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The successful reintroduction of Wild Turkeys ( Meleagris gallopavo) to Ontario, Canada, has led to established populations in southern portions of the province and currently allows for biannual hunting seasons. These populations geographically overlap Domestic Turkey farms, an important sector of the provincial agri-food industry. Potential pathogen transmission between Wild Turkeys and Domestic Turkeys ( Meleagris gallopavo) is a concern, because they are susceptible to infection with many of the same pathogens and have direct and indirect contact in outdoor or open farm settings and contaminated environmental substrates. However, data concerning potential poultry pathogens in Wild Turkeys in Canada are scarce. Thus, we assessed the prevalence and geographic distribution of geographically relevant viruses in Ontario Wild Turkeys. Oropharyngeal and cloacal swabs were tested for avian influenza viruses (AIV) by real-time reverse transcriptase (RT)-PCR ( n=207), pooled tissues for lymphoproliferative disease virus (LPDV; n=183) and reticuloendotheliosis virus ( n=119) by PCR, and gross skin lesions by real-time RT-PCR for avian poxvirus ( n=8). We sequenced a fragment of the gag polyprotein (p31) gene of LPDV on a subset ( n=10) of LPDV-positive samples for phylogenetic analysis and tested additional upland game bird species ( n=39) and domestic fowl for LPDV ( n=17). To the best of our knowledge, we document the first detection of LPDV in Wild Turkeys in Canada, with a prevalence of 65% (119/183). Phylogenetic analysis revealed that LPDV sequences from Ontario were genetically similar to other North American strains and did not group into separate clades. Reticuloendotheliosis virus was detected in 4% (5/119) of LPDV-positive Wild Turkeys. Grossly evident skin lesions from five Wild Turkeys tested positive for poxvirus, and all turkeys tested negative for AIV. This study provides evidence of LPDV circulation in Canada and provides a baseline for comparison with future Wild Turkey pathogen surveillance and monitoring in Ontario and elsewhere.

Following extirpation from Ontario, Canada in the early 1900s, Eastern Wild Turkeys (EWTs; Meleagris gallopavo silvestris) were successfully reintroduced to the province in 1984. Despite the subsequent establishment of robust populations and biannual hunting seasons, data on the circulation of potential pathogens in these birds are lacking. Similarly, the interface between EWTs and poultry is poorly understood and includes possible bidirectional pathogen transmission via direct or indirect contact. Mycoplasma and Eimeria spp. are potential pathogens in Galliformes, and our objective was to determine their prevalence and distribution in Ontario EWTs. During the 2015 spring hunting season (April and May), oropharyngeal swabs from 147 hunter-harvested and five opportunistically collected EWTs from southern Ontario were cultured for Mycoplasma spp. The intestinal or cloacal contents of 107 of these birds and an additional 24 opportunistically and biologist-collected EWTs were analyzed for Eimeria spp. using PCR or fecal flotation. At least one Mycoplasma spp. was isolated from 98.7% (150/152) of EWTs, with six species identified. Mycoplasma gallopavonis was identified most commonly in 96.7% (147/152), followed by Mycoplasma gallinaceum in 23.7% (36/152). Potential poultry pathogens ( Mycoplasma meleagridis, Mycoplasma iowae, and Mycoplasma synoviae) were isolated from swabs of five (3.3%) EWTs. Coinfections with up to three Mycoplasma spp. were detected in 36.8% (56/152) of EWTs. Most EWTs tested positive for Eimeria spp. oocysts (75.6%; 99/131). A subset of positive samples ( n=16) were characterized by PCR, which detected the following species: Eimeria meleagrimitis (93.8%), Eimeria adenoeides (93.8%), Eimeria gallopavonis (56.3%), and Eimeria meleagridis (12.5%). The majority (93.8%) of these samples were positive for more than one Eimeria spp. We showed that numerous, mostly nonpathogenic Mycoplasma and Eimeria spp. circulate in EWTs across southern Ontario, and this helped to establish baseline information for comparison with future surveillance and monitoring.

Since being successfully reintroduced into Ontario, Canada, wild turkey ( Meleagris gallopavo) populations have undergone robust growth and range expansion. This, along with increases in land use changes from human population growth and subsequent developments in agriculture and livestock production, has heightened opportunities for interactions between wild turkeys, domestic poultry, and humans. As conspecifics, wild and domestic turkeys are susceptible to infection and disease from many of the same pathogens. Thus, transmission by direct or indirect contact is a potential health threat to both groups, particularly with the overlapping range of wild turkeys in Ontario with numerous commercial and backyard poultry operations. However, these threats are difficult to assess due to knowledge gaps in the prevalence and geographic distribution of potential pathogens circulating among wild turkeys. We assessed for potentially pathogenic bacteria in free-ranging, hunter-harvested wild turkeys in Ontario ( n = 152) by cloacal swab culture for Campylobacter spp., Salmonella spp., and Escherichia coli and culture of lung and spleen for Pasteurella multocida, Ornithobacterium rhinotracheale, and Erysipelothrix rhusiopathiae. Antimicrobial resistance testing was also performed on E. coli isolates. Generic E. coli isolates were recovered from 69.1% (105/152) of wild turkeys tested, and two (1.9%) of these isolates exhibited resistance to azithromycin and one (1.0%) to ampicillin. Intermediate susceptibility to chloramphenicol was observed in one (1.0%) isolate. One (0.7%) wild turkey swab tested positive for C. jejuni, but no samples were positive for P. multocida, Salmonella spp., O. rhinotracheale, or E. rhusiopathiae. To our knowledge, this is the first survey of these bacteria and assessment for antimicrobial resistance among wild turkeys in Ontario.

The use of neonicotinoid insecticides in agriculture is now recognized for the health risks it poses to non-target wildlife, with associated honey bee mortality especially concerning. Research directed toward the presence and effects of these pesticides on terrestrial vertebrates that consume neonicotinoid-coated seeds, such as wild turkeys (Meleagris gallopavo silvestris), is lacking. This study used liquid chromatography attached to a tandem mass spectrometer to assess the liver from 40 wild turkeys for neonicotinoid and other pesticide residues and compared detected levels of these contaminants across the southern Ontario, Canada. Nine (22.5%) wild turkeys had detectible levels of neonicotinoid residues-clothianidin in eight, and thiamethoxam in three. Two (5.0%) of these turkeys had detectable levels of both clothianidin and thiamethoxam. Fuberidazole was detected in two (5.0%) wild turkeys. The highest level of thiamethoxam detected was 0.16 ppm, while clothianidin was detected at 0.12 ppm, and fuberidazole at 0.0094 ppm. Knowledge of exposure in free-ranging wildlife is critical for better understanding the effects of neonicotinoids on wildlife health; thus, these data help establish baseline data for southern Ontario wild turkeys and provide context for reference values in future analyses.

Water spread like liquid fire damaging more than 60,000 sq. ft. of clinical and support space, bringing the emergency department (ED) and operating rooms at St Joe's to an abrupt halt. Staff mobilized immediately, calling a hospital-wide Code Aqua (flood) and Code Green (evacuation) for the ED, and launching into action to save equipment and supplies worth millions of dollars. Our path to recovery has been difficult, but we have emerged stronger as an organization. The urgent necessity of rethinking care led to radical innovation, particularly in the flow and care of patients admitted through the ED.