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2 Southeastern Cooperative Wildlife Diseases Study, Department of Population Health, College of Veterinary Medicine, The University of Georgia, Athens, Georgia 30602, USA
3 Corresponding author (email: dstall{at}vet.uga.edu)
| ABSTRACT |
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| INTRODUCTION |
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Like most diseases, the epidemiology of AIV in wild birds is defined by interactions between the host, agent, and environment. This simple concept has important implications not only to understanding the epidemiology of wild-type AIV but also to understanding potential impacts associated with the introduction of HPAI viruses into wild bird populations.
| The host and host populations |
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Among migratory birds AIV prevalence can vary greatly according to season and location, and because individual species (and populations within species) exhibit different migratory behaviors, habitat preferences, and geographic ranges, individual species within these reservoir groups may play distinct but important roles in the epidemiology of AIV. As a general model, AIV prevalence in ducks peaks in late summer and early fall. This is associated with premigration staging (Hinshaw et al., 1985) and is clearly the pattern seen in mallards in North America. The pattern is attributed to increased concentrations of susceptible hatching-year birds, leading to AIV infection rates that exceed 30% in juveniles at this time. However, in blue-winged teal (Anas discors), an earlier and more long-distance migrant, a more complex pattern emerges. High prevalence rates are recorded when teal are associated with mallards on northern staging areas, but these birds represent only a portion of the continental population of teal. In August and September, very large numbers of blue-winged teal have already left the staging areas and have arrived on wintering areas. Prevalence rate in this portion of the teal population is substantially lower (approximately 8% of these birds are infected in September) (Stallknecht et al., 1990a). These same birds eventually migrate further to wintering areas in both Central and South America and may provide a link for the exchange of AIVs between continents. This scenario suggests that blue-winged teal, by escaping the force of infection in northern staging areas, may represent an important species in the maintenance of AIV through the winter migration period, as evidenced by isolation of AIVs from this species prior to leaving the wintering grounds for spring migration (Hanson et al., 2005). These are just two of many duck species, and it is very possible that individual species contribute differently to the AIV transmission and maintenance cycles. Although ducks are a very well-studied group with regards to the epidemiology of AIV, there are many species and populations worldwide for which little information is available.
The temporal patterns observed in ducks correspond to consistent spatial patterns. In general, AIV prevalence in North America is highest in waterfowl staging areas in Canada and the northern United States (Hinshaw et al., 1985). During migration, prevalence rapidly decreases, and on wintering areas AIV prevalence often is lower than 1–2% (Stallknecht and Shane, 1988). Low AIV prevalence estimates also occur during winter in ducks in Europe (Fouchier et al., 2003).
Spatial and temporal patterns in Charadriiformes are more difficult to understand. A consistent spatial relationship is observed with ruddy turnstones during spring migration stopovers at Delaware Bay (Kawaoka et al., 1988; Hanson, 2002; Krauss et al., 2004); however, this is the only site, worldwide, where consistent AIV isolations from shorebirds have been reported. In most cases, reported prevalence rates from these species are either very low or negative (Stallknecht, 1998; Hanson, 2002; Fouchier et al., 2003). The epidemiology of AIV in this group of birds is far from understood and as with ducks there are many species for which no information is available.
| The viruses |
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In shorebirds and gulls, AIV subtype diversity is not well understood, but differences exist between Charadriiforme species as compared to ducks (Kawaoka et al., 1988; Hanson, 2002; Krauss et al., 2004). To date, nine subtypes of AIVs occur more often in shorebirds than ducks including the H5, H7, H9, and H13 (Krauss et al., 2004). It is important to understand that existing data on subtype diversity in shorebirds are limited in scope with most isolates recovered from one species (ruddy turnstone) at one location (Delaware Bay, USA).
| The environment |
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Despite the recognized importance of fecal/oral transmission of these viruses in wild bird populations, existing data on AIV persistence in water are extremely limited. The potential for environmental persistence of these viruses was reported initially by Webster et al. (1978) using A/ Duck/Memphis/546/74 H3N2 in both fecal material and nonchlorinated river water. Subsequent to this work, AIV persistence was evaluated in feces (Beard et al., 1984; Lu et al., 2003) and allantoic fluid (Lu et al., 2003) and in all cases infectivity was relatively short-lived (days). Other than the original work done by Webster et al. (1978), only three studies (Stallknecht et al., 1990b, c; Brown et al., 2007) evaluated the persistence of AIV in water. These studies demonstrated that AIVs (including wild-type and HPAI H5N1 viruses) can persist for extended periods of time in water. Individual viruses differ in their ability to remain infective, and persistence is dependent on water temperature, pH, and salinity, within ranges that are normally encountered with surface water in the field.
| The HPAI H5N1 window |
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| CONCLUSIONS |
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| FOOTNOTES |
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Received for publication 30 December 2006.
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