in South Korea from China or Russia (Lee et al, 2020). In an earlier study conducted in South Korea, isolation rates of AIVs in wild bird feces increased during stage 1 but decreased during stage 2, which is consistent with the results of the current study (Shin et al, 2015). These findings suggest that many wild birds that are infected with AIVs migrate to South Korea during the autumn season. AIV surveillance is therefore particularly needed from October to November to prevent the spread of AIVs from wild birds to poultry farms.
The isolation rate of AIVs was especially high in the mallard (
The H4 subtype was distributed worldwide and showed high prevalence in wild birds (Tang et al, 2020). The H4N6 subtype was detected yearly during the study period, which is consistent with previous research. The H5 and H7 subtypes were also isolated, but except for the H5N8 virus, all other H5 and H7 subtypes were LPAIVs. In 2019/2020 and 2020/2021 mixed subtypes of AIVs were isolated in a single wild bird fecal sample, suggesting that coinfection with multiple subtypes of AIVs occurred in wild birds. Coinfection of wild birds by AIVs is important source of reassortment events that generate novel strains of AIVs (Fuller et al, 2010). Thus, even if LPAIVs, continuous genetic analysis of AIVs is required.
AIVs have zoonotic potential, with some subtypes able to infect mammals including humans (Mostafa et al, 2018). The US Centers for Disease Control and Prevention (CDC) have reported that most AIVs that cause severe symptoms and lead to death in humans belong to the H7N9 and H5N1 subtypes of HPAIVs. Human infections with AIVs have occurred, albeit not in South Korea. The World Health Organization International Health Regulations (WHO IHR) recorded 132 such cases from January 1, 2018 to April 4, 2022, and H9N2 LPAIV was identified as the most common virus subtype. Thus, since human infections caused by not only HPAIVs but also LPAIVs have been confirmed continuously and considering that H9N2 LPAIVs are frequently detected in wild birds in South Korea, continuous and active surveillance of AIVs in wild birds is essential to prevent their spread to mammals.
This research was supported by the Basic Science Research Program through the National Research Foundation of Korea (NRF), funded by the Ministry of Education (2019R1A6A1A03033084), as well as by a Government-sponsored R&D Fund for infectious disease research (GFID; HG18C0084). We would also like to express our gratitude to the editors of the Writing Center at Jeonbuk National University for their skilled English-language assistance.
No potential conflict of interest relevant to this article was reported.
Table 1 . Prevalence of AIVs from 2019 to 2022 in South Korea.
Year | Number of collected samples | Number of AIV isolates | Prevalence of AIV (%) |
---|---|---|---|
2019.10 | 944 | 10 | 1.05 |
2019.11 | 932 | 11 | 1.18 |
2019.12 | 740 | 2 | 0.27 |
2020.01 | 130 | 0 | 0.00 |
2020.02 | 330 | 3 | 0.90 |
2020.03 | 172 | 1 | 0.58 |
2019.10∼2020.03 | 3,248 | 27 | 0.83 |
2020.09 | 100 | 18 | 18 |
2020.10 | 229 | 9 | 3.93 |
2020.11 | 200 | 1 | 0.5 |
2020.12 | 650 | 4 | 0.61 |
2021.01 | 640 | 3 | 0.46 |
2021.02 | 630 | 1 | 0.16 |
2021.03 | 50 | 1 | 2 |
2020.09∼2021.02 | 2,499 | 37 | 1.48 |
2021.11 | 708 | 28 | 3.95 |
2021.12 | 635 | 5 | 0.78 |
2021.11∼2022.01 | 1,843 | 33 | 1.79 |
Total | 7,590 | 97 | 1.27 |
Table 2 . Numbers of AIVs detected in wild bird species.
Location | Chungcheong-do | Jeolla-do | Total | |||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
Pungseo-cheon | Sapgyo-cheon | Bonggang-cheon | Gokgyo-cheon | Bunam-ho | Jeonju-cheon | Mangyeong-gang | Dongjin-gang | Geum-gang | ||||
Number of collected samples | 90 | 454 | 233 | 253 | 120 | 290 | 2,422 | 576 | 1,243 | |||
Number of AIVs isolates (Prevalence of AIV, %) | 2 (2.22) | 20 (4.40) | 3 (1.28) 33 (2.86) | 6 (2.37) | 2 (1.66) | 4 (1.37) | 44 (1.81) | 8 (1.38) 64 (1.41) | 8 (0.64) | 97 | ||
Numbers of host | 14 | 2 | 5 | 1 | 3 | 39 | 5 | 1 | 70 | |||
2 | 5 | 1 | 1 | 1 | 3 | 2 | 15 | |||||
1 | 1 | 4 | 6 | |||||||||
2 | 2 | |||||||||||
2 | 2 | |||||||||||
1 | 1 | |||||||||||
1 | 1 |
Table 3 . Numbers of haemagglutinin (HA) and neuraminidase (NA) subtypes during AIVs surveillance in wild birds in South Korea, 2019∼2022.
Location | Chungcheong-do | Jeolla-do | Total (prevalence, %) | |||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
Pungseo-cheon | Sapgyo-cheon | Bonggang-cheon | Gokgyo-cheon | Bunam-ho | Jeonju-cheon | Mangyeong-gang | Dongjin-gang | Geum-gang | ||||
Numbers of subtypes | ||||||||||||
H3 | N6 | 3 | 3 (3.09) | |||||||||
N8 | 3 | 3 (3.09) | ||||||||||
N9 | 1 | 1 (1.03) | ||||||||||
H4 | N2 | 1 | 1 (1.03) | |||||||||
N3 | 1 | 1 (1.03) | ||||||||||
N6 | 2 | 1 | 1 | 1 | 7 | 12 (12.37) | ||||||
H5 | N2 | 3 | 3 (3.09) | |||||||||
N3 | 1 | 11 | 12 (12.37) | |||||||||
N8 | 1 | 1 (1.03) | ||||||||||
H6 | N1 | 2 | 1 | 1 | 4 (4.12) | |||||||
N2 | 7 | 1 | 8 (8.24) | |||||||||
N6 | 3 | 3 (3.09) | ||||||||||
N8 | 1 | 1 | 2 (2.06) | |||||||||
H7 | N1 | 1 | 1 (1.03) | |||||||||
N6 | 1 | 1 (1.03) | ||||||||||
N7 | 1 | 1 | 2 (2.06) | |||||||||
N9 | 1 | 1 (1.03) | ||||||||||
H8 | N4 | 1 | 1 (1.03) | |||||||||
H9 | N2 | 1 | 2 | 3 (3.09) | ||||||||
H10 | N4 | 1 | 1 | 2 (2.06) | ||||||||
N7 | 1 | 1 (1.03) | ||||||||||
H11 | N2 | 2 | 2 (2.06) | |||||||||
N3 | 4 | 4 (4.12) | ||||||||||
N8 | 1 | 1 (1.03) | ||||||||||
N9 | 5 | 5 (5.15) | ||||||||||
Mixed subtypes | 5 | 4 | 2 | 3 | 1 | 15 (15.4) | ||||||
HxNx | 2 | 1 | 1 | 4 (4.12) |
Kyung-Hee Kim, Hyun-Suk Lim, Jung-Woo Lee, Dae-Hyun Park, Chang-Ryoul Yang, Jae-Keun Cho
Korean J. Vet. Serv. 2021; 44(4): 209-216 https://doi.org/10.7853/kjvs.2021.44.4.209