Degernes Laurel, Heilman Sarah, Trogdon Maureen, Jordan Martha, Davison Mike, Kraege Don, Correa Maria, Cowen Peter
Department of Clinical Sciences, College of Veterinary Medicine, North Carolina State University, Raleigh, North Carolina 27606, USA.
J Wildl Dis. 2006 Apr;42(2):345-58. doi: 10.7589/0090-3558-42.2.345.
An observational study was conducted to determine the proportionate mortality of wild trumpeter (Cygnus buccinator) and tundra (Cygnus columbianus columbianus) swans that died during the winters of 2000-02 in northwestern Washington State, USA. Among 400 swans necropsied, 81% were lead poisoned (302/365 trumpeter swans; 20/35 tundra swans). Mortality started in mid-November and peaked from late December through mid-February; swan mortality that was not associated with lead poisoning was uniformly lower throughout the winter months. Lead poisoning was 24 times more likely to be the cause of death in swans found in Whatcom County compared to swans found in other locations in northwestern Washington State (95% CI: 12.7, 47.0). Mortality attributable to lead poisoning was twice as likely in adults as in juveniles (95% CI: 1.0, 4.2). Aspergillosis was documented in 62 trumpeter and two tundra swans, including 37 swans in which mortality was caused by lead poisoning. Males were twice as likely as females to have aspergillosis (95% CI: 1.1, 3.8). Traumatic injuries were documented in 37 trumpeter and seven tundra swans, including seven trumpeter swans with concurrent lead poisoning. Dead swans found outside Whatcom County were four times more likely to have traumatic injuries compared to those found in Whatcom County (95% CI: 1.6, 10.0). Overall, lead-poisoned swans were significantly less likely to have concurrent aspergillosis or traumatic injuries. There was no apparent association between grit ingestion (total mass or mass categorized by size) and lead poisoning or number of lead shot. Not surprisingly, lead-poisoned swans were more likely to have one or more lead shot compared to swans that died from other causes (OR 294; 95% CI: 92, 1,005); lead-poisoned swans were also more likely to have one or more nontoxic shot compared to swans that were not poisoned (OR 63; 95% CI: 19, 318). The source(s) of shot are unknown but likely are in or near Whatcom County, Washington.
一项观察性研究旨在确定2000 - 2002年冬季在美国华盛顿州西北部死亡的野生号手天鹅(疣鼻天鹅)和苔原天鹅(小天鹅指名亚种)的比例死亡率。在400只接受尸检的天鹅中,81%死于铅中毒(365只号手天鹅中有302只;35只苔原天鹅中有20只)。死亡从11月中旬开始,在12月下旬至2月中旬达到高峰;在整个冬季,与铅中毒无关的天鹅死亡率一直较低。与在华盛顿州西北部其他地区发现的天鹅相比,在霍特科姆县发现的天鹅死于铅中毒的可能性高24倍(95%置信区间:12.7,47.0)。成年天鹅因铅中毒导致死亡的可能性是幼年天鹅的两倍(95%置信区间:1.0,4.2)。在62只号手天鹅和2只苔原天鹅中记录到曲霉菌病,其中包括37只因铅中毒导致死亡的天鹅。雄性感染曲霉菌病的可能性是雌性的两倍(95%置信区间:1.1,3.8)。在37只号手天鹅和7只苔原天鹅中记录到外伤,其中包括7只同时患有铅中毒的号手天鹅。与在霍特科姆县发现的死天鹅相比,在该县以外发现的死天鹅有外伤的可能性高4倍(95%置信区间:1.6,10.0)。总体而言,铅中毒的天鹅同时患有曲霉菌病或外伤的可能性显著较低。沙砾摄入(总质量或按大小分类的质量)与铅中毒或铅弹数量之间没有明显关联。不出所料,与死于其他原因的天鹅相比,铅中毒的天鹅更有可能有一枚或多枚铅弹(比值比294;95%置信区间:92,1005);与未中毒的天鹅相比,铅中毒的天鹅也更有可能有一枚或多枚无毒子弹(比值比63;95%置信区间:19,318)。子弹的来源不明,但可能在华盛顿州的霍特科姆县或其附近。