EPIDEMIOLOGIC INVESTIGATION OF LEAD POISONING IN TRUMPETER AND TUNDRA SWANS IN WASHINGTON STATE, USA, 2000–2002
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...
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Veröffentlicht in: | Journal of wildlife diseases 2006-04, Vol.42 (2), p.345-358 |
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description | 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. |
doi_str_mv | 10.7589/0090-3558-42.2.345 |
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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.</description><identifier>ISSN: 0090-3558</identifier><identifier>EISSN: 1943-3700</identifier><identifier>DOI: 10.7589/0090-3558-42.2.345</identifier><identifier>PMID: 16870857</identifier><language>eng</language><publisher>United States: Wildlife Disease Association</publisher><subject>Animals ; Aspergillosis ; Aspergillosis - epidemiology ; Aspergillosis - mortality ; Aspergillosis - veterinary ; Aspergillus ; Bird Diseases - epidemiology ; Bird Diseases - mortality ; Birds ; Cause of Death ; Cygnus buccinator ; Cygnus columbianus columbianus ; Female ; Food Chain ; Food Contamination - analysis ; Lead - analysis ; lead poisoning ; Lead Poisoning - epidemiology ; Lead Poisoning - mortality ; Lead Poisoning - veterinary ; Male ; powerline collisions ; Prevalence ; Seasons ; TOXICOLOGY ; trumpeter swan ; tundra swan ; Washington - epidemiology ; waterfowl ; Wounds and Injuries - epidemiology ; Wounds and Injuries - mortality ; Wounds and Injuries - veterinary ; Wounds, Gunshot - epidemiology ; Wounds, Gunshot - mortality ; Wounds, Gunshot - veterinary</subject><ispartof>Journal of wildlife diseases, 2006-04, Vol.42 (2), p.345-358</ispartof><rights>Wildlife Disease Association 2006</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://bioone.org/doi/pdf/10.7589/0090-3558-42.2.345$$EPDF$$P50$$Gbioone$$H</linktopdf><link.rule.ids>109,314,776,780,27901,27902,52694</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/16870857$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Degernes, Laurel</creatorcontrib><creatorcontrib>Heilman, Sarah</creatorcontrib><creatorcontrib>Trogdon, Maureen</creatorcontrib><creatorcontrib>Jordan, Martha</creatorcontrib><creatorcontrib>Davison, Mike</creatorcontrib><creatorcontrib>Kraege, Don</creatorcontrib><creatorcontrib>Correa, Maria</creatorcontrib><creatorcontrib>Cowen, Peter</creatorcontrib><title>EPIDEMIOLOGIC INVESTIGATION OF LEAD POISONING IN TRUMPETER AND TUNDRA SWANS IN WASHINGTON STATE, USA, 2000–2002</title><title>Journal of wildlife diseases</title><addtitle>J Wildl Dis</addtitle><description>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.</description><subject>Animals</subject><subject>Aspergillosis</subject><subject>Aspergillosis - epidemiology</subject><subject>Aspergillosis - mortality</subject><subject>Aspergillosis - veterinary</subject><subject>Aspergillus</subject><subject>Bird Diseases - epidemiology</subject><subject>Bird Diseases - mortality</subject><subject>Birds</subject><subject>Cause of Death</subject><subject>Cygnus buccinator</subject><subject>Cygnus columbianus columbianus</subject><subject>Female</subject><subject>Food Chain</subject><subject>Food Contamination - analysis</subject><subject>Lead - analysis</subject><subject>lead poisoning</subject><subject>Lead Poisoning - epidemiology</subject><subject>Lead Poisoning - mortality</subject><subject>Lead Poisoning - veterinary</subject><subject>Male</subject><subject>powerline collisions</subject><subject>Prevalence</subject><subject>Seasons</subject><subject>TOXICOLOGY</subject><subject>trumpeter swan</subject><subject>tundra swan</subject><subject>Washington - epidemiology</subject><subject>waterfowl</subject><subject>Wounds and Injuries - epidemiology</subject><subject>Wounds and Injuries - mortality</subject><subject>Wounds and Injuries - veterinary</subject><subject>Wounds, Gunshot - epidemiology</subject><subject>Wounds, Gunshot - mortality</subject><subject>Wounds, Gunshot - veterinary</subject><issn>0090-3558</issn><issn>1943-3700</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2006</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNpFkc9OwkAQxjdGo_jnBTyYveiJ4uy_tnvcSMEm2BK6yHFT6FZriiiVEG--g2_ok7iI4mlmMr_vy2Q-hM4JdAIRymsACR4TIvQ47dAO42IPtYjkzGMBwD5q7YAjdNw0TwBUuOEQHRE_DCAUQQu9RsO4G93F6SDtxzc4Tu6jTMd9peM0wWkPDyLVxcM0ztIkTvpuj_VofDeMdDTCKuliPU66I4WziUqyzXaislsHaqfOtNJRG48z1cYUAL4-Pl2hp-igzOvGnv3WEzTuRfrm1vu5QA28KSPkzaOMlCWdiRJKTmWRi4JR6TNGqR8KyQvJLQ-LYGpnTOZsBj4tZUB8yInrct9nJ-hq6_uyXLyubPNm5lUzs3WdP9vFqjFEBkHIKHfgxS-4ms5tYV6W1Txfvpu_Jzngcgs8Vg-P62ppTTPP69rh1KzXa04NNe75joMtN60Wi2f7bwRmk5fZxGE2cZid5Bs6tnq0</recordid><startdate>20060401</startdate><enddate>20060401</enddate><creator>Degernes, Laurel</creator><creator>Heilman, Sarah</creator><creator>Trogdon, Maureen</creator><creator>Jordan, Martha</creator><creator>Davison, Mike</creator><creator>Kraege, Don</creator><creator>Correa, Maria</creator><creator>Cowen, Peter</creator><general>Wildlife Disease Association</general><general>Wildlife Dis Assoc</general><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>7SN</scope><scope>7U7</scope><scope>C1K</scope><scope>F1W</scope><scope>H95</scope><scope>L.G</scope></search><sort><creationdate>20060401</creationdate><title>EPIDEMIOLOGIC INVESTIGATION OF LEAD POISONING IN TRUMPETER AND TUNDRA SWANS IN WASHINGTON STATE, USA, 2000–2002</title><author>Degernes, Laurel ; Heilman, Sarah ; Trogdon, Maureen ; Jordan, Martha ; Davison, Mike ; Kraege, Don ; Correa, Maria ; Cowen, Peter</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-b311t-231ff2c5f0f429da5d3296332268594d94e48d7bec39a3c062f97160a162fa663</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2006</creationdate><topic>Animals</topic><topic>Aspergillosis</topic><topic>Aspergillosis - epidemiology</topic><topic>Aspergillosis - mortality</topic><topic>Aspergillosis - veterinary</topic><topic>Aspergillus</topic><topic>Bird Diseases - epidemiology</topic><topic>Bird Diseases - mortality</topic><topic>Birds</topic><topic>Cause of Death</topic><topic>Cygnus buccinator</topic><topic>Cygnus columbianus columbianus</topic><topic>Female</topic><topic>Food Chain</topic><topic>Food Contamination - analysis</topic><topic>Lead - analysis</topic><topic>lead poisoning</topic><topic>Lead Poisoning - epidemiology</topic><topic>Lead Poisoning - mortality</topic><topic>Lead Poisoning - veterinary</topic><topic>Male</topic><topic>powerline collisions</topic><topic>Prevalence</topic><topic>Seasons</topic><topic>TOXICOLOGY</topic><topic>trumpeter swan</topic><topic>tundra swan</topic><topic>Washington - epidemiology</topic><topic>waterfowl</topic><topic>Wounds and Injuries - epidemiology</topic><topic>Wounds and Injuries - mortality</topic><topic>Wounds and Injuries - veterinary</topic><topic>Wounds, Gunshot - epidemiology</topic><topic>Wounds, Gunshot - mortality</topic><topic>Wounds, Gunshot - veterinary</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Degernes, Laurel</creatorcontrib><creatorcontrib>Heilman, Sarah</creatorcontrib><creatorcontrib>Trogdon, Maureen</creatorcontrib><creatorcontrib>Jordan, Martha</creatorcontrib><creatorcontrib>Davison, Mike</creatorcontrib><creatorcontrib>Kraege, Don</creatorcontrib><creatorcontrib>Correa, Maria</creatorcontrib><creatorcontrib>Cowen, Peter</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>Ecology Abstracts</collection><collection>Toxicology Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 1: Biological Sciences & Living Resources</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><jtitle>Journal of wildlife diseases</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Degernes, Laurel</au><au>Heilman, Sarah</au><au>Trogdon, Maureen</au><au>Jordan, Martha</au><au>Davison, Mike</au><au>Kraege, Don</au><au>Correa, Maria</au><au>Cowen, Peter</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>EPIDEMIOLOGIC INVESTIGATION OF LEAD POISONING IN TRUMPETER AND TUNDRA SWANS IN WASHINGTON STATE, USA, 2000–2002</atitle><jtitle>Journal of wildlife diseases</jtitle><addtitle>J Wildl Dis</addtitle><date>2006-04-01</date><risdate>2006</risdate><volume>42</volume><issue>2</issue><spage>345</spage><epage>358</epage><pages>345-358</pages><issn>0090-3558</issn><eissn>1943-3700</eissn><abstract>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.</abstract><cop>United States</cop><pub>Wildlife Disease Association</pub><pmid>16870857</pmid><doi>10.7589/0090-3558-42.2.345</doi><tpages>14</tpages></addata></record> |
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subjects | Animals Aspergillosis Aspergillosis - epidemiology Aspergillosis - mortality Aspergillosis - veterinary Aspergillus Bird Diseases - epidemiology Bird Diseases - mortality Birds Cause of Death Cygnus buccinator Cygnus columbianus columbianus Female Food Chain Food Contamination - analysis Lead - analysis lead poisoning Lead Poisoning - epidemiology Lead Poisoning - mortality Lead Poisoning - veterinary Male powerline collisions Prevalence Seasons TOXICOLOGY trumpeter swan tundra swan Washington - epidemiology waterfowl Wounds and Injuries - epidemiology Wounds and Injuries - mortality Wounds and Injuries - veterinary Wounds, Gunshot - epidemiology Wounds, Gunshot - mortality Wounds, Gunshot - veterinary |
title | EPIDEMIOLOGIC INVESTIGATION OF LEAD POISONING IN TRUMPETER AND TUNDRA SWANS IN WASHINGTON STATE, USA, 2000–2002 |
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