Deaths among Wild Birds during Highly Pathogenic Avian Influenza A(H5N8) Virus Outbreak, the Netherlands.
In May-June 2016, a novel reassortant of HPAI virus subtype H5N8 clade 18.104.22.168a was detected in diseased waterbirds in China (5) and on the border between Russia and Mongolia (6). In October 2016, a similar H5N8 strain was found in a dead mute swan (Cygnus olor) in Hungary (7). H5N8 viruses then spread rapidly across Europe, causing widespread death among wild waterbirds (8).
Concurrent with first detections in Austria, Germany, and Denmark, an H5N8 outbreak started in the Netherlands in early November 2016 (7). Unlike previous H5N8 outbreaks in the Netherlands during 2014-2015 (9,10), increased deaths among wild birds were observed this time.
To quantify deaths among species groups with known susceptibility (4,11) or that tested positive for H5N8 during the outbreak, we assembled daily mortality data from organizations gathering death reports or removing carcasses in the Netherlands during November 2016-January 2017 (online Technical Appendix 1 Table 1, https://wwwnc. cdc.gov/EID/article/23/12/17-1086-Techapp1.xlsx). This collection was facilitated by close cooperation between ornithologists, virologists, animal health organizations, and other organizations involved in managing the H5N8 outbreak. After potential double-counts were excluded as much as possible, [approximately equal to]13,600 wild birds of 71 species were reported dead (Table); 49% of all carcasses were identified by species, most of which were tufted duck (Aythya fuligula [39%]) and Eurasian wigeon (Anas penelope [37%]). Unidentified waterbird carcasses probably also mostly represented these species. H5N8 infection was confirmed in 21 species and not detected among the low numbers of sampled birds representing 13 other species (online Technical Appendix 1 Table 2).
After the first H5N8 detection in diseased water-birds on November 8, hundreds of carcasses were found at Gouwzee (52[degrees]27'09"N, 5[degrees]04'07"E) and Wolderwijd (52[degrees]20'51"N, 5[degrees]34'20"E). Deaths at these locations peaked within 10 days, with [approximately equal to]5,300 carcasses reported by November 18 (Figure 1). An estimated 85% were tufted ducks. Other species found dead during this period included common pochard (Aythya ferina [6%]) and Eurasian coot (Fulica atra [4%]), in addition to great crested grebe (Podiceps cristatus), mute swan, greater scaup (Aythya marila), and several goose and gull species (each <1%).
Beginning in late November, outbreak hotspots moved from open water to water-rich agricultural areas (Figure 1; Video, https://wwwnc.cdc.gov/EID/article/23/12/17-1086-V1.htm). Deaths predominantly among Eurasian wigeon were reported from the island of Texel ([approximately equal to]883 birds) and the provinces Friesland ([approximately equal to]2,371), Noord-Holland ([approximately equal to]1,375), and Zuid-Holland ([approximately equal to]732). Reports of dead gulls, raptors and corvids, presumably infected after scavenging on carcasses, also increased.
Because these data are based on numbers of reported carcasses, they provide an underestimation of actual deaths. Although carcass detection rates during daily searches at Gouwzee and Wolderwijd were estimated to be 90%-95% (C. Oshaar, pers. comm., June 12, 2017), search efficiency was probably much lower at other outbreak hotspots. Collection rates of waterbird carcasses during typical avian botulism outbreaks are 10%-25% (12), suggesting that the number of carcasses reported during this H5N8 outbreak represented a limited proportion of total deaths.
We screened a relatively small proportion of carcasses for HPAI virus by real-time reverse transcription on tracheal and cloacal swab samples. We then determined pathogenicity and N-subtype by sequencing, as previously described (9,13). Testing confirmed H5N8 infection in a large proportion of sampled tufted ducks, Eurasian wigeons, gulls, raptors, and corvids (Table); another HPAI virus subtype was detected only twice (H5N5 in tufted duck and mute swan).
We used the public science database of Sovon (Dutch Center for Field Ornithology, Nijmegen, the Netherlands) to compare the number of deaths per species group during November 2016-January 2017 with those occurring in the same timeframe from 2010-2011 to 2015-2016 (Figure 2). Death counts among diving ducks (including tufted ducks) were >2,000 times higher than average during November 2016-January 2017, and the relative prevalence of deaths substantially increased (4-177 times) for dabbling ducks, herons, geese, swans, and corvids. The same analysis based on another database (http://www.waarneming.nl) yielded similar results (online Technical Appendix 2 Figure, https://wwwnc.cdc.gov/EID/article/23/12/17-1086-Techapp2.pdf).
The elevated number of deaths among wild birds raises concern about potential population effects. After accounting for detection probability (12), we found that up to 5% of the wintering populations of tufted ducks and Eurasian wigeons in the Netherlands might have died. In addition, 2%-10% of the wintering population of great black-backed gulls (Larus marinus) and 11%-39% of the wintering population of peregrine falcons (Falco peregrinus) were similarly affected. Stronger effects were observed locally. At Gouwzee, [approximately equal to]6,000 tufted ducks were counted in December after [approximately equal to]2,000 of them had died in November. Assuming that no migration occurred, we estimate that up to 25% of the local population of tufted ducks might have died, which might affect population dynamics substantially. Additional studies are needed to evaluate long-term impacts on these populations and to elucidate why high numbers of birds survived or escaped infection.
The first H5N8 outbreak among poultry in the Netherlands occurred on November 25, two weeks after the first detection in wild waterbirds and coinciding with increasing death reports in Eurasian wigeons. This time lag might be related to the limited mobility of wintering Aythya ducks, which, in contrast to Eurasian wigeons, rarely fly over land between foraging and roosting sites. Wild bird ecology might thus affect infection risk among poultry, which was further explored by researchers using network analyses of virus sequences obtained from wild birds and poultry during the same outbreak (14).
The quality of reporting of wild bird deaths during this H5N8 outbreak was vastly improved compared with earlier outbreaks, when species names, death rates, and spatiotemporal patterns of deaths were rarely recorded. However, documentation and management of future outbreaks in wild birds can be further improved. To contain outbreaks and minimize losses in the poultry sector, early HPAI virus detection in wild birds is crucial. Monitoring of wild bird deaths can be optimized (e.g., by timely investigation at sites where migratory birds first arrive, especially when surrounding countries report outbreaks). Awareness of clinical signs in wild birds (online Technical Appendix 2) might facilitate this effort. Detailed, real-time, active and passive surveillance during outbreaks might help assess acute risk for infection in poultry. Such surveillance would require central coordination of information exchange during outbreaks, which would also facilitate evaluation afterward.
Readily available specific guidelines would help management of HPAI virus outbreaks in wild birds. National HPAI preparedness plans should include specific protocols about how to handle carcasses (e.g., biosafety and disposal instructions) and what to report (e.g., species, number of birds, demographic parameters, and presence of leg bands). Moreover, sufficient resources should be available for adequate sampling and testing of specimens to rule out other diseases and to track virus dynamics during an outbreak.
Our findings indicate that the 2016-2017 H5N8 outbreaks in the Netherlands were associated with unprecedented high HPAI-related mortality rates in a wide range of wild bird species. These latest H5N8 outbreaks have shifted the paradigm of wild birds as unaffected agents of HPAI viruses, with increasing concerns about potential effects on their populations. The Netherlands and other important staging areas for migratory waterbirds across Eurasia that have been affected by the 2016-2017 H5N8 outbreaks (3,15) are at risk for substantial numbers of bird deaths during future HPAI outbreaks. International responsibilities regarding migratory bird populations should stimulate national authorities to avert HPAI outbreaks not only in poultry and humans but also in wild birds.
We thank Menno Hornman, Jeroen Nienhuis, Natasha Buijs, Hanna Hesselink, Hisko de Vries, Eckard Boot, Cor Oshaar, Jan Regeling, Jan Roelsma, Geert Hamstra, Marko Cortel, Rommert Cazemier, Hoogheemraadschap Hollands Noorderkwartier, Natuurmonumenten, Rijkswaterstaat, Staatsbosbeheer, and Wetterskip Fryslan for kindly sharing data on wild bird deaths.
Financial support for this study was provided by the Dutch Ministry of Economic Affairs and the US National Health Institute's National Institute of Allergy and Infectious Diseases (contract no. HHSN272201400008C).
Dr. Kleyheeg is a postdoctoral researcher at the Max Planck Institute for Ornithology, Radolfzell am Bodensee, Germany. His primary research interest is the relation between bird movement and the spread of pathogenic and nonpathogenic organisms.
(1.) Lai S, Qin Y, Cowling BJ, Ren X, Wardrop NA, Gilbert M, et al. Global epidemiology of avian influenza A H5N1 virus infection in humans, 1997-2015: a systematic review of individual case data. Lancet Infect Dis. 2016;16:e108-18. http://dx.doi.org/10.1016/ S1473-3099(16)00153-5
(2.) World Health Organization. Cumulative number of confirmed human cases of avian influenza A(H5N1) reported to WHO [cited 2017 June 12]. http://www.who.int/influenza/human_ animal_interface/H5N1_cumulative_table_archives
(3.) Keawcharoen J, van Riel D, van Amerongen G, Bestebroer T, Beyer WE, van Lavieren R, et al. Wild ducks as long-distance vectors of highly pathogenic avian influenza virus (H5N1). Emerg Infect Dis. 2008;14:600-7. http://dx.doi.org/10.3201/ eid1404.071016
(4.) Lycett SJ, Bodewes R, Pohlmann A, Banks J, Banyai K, Boni MF, et al. Role for migratory wild birds in the global spread of avian influenza H5N8. Science. 2016;354:213-7. http://dx.doi.org/ 10.1126/science.aaf8852
(5.) Li M, Liu H, Bi Y, Sun J, Wong G, Liu D, et al. Highly pathogenic avian influenza A(H5N8) virus in wild migratory birds, Qinghai Lake, China. Emerg Infect Dis. 2017;23:637-41. http://dx.doi.org/10.3201/eid2304.161866
(6.) Lee DH, Sharshov K, Swayne DE, Kurskaya O, Sobolev I, Kabilov M, et al. Novel Reassortant clade 22.214.171.124 avian influenza A(H5N8) virus in wild aquatic birds, Russia, 2016. Emerg Infect Dis. 2017;23:359-60. http://dx.doi.org/10.3201/ eid2302.161252
(7.) World Organisation for Animal Health (OIE). Avian influenza portal [cited 2017 May 29]. http://www.oie.int/animal-health-in-the-world/update-on-avian-influenza
(8.) More S, Bicout D, Botner A, Butterworth A, Calistri A, et al. Urgent request on avian influenza. EFSA J. 2017;15:4687.
(9.) Verhagen JH, van der Jeugd HP, Nolet BA, Slaterus R, Kharitonov SP, de Vries PP, et al. Wild bird surveillance around outbreaks of highly pathogenic avian influenza A(H5N8) virus in the Netherlands, 2014, within the context of global flyways. Euro Surveill. 2015;20:21069. http://dx.doi.org/10.2807/1560-7917. ES2015.20.12.21069
(10.) Poen MJ, Verhagen JH, Manvell RJ, Brown I, Bestebroer TM, van der Vliet S, et al. Lack of virological and serological evidence for continued circulation of highly pathogenic avian influenza H5N8 virus in wild birds in the Netherlands, 14 November 2014 to 31 January 2016. Euro Surveill. 2016;21:30349. http://dx.doi.org/10.2807/1560-7917.ES.2016.21.38.30349
(11.) Breed AC, Harris K, Hesterberg U, Gould G, Londt BZ, Brown IH, et al. Surveillance for avian influenza in wild birds in the European Union in 2007. Avian Dis. 2010;54(Suppl):399-404. http://dx.doi.org/10.1637/8950-053109-Reg.1
(12.) Bollinger TK, Evelsizer DD, Dufour KW, Soos C, Clark RG, Wobeser G, et al. Ecology and management of avian botulism on the Canadian prairies [cited 2017 Jun 20]. http://www. phjv.ca/pdf/BotulismReport_FINAL_FullReport_Aug2011.pdf
(13.) Bouwstra RJ, Koch G, Heutink R, Harders F, van der Spek A, Elbers ARW, et al. Phylogenetic analysis of highly pathogenic avian influenza A(H5N8) virus outbreak strains provides evidence for four separate introductions and one between-poultry farm transmission in the Netherlands, November 2014. Euro Surveill. 2015;20:21174. http://dx.doi.org/10.2807/1560-7917.ES2015.20.26.21174
(14.) Beerens N, Heutink R, Bergervoet SA, Harders F, Bossers A, Koch G. Multiple reassorted viruses as cause of highly pathogenic avian influenza virus A(H5N8) epidemic, the Netherlands, 2016. Emerg Infect Dis. 2017;23:1974-81.
(15.) Pohlmann A, Starick E, Harder T, Grund C, Hoper D, Globig A, et al. Outbreaks among wild birds and domestic poultry caused by reassorted influenza A (H5N8) clade 2.3. 4.4 viruses, Germany, 2016. Emerg Infect Dis. 2017;23:633-6. http://dx.doi.org/10.3201/ eid2304.161949
Address for correspondence: Erik Kleyheeg, Max Planck Institute for Ornithology, Am Obstberg 1, 78315 Radolfzell am Bodensee, Germany; email: email@example.com
Erik Kleyheeg,  Roy Slaterus, Rogier Bodewes, Jolianne M. Rijks, Marcel A.H. Spierenburg, Nancy Beerens, Leon Kelder, Marjolein J. Poen, Jan A. Stegeman, Ron A.M. Fouchier, Thijs Kuiken,  Henk P. van der Jeugd 
Author affiliations: Dutch Center for Avian Migration and Demography, Wageningen, the Netherlands (E. Kleyheeg, H.P. van der Jeugd); Sovon, Dutch Center for Field Ornithology, Nijmegen, the Netherlands (R. Slaterus); Utrecht University, Utrecht, the Netherlands (R. Bodewes, J.A. Stegeman); Dutch Wildlife Health Center, Utrecht (J.M. Rijks); Netherlands Food and Consumer Product Safety Authority, Utrecht (M.A.H. Spierenburg); Wageningen Bioveterinary Research, Lelystad, the Netherlands (N. Beerens); Staatsbosbeheer, Amersfoort, the Netherlands (L. Kelder); Erasmus Medical Center, Rotterdam, the Netherlands (M.J. Poen, R.A.M. Fouchier, T. Kuiken)
 Current affiliation: Max Planck Institute for Ornithology, Radolfzell am Bodensee, Germany.
 These senior authors contributed equally to this article.
Caption: Figure 1. Spatiotemporal pattern of wild bird deaths during an outbreak of HPAI A(H5H8) virus, the Netherlands, November 2016-January 2017. A) Outbreak chronology in tufted duck (red); Eurasian wigeon (blue); unidentified carcasses (light gray), probably also mostly tufted duck and Eurasian wigeon; and all other species combined (dark gray). Dashed vertical lines depict the first detections in wild birds and in poultry in the Netherlands. B-D) Spatial overview of the reported cumulative number of deaths in November 2016 (B), December 2016 (C), and January 2017 (D). Each point on the maps is a pie chart giving the proportions of the respective species (groups) at that location and their size is scaled to the [log.sub.10] of the number of reported carcasses. Yellow triangles mark the locations of outbreaks in commercial poultry holdings. Only locations where [greater than or equal to]3 dead birds were reported are shown. HPAI, highly pathogenic avian influenza.
Caption: Figure 2. Relative number of deaths among wild birds during an outbreak of highly pathogenic avian influenza A(H5N8) virus, the Netherlands, November 2016-January 2017. Number of reported deaths during November 2016-January 2017 (red asterisks) is shown relative to the normalized number of deaths reported over the same timeframe in the previous 5 years (average is 1, error bars indicate maximum and minimum from 2011-2012 to 2015-2016). The y-axis is on a log-scale (e.g., reported deaths among diving ducks during 2016-2017 was >2,000 times greater than the average reported in the previous 5 years). Within species groups, numbers of deaths are averaged over species. Data from Sovon (Dutch Center for Field Ornithology, Nijmegen, the Netherlands). A graph of the same analysis based on data from the Nature Information Foundation (http://www.waarneming.nl) was also plotted (online Technical Appendix 2, https://wwwnc.cdc.gov/EID/article/23/12/17-1086-Techapp2.pdf).
Table. Reported bird species, winter population size estimates, number of carcasses, and rRT-PCR test results per incident during outbreak of HPAI A(H5N8) virus, the Netherlands, November 2016-January 2017 * Maximum estimated Avian family and species (common name) winter population, x1,000 ([dagger]) Anatidae (waterbirds) Anas penelope (Eurasian wigeon) 680-920 Aythya fuliqula (tufted duck) 190-230 Unidentified waterfowl Podicipedidae (grebes) Ardeidae (herons) ([section]) Phalacrocoracidae (comorants) Rallidae (rallids) Scolopacidae (shorebirds) ([paragraph]) Laridae (gulls) Larus marinus (great black-backed gull) 7.4-13 Accipitridae (hawks) Falconidae (falcons) Falco pereqrinus (peregrine falcon) 0.36-0.52 Corvidae (corvids) Aves indet. (unidentified) Total Avian family and species (common name) No. carcasses Anatidae (waterbirds) 7,326 Anas penelope (Eurasian wigeon) 2,511 Aythya fuliqula (tufted duck) 2,633 Unidentified waterfowl 1,771 Podicipedidae (grebes) 31 Ardeidae (herons) ([section]) 165 Phalacrocoracidae (comorants) 50 Rallidae (rallids) 279 Scolopacidae (shorebirds) ([paragraph]) 103 Laridae (gulls) 698 Larus marinus (great black-backed gull) 78 Accipitridae (hawks) 119 Falconidae (falcons) 23 Falco pereqrinus (peregrine falcon) 16 Corvidae (corvids) 88 Aves indet. (unidentified) 4,708 Total 13,590 HPAI incidents Avian family and species (common name) tested ([double dagger]) Anatidae (waterbirds) 51/134 Anas penelope (Eurasian wigeon) 18/18 Aythya fuliqula (tufted duck) 8/11 Unidentified waterfowl 23/95 Podicipedidae (grebes) 3/5 Ardeidae (herons) ([section]) 0/13 Phalacrocoracidae (comorants) 1/2 Rallidae (rallids) 1/9 Scolopacidae (shorebirds) ([paragraph]) 0/2 Laridae (gulls) 12/28 Larus marinus (great black-backed gull) 5/5 Accipitridae (hawks) 4/17 Falconidae (falcons) 3/4 Falco pereqrinus (peregrine falcon) 3/4 Corvidae (corvids) 3/10 Aves indet. (unidentified) 4/28 Total 84/255 * Incidents are defined as death reports of a species per site per day. HPAI, highly pathogenic avian influenza; rRT-PCR, real-time reverse transcription PCR. ([dagger]) Population estimates represent the lowest and highest yearly maxima for the Netherlands during 2009-2014. Data from Sovon (Dutch Center for Field Ornithology, Nijmegen, the Netherlands). ([double dagger]) Number of positive versus all tested incidents are presented (number positive/number tested), based on infection data from the Netherlands Food and Consumer Product Safety Authority, Dutch Wildlife Health Center, Wageningen Bioveterinary Research, and Erasmus Medical Center. ([section]) H5N8 HPAI virus infection in grey heron (Ardea cinerea) was confirmed elsewhere in Europe (8). ([paragraph]) Eurasian woodcocks (Scolopax rusticola) are more prone than other species to window collisions during nocturnal migration; thus, their deaths (54 carcasses reported) might not be related to HPAI.
|Printer friendly Cite/link Email Feedback|
|Author:||Kleyheeg, Erik; Slaterus, Roy; Bodewes, Rogier; Rijks, Jolianne M.; Spierenburg, Marcel A.H.; Beeren|
|Publication:||Emerging Infectious Diseases|
|Date:||Dec 1, 2017|
|Previous Article:||Avian Influenza A(H7N2) Virus in Human Exposed to Sick Cats, New York, USA, 2016.|
|Next Article:||December 2015: Zoonotic Infections.|