Metal levels in body tissues, forage and fecal pellets of elk ( Cervus elaphus) living near the ore smelters at Sudbury, Ontario
Varying levels of metals from smelters were found in body tissues, forage and fecal pellets of elk. Ontario’s only free-ranging elk herd located at Burwash–French River has been subjected to the influence of historic copper–nickel–iron (Cu–Ni–Fe) ore smelting operations within the Sudbury area. Meta...
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description | Varying levels of metals from smelters were found in body tissues, forage and fecal pellets of elk.
Ontario’s only free-ranging elk herd located at Burwash–French River has been subjected to the influence of historic copper–nickel–iron (Cu–Ni–Fe) ore smelting operations within the Sudbury area. Metal levels in selected body tissues, preferred forage items and fecal pellets were determined, and their potential effects on health and reproductive viability assessed. Significant age effects were apparent in 13 out of 31 tissue metal values obtained, with most age-related differences attributable to elevated concentrations in fetal tissues. Cu and zinc (Zn) levels were four to six times higher in livers and one and a half to two times higher in the bones of fetuses as compared to post-natal animals. Enhanced pre-natal tissue burdens were also noted for cobalt (Co), Ni and lead (Pb) in muscles. However, mean cadmium (Cd) levels in kidney, liver and muscle tissues, as well as hepatic Fe concentrations, showed significant increases with age. Although Cd levels in the kidneys of older elk were still well below the reported threshold for irreversible organ damage, and not considered to be health-threatening, detailed histological study of the cortical tissues for subtle pathotoxicological effects may be warranted. Unlike renal and hepatic tissues, Cd concentrations in skeletal muscle were minimal and within levels considered acceptable for human consumption. Forage species collected in the elk range generally showed higher (two to eight times) Ni and Fe levels than the corresponding plants from a non-contaminated reference site. The highest Ni and Fe burdens were carried by eastern white cedar, a preferred winter food item for elk. No consistent site-related trends were demonstrated by Cu, Zn, Co, Pb, chromium (Cr) and Cd forage levels. Mean metal concentrations in fecal pellets generally exceeded the mean composite forage levels by a factor of 3, except for Ni, which was five times more concentrated in feces. Significantly elevated Ni and Fe levels in preferred browse species and fecal pellets of the Sudbury-area elk could be of concern and warrant further investigation. |
doi_str_mv | 10.1016/S0269-7491(00)00183-4 |
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Ontario’s only free-ranging elk herd located at Burwash–French River has been subjected to the influence of historic copper–nickel–iron (Cu–Ni–Fe) ore smelting operations within the Sudbury area. Metal levels in selected body tissues, preferred forage items and fecal pellets were determined, and their potential effects on health and reproductive viability assessed. Significant age effects were apparent in 13 out of 31 tissue metal values obtained, with most age-related differences attributable to elevated concentrations in fetal tissues. Cu and zinc (Zn) levels were four to six times higher in livers and one and a half to two times higher in the bones of fetuses as compared to post-natal animals. Enhanced pre-natal tissue burdens were also noted for cobalt (Co), Ni and lead (Pb) in muscles. However, mean cadmium (Cd) levels in kidney, liver and muscle tissues, as well as hepatic Fe concentrations, showed significant increases with age. Although Cd levels in the kidneys of older elk were still well below the reported threshold for irreversible organ damage, and not considered to be health-threatening, detailed histological study of the cortical tissues for subtle pathotoxicological effects may be warranted. Unlike renal and hepatic tissues, Cd concentrations in skeletal muscle were minimal and within levels considered acceptable for human consumption. Forage species collected in the elk range generally showed higher (two to eight times) Ni and Fe levels than the corresponding plants from a non-contaminated reference site. The highest Ni and Fe burdens were carried by eastern white cedar, a preferred winter food item for elk. No consistent site-related trends were demonstrated by Cu, Zn, Co, Pb, chromium (Cr) and Cd forage levels. Mean metal concentrations in fecal pellets generally exceeded the mean composite forage levels by a factor of 3, except for Ni, which was five times more concentrated in feces. Significantly elevated Ni and Fe levels in preferred browse species and fecal pellets of the Sudbury-area elk could be of concern and warrant further investigation.</description><identifier>ISSN: 0269-7491</identifier><identifier>EISSN: 1873-6424</identifier><identifier>DOI: 10.1016/S0269-7491(00)00183-4</identifier><identifier>PMID: 11428143</identifier><identifier>CODEN: ENVPAF</identifier><language>eng</language><publisher>Oxford: Elsevier Ltd</publisher><subject>Age Factors ; Age-dependent accumulation ; Animal, plant and microbial ecology ; Animals ; Applied ecology ; Biological and medical sciences ; Canada, Ontario ; Cervus elaphus ; Deer - physiology ; Diet ; Ecotoxicology, biological effects of pollution ; Effects of pollution and side effects of pesticides on vertebrates ; Elk ; Environmental Exposure ; Feces - chemistry ; Female ; Fundamental and applied biological sciences. Psychology ; Industry ; Kidney - physiology ; Liver - physiology ; Male ; Mammalia ; Metal levels ; Metallurgy ; Metals, Heavy - pharmacokinetics ; Muscle, Skeletal - physiology ; Sudbury ; Tissue Distribution</subject><ispartof>Environmental pollution (1987), 2001-01, Vol.113 (3), p.347-355</ispartof><rights>2000 Elsevier Science Ltd</rights><rights>2001 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c483t-59b1f3bbfbe856f6980255a99c5f9bd9fd3420e212b5df1114b8d7aab82d0a03</citedby><cites>FETCH-LOGICAL-c483t-59b1f3bbfbe856f6980255a99c5f9bd9fd3420e212b5df1114b8d7aab82d0a03</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://dx.doi.org/10.1016/S0269-7491(00)00183-4$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>314,780,784,3550,27924,27925,45995</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=1131323$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/11428143$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Parker, G.H</creatorcontrib><creatorcontrib>Hamr, J</creatorcontrib><title>Metal levels in body tissues, forage and fecal pellets of elk ( Cervus elaphus) living near the ore smelters at Sudbury, Ontario</title><title>Environmental pollution (1987)</title><addtitle>Environ Pollut</addtitle><description>Varying levels of metals from smelters were found in body tissues, forage and fecal pellets of elk.
Ontario’s only free-ranging elk herd located at Burwash–French River has been subjected to the influence of historic copper–nickel–iron (Cu–Ni–Fe) ore smelting operations within the Sudbury area. Metal levels in selected body tissues, preferred forage items and fecal pellets were determined, and their potential effects on health and reproductive viability assessed. Significant age effects were apparent in 13 out of 31 tissue metal values obtained, with most age-related differences attributable to elevated concentrations in fetal tissues. Cu and zinc (Zn) levels were four to six times higher in livers and one and a half to two times higher in the bones of fetuses as compared to post-natal animals. Enhanced pre-natal tissue burdens were also noted for cobalt (Co), Ni and lead (Pb) in muscles. However, mean cadmium (Cd) levels in kidney, liver and muscle tissues, as well as hepatic Fe concentrations, showed significant increases with age. Although Cd levels in the kidneys of older elk were still well below the reported threshold for irreversible organ damage, and not considered to be health-threatening, detailed histological study of the cortical tissues for subtle pathotoxicological effects may be warranted. Unlike renal and hepatic tissues, Cd concentrations in skeletal muscle were minimal and within levels considered acceptable for human consumption. Forage species collected in the elk range generally showed higher (two to eight times) Ni and Fe levels than the corresponding plants from a non-contaminated reference site. The highest Ni and Fe burdens were carried by eastern white cedar, a preferred winter food item for elk. No consistent site-related trends were demonstrated by Cu, Zn, Co, Pb, chromium (Cr) and Cd forage levels. Mean metal concentrations in fecal pellets generally exceeded the mean composite forage levels by a factor of 3, except for Ni, which was five times more concentrated in feces. Significantly elevated Ni and Fe levels in preferred browse species and fecal pellets of the Sudbury-area elk could be of concern and warrant further investigation.</description><subject>Age Factors</subject><subject>Age-dependent accumulation</subject><subject>Animal, plant and microbial ecology</subject><subject>Animals</subject><subject>Applied ecology</subject><subject>Biological and medical sciences</subject><subject>Canada, Ontario</subject><subject>Cervus elaphus</subject><subject>Deer - physiology</subject><subject>Diet</subject><subject>Ecotoxicology, biological effects of pollution</subject><subject>Effects of pollution and side effects of pesticides on vertebrates</subject><subject>Elk</subject><subject>Environmental Exposure</subject><subject>Feces - chemistry</subject><subject>Female</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Industry</subject><subject>Kidney - physiology</subject><subject>Liver - physiology</subject><subject>Male</subject><subject>Mammalia</subject><subject>Metal levels</subject><subject>Metallurgy</subject><subject>Metals, Heavy - pharmacokinetics</subject><subject>Muscle, Skeletal - physiology</subject><subject>Sudbury</subject><subject>Tissue Distribution</subject><issn>0269-7491</issn><issn>1873-6424</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2001</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqNkctrVDEUh4NY7Fj9E5SzEGmhV_O6j6xEBh-Fli7afUhuTtronXvHJHdgdv7pZjqDumtXhwPfefz4CHnD6AdGWfPxhvJGVa1U7JTSM0pZJyr5jCxY14qqkVw-J4u_yDF5mdIPSqkUQrwgx4xJ3jEpFuT3FWYzwIAbHBKEEezktpBDSjOmc_BTNHcIZnTgsS_gGocBc4LJAw4_4RSWGDdzKo1Z38_pDIawCeMdjGgi5HuEKSKkFQ4ZYwKT4WZ2do7bc7ges4lhekWOvBkSvj7UE3L79cvt8nt1ef3tYvn5suplJ3JVK8u8sNZb7OrGN6qjvK6NUn3tlXXKOyE5Rc64rZ1nJaDtXGuM7bijhooT8n6_dh2nXyVa1quQ-hLGjDjNSXPVsqZh9RNAoZqWP76RKcWV6lgB6z3YxymliF6vY1iZuNWM6p1L_eBS70RpSvWDSy3L3NvDgdmu0P2bOsgrwLsDYFJx46MZ-5D-4wQTfId92mPFMG4CRp36gGOPLkTss3ZTeOSTPxg0uwY</recordid><startdate>20010101</startdate><enddate>20010101</enddate><creator>Parker, G.H</creator><creator>Hamr, J</creator><general>Elsevier Ltd</general><general>Elsevier</general><scope>IQODW</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>7ST</scope><scope>7T4</scope><scope>7TV</scope><scope>7U6</scope><scope>7U7</scope><scope>C1K</scope><scope>7TB</scope><scope>8FD</scope><scope>FR3</scope><scope>8BQ</scope><scope>JG9</scope><scope>KR7</scope></search><sort><creationdate>20010101</creationdate><title>Metal levels in body tissues, forage and fecal pellets of elk ( Cervus elaphus) living near the ore smelters at Sudbury, Ontario</title><author>Parker, G.H ; Hamr, J</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c483t-59b1f3bbfbe856f6980255a99c5f9bd9fd3420e212b5df1114b8d7aab82d0a03</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2001</creationdate><topic>Age Factors</topic><topic>Age-dependent accumulation</topic><topic>Animal, plant and microbial ecology</topic><topic>Animals</topic><topic>Applied ecology</topic><topic>Biological and medical sciences</topic><topic>Canada, Ontario</topic><topic>Cervus elaphus</topic><topic>Deer - physiology</topic><topic>Diet</topic><topic>Ecotoxicology, biological effects of pollution</topic><topic>Effects of pollution and side effects of pesticides on vertebrates</topic><topic>Elk</topic><topic>Environmental Exposure</topic><topic>Feces - chemistry</topic><topic>Female</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>Industry</topic><topic>Kidney - physiology</topic><topic>Liver - physiology</topic><topic>Male</topic><topic>Mammalia</topic><topic>Metal levels</topic><topic>Metallurgy</topic><topic>Metals, Heavy - pharmacokinetics</topic><topic>Muscle, Skeletal - physiology</topic><topic>Sudbury</topic><topic>Tissue Distribution</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Parker, G.H</creatorcontrib><creatorcontrib>Hamr, J</creatorcontrib><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Environment Abstracts</collection><collection>Human Population & Natural Resource Management</collection><collection>Pollution Abstracts</collection><collection>Sustainability Science Abstracts</collection><collection>Toxicology Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Mechanical & Transportation Engineering Abstracts</collection><collection>Technology Research Database</collection><collection>Engineering Research Database</collection><collection>METADEX</collection><collection>Materials Research Database</collection><collection>Civil Engineering Abstracts</collection><jtitle>Environmental pollution (1987)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Parker, G.H</au><au>Hamr, J</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Metal levels in body tissues, forage and fecal pellets of elk ( Cervus elaphus) living near the ore smelters at Sudbury, Ontario</atitle><jtitle>Environmental pollution (1987)</jtitle><addtitle>Environ Pollut</addtitle><date>2001-01-01</date><risdate>2001</risdate><volume>113</volume><issue>3</issue><spage>347</spage><epage>355</epage><pages>347-355</pages><issn>0269-7491</issn><eissn>1873-6424</eissn><coden>ENVPAF</coden><abstract>Varying levels of metals from smelters were found in body tissues, forage and fecal pellets of elk.
Ontario’s only free-ranging elk herd located at Burwash–French River has been subjected to the influence of historic copper–nickel–iron (Cu–Ni–Fe) ore smelting operations within the Sudbury area. Metal levels in selected body tissues, preferred forage items and fecal pellets were determined, and their potential effects on health and reproductive viability assessed. Significant age effects were apparent in 13 out of 31 tissue metal values obtained, with most age-related differences attributable to elevated concentrations in fetal tissues. Cu and zinc (Zn) levels were four to six times higher in livers and one and a half to two times higher in the bones of fetuses as compared to post-natal animals. Enhanced pre-natal tissue burdens were also noted for cobalt (Co), Ni and lead (Pb) in muscles. However, mean cadmium (Cd) levels in kidney, liver and muscle tissues, as well as hepatic Fe concentrations, showed significant increases with age. Although Cd levels in the kidneys of older elk were still well below the reported threshold for irreversible organ damage, and not considered to be health-threatening, detailed histological study of the cortical tissues for subtle pathotoxicological effects may be warranted. Unlike renal and hepatic tissues, Cd concentrations in skeletal muscle were minimal and within levels considered acceptable for human consumption. Forage species collected in the elk range generally showed higher (two to eight times) Ni and Fe levels than the corresponding plants from a non-contaminated reference site. The highest Ni and Fe burdens were carried by eastern white cedar, a preferred winter food item for elk. No consistent site-related trends were demonstrated by Cu, Zn, Co, Pb, chromium (Cr) and Cd forage levels. Mean metal concentrations in fecal pellets generally exceeded the mean composite forage levels by a factor of 3, except for Ni, which was five times more concentrated in feces. Significantly elevated Ni and Fe levels in preferred browse species and fecal pellets of the Sudbury-area elk could be of concern and warrant further investigation.</abstract><cop>Oxford</cop><pub>Elsevier Ltd</pub><pmid>11428143</pmid><doi>10.1016/S0269-7491(00)00183-4</doi><tpages>9</tpages></addata></record> |
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subjects | Age Factors Age-dependent accumulation Animal, plant and microbial ecology Animals Applied ecology Biological and medical sciences Canada, Ontario Cervus elaphus Deer - physiology Diet Ecotoxicology, biological effects of pollution Effects of pollution and side effects of pesticides on vertebrates Elk Environmental Exposure Feces - chemistry Female Fundamental and applied biological sciences. Psychology Industry Kidney - physiology Liver - physiology Male Mammalia Metal levels Metallurgy Metals, Heavy - pharmacokinetics Muscle, Skeletal - physiology Sudbury Tissue Distribution |
title | Metal levels in body tissues, forage and fecal pellets of elk ( Cervus elaphus) living near the ore smelters at Sudbury, Ontario |
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