SPATIAL AND TEMPORAL VARIATION IN LEAD LEVELS RELATED TO BODY CONDITION IN THE MISSISSIPPI VALLEY POPULATION OF CANADA GEESE
Concern over lead poisoning led to progressive prohibition of toxic shot to harvest waterfowl in the 1980's. Nevertheless, waterfowl remain susceptible to ingestion of lead shot because illegal use continues and spent shot persists in soil and wetland substrates. While mortality due to lead tox...
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Veröffentlicht in: | Journal of wildlife diseases 1999-04, Vol.35 (2), p.178-186 |
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description | Concern over lead poisoning led to progressive prohibition of toxic shot to harvest waterfowl in the 1980's. Nevertheless, waterfowl remain susceptible to ingestion of lead shot because illegal use continues and spent shot persists in soil and wetland substrates. While mortality due to lead toxicosis has subsided, sublethal effects may still affect survival and reproduction. We measured liver lead levels and body condition in 732 Canada geese (Branta canadensis interior) during July 1984 to April 1989 in southern Illinois (USA), east-central Wisconsin (USA), and northern Ontario (Canada). Although we sampled only individuals that were visibly healthy, 55 of 732 (7.5%) geese had elevated liver lead levels (>2 ppm). Lead levels of 46 (6.3%) geese indicated subclinical poisoning (2–6 ppm) and 9 (1.2%) geese had lead levels indicative of clinical poisoning (>6 ppm). A greater proportion of juveniles (14.3%) had elevated lead levels than did adults (6.0%), but there was no difference between genders. Lead levels were highest in autumn and winter in southern Illinois, but were low during nesting and summer, despite legal use of lead shot in northern Ontario during our study. Lead poisoning (≥5% of the population) was still evident during all seasons in juveniles, and during autumn and winter in adults, 5 to 10 yr after toxic shot was banned from areas where we collected geese during migration and winter. Elevated lead levels did not affect total body mass, lipid reserves, or mineral levels of geese we collected. Protein levels also were unaffected below 10 ppm, but there was evidence of decline at higher concentrations. Thus, it seems unlikely that lead exposure currently affects survival or reproduction of Mississippi Valley Population (MVP) geese via body condition, although other sublethal effects cannot be discounted. |
doi_str_mv | 10.7589/0090-3558-35.2.178 |
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Nevertheless, waterfowl remain susceptible to ingestion of lead shot because illegal use continues and spent shot persists in soil and wetland substrates. While mortality due to lead toxicosis has subsided, sublethal effects may still affect survival and reproduction. We measured liver lead levels and body condition in 732 Canada geese (Branta canadensis interior) during July 1984 to April 1989 in southern Illinois (USA), east-central Wisconsin (USA), and northern Ontario (Canada). Although we sampled only individuals that were visibly healthy, 55 of 732 (7.5%) geese had elevated liver lead levels (>2 ppm). Lead levels of 46 (6.3%) geese indicated subclinical poisoning (2–6 ppm) and 9 (1.2%) geese had lead levels indicative of clinical poisoning (>6 ppm). A greater proportion of juveniles (14.3%) had elevated lead levels than did adults (6.0%), but there was no difference between genders. Lead levels were highest in autumn and winter in southern Illinois, but were low during nesting and summer, despite legal use of lead shot in northern Ontario during our study. Lead poisoning (≥5% of the population) was still evident during all seasons in juveniles, and during autumn and winter in adults, 5 to 10 yr after toxic shot was banned from areas where we collected geese during migration and winter. Elevated lead levels did not affect total body mass, lipid reserves, or mineral levels of geese we collected. Protein levels also were unaffected below 10 ppm, but there was evidence of decline at higher concentrations. Thus, it seems unlikely that lead exposure currently affects survival or reproduction of Mississippi Valley Population (MVP) geese via body condition, although other sublethal effects cannot be discounted.</description><identifier>ISSN: 0090-3558</identifier><identifier>EISSN: 1943-3700</identifier><identifier>DOI: 10.7589/0090-3558-35.2.178</identifier><identifier>PMID: 10231744</identifier><language>eng</language><publisher>United States: Wildlife Disease Association</publisher><subject>Age Factors ; Animals ; Bird Diseases - epidemiology ; Bird Diseases - pathology ; Body Composition - drug effects ; body condition ; Branta canadensis ; Branta canadensis interior ; Canada geese ; Female ; Freshwater ; Geese ; Illinois - epidemiology ; Lead - analysis ; lead poisoning ; Lead Poisoning - epidemiology ; Lead Poisoning - pathology ; Lead Poisoning - veterinary ; Liver - chemistry ; Male ; Mississippi Valley population ; Ontario - epidemiology ; s ; seasonal variation ; sublethal effects ; USA, Mississippi R ; USA, Mississippi Valley ; Wisconsin - epidemiology</subject><ispartof>Journal of wildlife diseases, 1999-04, Vol.35 (2), p.178-186</ispartof><rights>1999 Wildlife Disease Association</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-b469t-38dc8842b05c76afec06eacfcc97f8e8016c75e6098ec7cd9cc3fbc4db99dfcf3</citedby></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://bioone.org/doi/pdf/10.7589/0090-3558-35.2.178$$EPDF$$P50$$Gbioone$$H</linktopdf><link.rule.ids>109,314,776,780,27901,27902,52694</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/10231744$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Wheeler, William E</creatorcontrib><creatorcontrib>Gates, Robert J</creatorcontrib><title>SPATIAL AND TEMPORAL VARIATION IN LEAD LEVELS RELATED TO BODY CONDITION IN THE MISSISSIPPI VALLEY POPULATION OF CANADA GEESE</title><title>Journal of wildlife diseases</title><addtitle>J Wildl Dis</addtitle><description>Concern over lead poisoning led to progressive prohibition of toxic shot to harvest waterfowl in the 1980's. Nevertheless, waterfowl remain susceptible to ingestion of lead shot because illegal use continues and spent shot persists in soil and wetland substrates. While mortality due to lead toxicosis has subsided, sublethal effects may still affect survival and reproduction. We measured liver lead levels and body condition in 732 Canada geese (Branta canadensis interior) during July 1984 to April 1989 in southern Illinois (USA), east-central Wisconsin (USA), and northern Ontario (Canada). Although we sampled only individuals that were visibly healthy, 55 of 732 (7.5%) geese had elevated liver lead levels (>2 ppm). Lead levels of 46 (6.3%) geese indicated subclinical poisoning (2–6 ppm) and 9 (1.2%) geese had lead levels indicative of clinical poisoning (>6 ppm). A greater proportion of juveniles (14.3%) had elevated lead levels than did adults (6.0%), but there was no difference between genders. Lead levels were highest in autumn and winter in southern Illinois, but were low during nesting and summer, despite legal use of lead shot in northern Ontario during our study. Lead poisoning (≥5% of the population) was still evident during all seasons in juveniles, and during autumn and winter in adults, 5 to 10 yr after toxic shot was banned from areas where we collected geese during migration and winter. Elevated lead levels did not affect total body mass, lipid reserves, or mineral levels of geese we collected. Protein levels also were unaffected below 10 ppm, but there was evidence of decline at higher concentrations. Thus, it seems unlikely that lead exposure currently affects survival or reproduction of Mississippi Valley Population (MVP) geese via body condition, although other sublethal effects cannot be discounted.</description><subject>Age Factors</subject><subject>Animals</subject><subject>Bird Diseases - epidemiology</subject><subject>Bird Diseases - pathology</subject><subject>Body Composition - drug effects</subject><subject>body condition</subject><subject>Branta canadensis</subject><subject>Branta canadensis interior</subject><subject>Canada geese</subject><subject>Female</subject><subject>Freshwater</subject><subject>Geese</subject><subject>Illinois - epidemiology</subject><subject>Lead - analysis</subject><subject>lead poisoning</subject><subject>Lead Poisoning - epidemiology</subject><subject>Lead Poisoning - pathology</subject><subject>Lead Poisoning - veterinary</subject><subject>Liver - chemistry</subject><subject>Male</subject><subject>Mississippi Valley population</subject><subject>Ontario - epidemiology</subject><subject>s</subject><subject>seasonal variation</subject><subject>sublethal effects</subject><subject>USA, Mississippi R</subject><subject>USA, Mississippi Valley</subject><subject>Wisconsin - epidemiology</subject><issn>0090-3558</issn><issn>1943-3700</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>1999</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqNkM1q3DAUhUVpaaZpX6CLVpt256kk_0haqmMlMSi2GXsCWQlblhMXT5xaGYZCH74anJYsC5dzueI7B3EA-IjRmsaMf0OIoyCMY-ZlTdaYsldghXkUBiFF6DVY_QPOwDvnfiBEYn-8BWcYkRDTKFqB31Up6kwoKPIU1vK6LLb-uBHbzD8XOcxyqKRIvdxIVcGtVKKWnizg9yK9hZsiT7O_YH0l4XVWVacpy8ynKCVvYVmUO7WkFRdwI3KRCngpZSXfgzd9Mzr74Xmfg92FrDdXgSous41QQRsl_CkIWWcYi0iLYkOTprcGJbYxvTGc9swyhBNDY5sgzqyhpuPGhH1roq7lvOtNH56Dr0vu4zz9PFj3pPeDM3Ycmwc7HZzGNKYsYaEHyQKaeXJutr1-nId9M__SGOlT5_pUqT5V6kUT72Te9Ok5_dDubffCspTsgS8LcD_c3R-H2Wq3b8bR40Qfj8cXQZ8Xrm8m3dzNg9O7iiAcIsIRT2LqCbQQ7TBND_Z_fvcHvFKYGw</recordid><startdate>19990401</startdate><enddate>19990401</enddate><creator>Wheeler, William E</creator><creator>Gates, Robert J</creator><general>Wildlife Disease Association</general><general>Wildlife Dis Assoc</general><scope>FBQ</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7TV</scope><scope>7U7</scope><scope>C1K</scope><scope>F1W</scope><scope>H95</scope><scope>H97</scope><scope>L.G</scope></search><sort><creationdate>19990401</creationdate><title>SPATIAL AND TEMPORAL VARIATION IN LEAD LEVELS RELATED TO BODY CONDITION IN THE MISSISSIPPI VALLEY POPULATION OF CANADA GEESE</title><author>Wheeler, William E ; Gates, Robert J</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-b469t-38dc8842b05c76afec06eacfcc97f8e8016c75e6098ec7cd9cc3fbc4db99dfcf3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>1999</creationdate><topic>Age Factors</topic><topic>Animals</topic><topic>Bird Diseases - epidemiology</topic><topic>Bird Diseases - pathology</topic><topic>Body Composition - drug effects</topic><topic>body condition</topic><topic>Branta canadensis</topic><topic>Branta canadensis interior</topic><topic>Canada geese</topic><topic>Female</topic><topic>Freshwater</topic><topic>Geese</topic><topic>Illinois - epidemiology</topic><topic>Lead - analysis</topic><topic>lead poisoning</topic><topic>Lead Poisoning - epidemiology</topic><topic>Lead Poisoning - pathology</topic><topic>Lead Poisoning - veterinary</topic><topic>Liver - chemistry</topic><topic>Male</topic><topic>Mississippi Valley population</topic><topic>Ontario - epidemiology</topic><topic>s</topic><topic>seasonal variation</topic><topic>sublethal effects</topic><topic>USA, Mississippi R</topic><topic>USA, Mississippi Valley</topic><topic>Wisconsin - epidemiology</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Wheeler, William E</creatorcontrib><creatorcontrib>Gates, Robert J</creatorcontrib><collection>AGRIS</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Pollution 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) 3: Aquatic Pollution & Environmental Quality</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>Wheeler, William E</au><au>Gates, Robert J</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>SPATIAL AND TEMPORAL VARIATION IN LEAD LEVELS RELATED TO BODY CONDITION IN THE MISSISSIPPI VALLEY POPULATION OF CANADA GEESE</atitle><jtitle>Journal of wildlife diseases</jtitle><addtitle>J Wildl Dis</addtitle><date>1999-04-01</date><risdate>1999</risdate><volume>35</volume><issue>2</issue><spage>178</spage><epage>186</epage><pages>178-186</pages><issn>0090-3558</issn><eissn>1943-3700</eissn><abstract>Concern over lead poisoning led to progressive prohibition of toxic shot to harvest waterfowl in the 1980's. Nevertheless, waterfowl remain susceptible to ingestion of lead shot because illegal use continues and spent shot persists in soil and wetland substrates. While mortality due to lead toxicosis has subsided, sublethal effects may still affect survival and reproduction. We measured liver lead levels and body condition in 732 Canada geese (Branta canadensis interior) during July 1984 to April 1989 in southern Illinois (USA), east-central Wisconsin (USA), and northern Ontario (Canada). Although we sampled only individuals that were visibly healthy, 55 of 732 (7.5%) geese had elevated liver lead levels (>2 ppm). Lead levels of 46 (6.3%) geese indicated subclinical poisoning (2–6 ppm) and 9 (1.2%) geese had lead levels indicative of clinical poisoning (>6 ppm). A greater proportion of juveniles (14.3%) had elevated lead levels than did adults (6.0%), but there was no difference between genders. Lead levels were highest in autumn and winter in southern Illinois, but were low during nesting and summer, despite legal use of lead shot in northern Ontario during our study. Lead poisoning (≥5% of the population) was still evident during all seasons in juveniles, and during autumn and winter in adults, 5 to 10 yr after toxic shot was banned from areas where we collected geese during migration and winter. Elevated lead levels did not affect total body mass, lipid reserves, or mineral levels of geese we collected. Protein levels also were unaffected below 10 ppm, but there was evidence of decline at higher concentrations. Thus, it seems unlikely that lead exposure currently affects survival or reproduction of Mississippi Valley Population (MVP) geese via body condition, although other sublethal effects cannot be discounted.</abstract><cop>United States</cop><pub>Wildlife Disease Association</pub><pmid>10231744</pmid><doi>10.7589/0090-3558-35.2.178</doi><tpages>9</tpages><oa>free_for_read</oa></addata></record> |
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subjects | Age Factors Animals Bird Diseases - epidemiology Bird Diseases - pathology Body Composition - drug effects body condition Branta canadensis Branta canadensis interior Canada geese Female Freshwater Geese Illinois - epidemiology Lead - analysis lead poisoning Lead Poisoning - epidemiology Lead Poisoning - pathology Lead Poisoning - veterinary Liver - chemistry Male Mississippi Valley population Ontario - epidemiology s seasonal variation sublethal effects USA, Mississippi R USA, Mississippi Valley Wisconsin - epidemiology |
title | SPATIAL AND TEMPORAL VARIATION IN LEAD LEVELS RELATED TO BODY CONDITION IN THE MISSISSIPPI VALLEY POPULATION OF CANADA GEESE |
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