Effects of mercury on wildlife: A comprehensive review
Wildlife may be exposed to mercury (Hg) and methylmercury (MeHg) from a variety of environmental sources, including mine tailings, industrial effluent, agricultural drainwater, impoundments, and atmospheric deposition from electric power generation. Terrestrial and aquatic wildlife may be at risk fr...
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| Published in | Environmental toxicology and chemistry Vol. 17; no. 2; pp. 146 - 160 |
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| Main Authors | , , |
| Format | Journal Article Conference Proceeding |
| Language | English |
| Published |
Hoboken
Wiley Periodicals, Inc
01.02.1998
SETAC |
| Subjects | |
| Online Access | Get full text |
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| Abstract | Wildlife may be exposed to mercury (Hg) and methylmercury (MeHg) from a variety of environmental sources, including mine tailings, industrial effluent, agricultural drainwater, impoundments, and atmospheric deposition from electric power generation. Terrestrial and aquatic wildlife may be at risk from exposure to waterborne Hg and MeHg. The transformation of inorganic Hg by anaerobic sediment microorganisms in the water column produces MeHg, which bioaccumulates at successive trophic levels in the food chain. If high trophic level feeders, such as piscivorous birds and mammals, ingest sufficient MeHg in prey and drinking water, Hg toxicoses, including damage to nervous, excretory and reproductive systems, result. Currently accepted no observed adverse effect levels (NOAELs) for waterborne Hg in wildlife have been developed from the piscivorous model in which most dietary Hg is in the methyl form. Such model are not applicable to omnivores, insectivores, and other potentially affected groups, and have not incorpotated data from other important matrices, such as eggs and muscle. The purpose of this paper is to present a comprehensive review of the Hg literature as it relates to effects on wildlife, including previously understudied groups. We present a critique of the current state of knowledge about effects of Hg on wildlife as an aid to identifying missing information and to planning research needed for conducting a complete assessment of Hg risks to wildlife. This review summarizes the toxicity of Hg to birds and mammals, the mechanisms of Hg toxicity, the measurement of Hg in biota, and interpretation of residue data. |
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| AbstractList | Wildlife may be exposed to mercury (Hg) and methylmercury (MeHg) from a variety of environmental sources, including mine tailings, industrial effluent, agricultural drainwater, impoundments, and atmospheric deposition from electric power generation. Terrestrial and aquatic wildlife may be at risk from exposure to waterborne Hg and MeHg. The transformation of inorganic Hg by anaerobic sediment microorganisms in the water column produces MeHg, which bioaccumulates at successive trophic levels in the food chain. If high trophic level feeders, such as piscivorous birds and mammals, ingest sufficient MeHg in prey and drinking water, Hg toxicoses, including damage to nervous, excretory and reproductive systems, result. Currently accepted no observed adverse effect levels (NOAELs) for waterborne Hg in wildlife have been developed from the piscivorous model in which most dietary Hg is in the methyl form. Such model are not applicable to omnivores, insectivores, and other potentially affected groups, and have not incorpotated data from other important matrices, such as eggs and muscle. The purpose of this paper is to present a comprehensive review of the Hg literature as it relates to effects on wildlife, including previously understudied groups. We present a critique of the current state of knowledge about effects of Hg on wildlife as an aid to identifying missing information and to planning research needed for conducting a complete assessment of Hg risks to wildlife. This review summarizes the toxicity of Hg to birds and mammals, the mechanisms of Hg toxicity, the measurement of Hg in biota, and interpretation of residue data. Wildlife may be exposed to mercury (Hg) and methylmercury (MeHg) from a variety of environmental sources, including mine tailings, industrial effluent, agricultural drainwater, impoundments, and atmospheric deposition from electric power generation. Terrestrial and aquatic wildlife may be at risk from exposure to waterborne Hg and MeHg. The transformation of inorganic Hg by anaerobic sediment microorganisms in the water column produces MeHg, which bioaccumulates at successive trophic levels in the food chain. If high trophic level feeders, such as piscivorous birds and mammals, ingest sufficient MeHg in prey and drinking water, Hg toxicoses, including damage to nervous, excretory and reproductive systems, result. Currently accepted no observed adverse effect levels (NOAELs) for waterborne Hg in wildlife have been developed from the piscivorous model in which most dietary Hg is in the methyl form. Such model are not applicable to omnivores, insectivores, and other potentially affected groups, and have not incorporated data from other important matrices, such as eggs and muscle. The purpose of this paper is to present a comprehensive review of the Hg literature as it relates to effects on wildlife, including previously understudied groups. We present a critique of the current state of knowledge about effects of Hg on wildlife as an aid to identifying missing information and to planning research needed for conducting a complete assessment of Hg risks to wildlife. This review summarizes the toxicity of Hg to birds and mammals, the mechanisms of Hg toxicity, the measurement of Hg in biota, and interpretation of residue data. Abstract Wildlife may be exposed to mercury (Hg) and methylmercury (MeHg) from a variety of environmental sources, including mine tailings, industrial effluent, agricultural drainwater, impoundments, and atmospheric deposition from electric power generation. Terrestrial and aquatic wildlife may be at risk from exposure to waterborne Hg and MeHg. The transformation of inorganic Hg by anaerobic sediment microorganisms in the water column produces MeHg, which bioaccumulates at successive trophic levels in the food chain. If high trophic level feeders, such as piscivorous birds and mammals, ingest sufficient MeHg in prey and drinking water, Hg toxicoses, including damage to nervous, excretory and reproductive systems, result. Currently accepted no observed adverse effect levels (NOAELs) for waterborne Hg in wildlife have been developed from the piscivorous model in which most dietary Hg is in the methyl form. Such model are not applicable to omnivores, insectivores, and other potentially affected groups, and have not incorpotated data from other important matrices, such as eggs and muscle. The purpose of this paper is to present a comprehensive review of the Hg literature as it relates to effects on wildlife, including previously understudied groups. We present a critique of the current state of knowledge about effects of Hg on wildlife as an aid to identifying missing information and to planning research needed for conducting a complete assessment of Hg risks to wildlife. This review summarizes the toxicity of Hg to birds and mammals, the mechanisms of Hg toxicity, the measurement of Hg in biota, and interpretation of residue data. |
| Author | Schwarzbach, Steven Wolfe, Marti F. Sulaiman, Rini A. |
| Author_xml | – sequence: 1 givenname: Marti F. surname: Wolfe fullname: Wolfe, Marti F. email: mfwolfe@ucdavis.edu organization: Institute of Toxicology and Environmental Health, University of California-Davis, Davis, California 95616, USA – sequence: 2 givenname: Steven surname: Schwarzbach fullname: Schwarzbach, Steven organization: U.S. Fish and Wildlife Service, 3500 El Camino, Sacramento, California 95825 – sequence: 3 givenname: Rini A. surname: Sulaiman fullname: Sulaiman, Rini A. organization: Toxicology Task Force, Seattle, Washington 98125, USA |
| BackLink | http://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=2144929$$DView record in Pascal Francis |
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| CODEN | ETOCDK |
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| ContentType | Journal Article Conference Proceeding |
| Copyright | Copyright © 1998 SETAC 1998 INIST-CNRS |
| Copyright_xml | – notice: Copyright © 1998 SETAC – notice: 1998 INIST-CNRS |
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| Issue | 2 |
| Keywords | Fauna Toxicity Review Pollutant Vertebrata Mammalia Environment impact Pisces Methylmercury Water pollution Invertebrata Biological accumulation Aves Mollusca Mercury |
| Language | English |
| License | CC BY 4.0 |
| LinkModel | DirectLink |
| MeetingName | Mercury in Wildlife: Assessing Exposure and Effects. Symposium |
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| Notes | istex:7B461AA9228CE55C7EB82960E9947BD87CDE1353 Presented at the Wildlife Mercury Conference, Fairfax, Virginia, USA, April 12-13, 1996. ark:/67375/WNG-QQWSLD0H-C ArticleID:ETC5620170203 Presented at the Wildlife Mercury Conference, Fairfax, Virginia, USA, April 12–13, 1996. ObjectType-Article-2 SourceType-Scholarly Journals-1 ObjectType-Feature-1 content type line 23 ObjectType-Feature-3 ObjectType-Review-1 |
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| PublicationCentury | 1900 |
| PublicationDate | February 1998 |
| PublicationDateYYYYMMDD | 1998-02-01 |
| PublicationDate_xml | – month: 02 year: 1998 text: February 1998 |
| PublicationDecade | 1990 |
| PublicationPlace | Hoboken |
| PublicationPlace_xml | – name: Hoboken – name: Pensacola, FL |
| PublicationTitle | Environmental toxicology and chemistry |
| PublicationTitleAlternate | Environmental Toxicology and Chemistry |
| PublicationYear | 1998 |
| Publisher | Wiley Periodicals, Inc SETAC |
| Publisher_xml | – name: Wiley Periodicals, Inc – name: SETAC |
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Determination of methylmercury in fish by headspace-gas chromatography with microwave-induc 1990; 51 1987; 36 1990; 228 1967; 21 1993; 20 1983; 5 1975; 13 1994; 68 1972 1971 1975; 10 1989; 46 1974; 2 1979 1983; 14 1983; 12 1987; 46 1993; 36 1971; 96 1998; 17 1987; 42 1993; 38 1990 1995; 28 1977; 36 1992; 115 1987 1986 1970; 21 1985 1984 1983 1981 1992; 48 1992; 49 1979; 20 1971; 173 1988; 81 1985; 10 1979; 21 1992; 5 1988 1989; 60 1976; 40 1990; 521 1992; 262 1991; 77 1975; 39 1989; 9 1986; 15 1988; 10 1986; 17 1996 1995 1994 1996; 121 1991 1988; 208 1994; 317 1996; 12 1996; 11 1967; 8 1977; 14 1984; 8 1984; 33 1980; 55 1982; 43 1991; 71 1988; 24 1992; 24 1992; 23 1973; 1 1993; 68 1987; 75 1966; 354 1990; 12 1992; 281 1974; 11 1991; 58 1990; 14 1991; 56 1991; 55 1982; 107 1996; 30 1992; 13 1994; 27 1992; 14 1993; 5 1983; 55 1982; 25 1986; 40 1991; 46 1984; 15 1995; 69 1994; 35 1972; 141 1988; 40 1990; 530 1983; 68 1985; 57 1974; 38 1987; 13 1985; 7 1986; 59 1978; 16 1988; 52 1992; 76 1968; 40 1994; 119 1994; 41 1996; 53 1987; 16 1974; 27 1993; 15 1988; 1 1994; 124 1993; 12 1987; 23 1989; 12 1995; 80 1986; 64 1991; 21 1980; 11 1994; 58 1976; 16 1979; 43 1977; 8 1985; 36 e_1_2_7_108_2 e_1_2_7_3_2 Boitreau HL (e_1_2_7_125_2) 1988 e_1_2_7_127_2 e_1_2_7_104_2 e_1_2_7_19_2 e_1_2_7_123_2 Das SK (e_1_2_7_49_2) 1982; 25 e_1_2_7_83_2 e_1_2_7_100_2 e_1_2_7_15_2 e_1_2_7_60_2 Snelgrove‐Hobson SM (e_1_2_7_72_2) 1988; 52 e_1_2_7_41_2 e_1_2_7_87_2 e_1_2_7_11_2 e_1_2_7_64_2 e_1_2_7_45_2 e_1_2_7_68_2 e_1_2_7_142_2 e_1_2_7_146_2 e_1_2_7_116_2 e_1_2_7_90_2 e_1_2_7_112_2 e_1_2_7_71_2 e_1_2_7_94_2 e_1_2_7_52_2 e_1_2_7_75_2 e_1_2_7_23_2 e_1_2_7_33_2 e_1_2_7_56_2 e_1_2_7_79_2 e_1_2_7_37_2 e_1_2_7_131_2 Heinz G (e_1_2_7_2_2) 1996 e_1_2_7_135_2 Sundberg J (e_1_2_7_16_2) 1992; 5 e_1_2_7_139_2 e_1_2_7_4_2 e_1_2_7_105_2 e_1_2_7_128_2 Burger J (e_1_2_7_115_2) 1993; 5 e_1_2_7_8_2 e_1_2_7_101_2 e_1_2_7_124_2 e_1_2_7_82_2 e_1_2_7_120_2 e_1_2_7_40_2 e_1_2_7_63_2 e_1_2_7_86_2 e_1_2_7_44_2 e_1_2_7_67_2 e_1_2_7_48_2 e_1_2_7_143_2 e_1_2_7_29_2 e_1_2_7_147_2 e_1_2_7_109_2 e_1_2_7_117_2 Barr JF (e_1_2_7_76_2) 1986 Scott ML (e_1_2_7_81_2) 1977; 36 Littrell EE (e_1_2_7_88_2) 1991; 77 e_1_2_7_113_2 e_1_2_7_93_2 Wobeser G (e_1_2_7_53_2) 1976; 40 e_1_2_7_24_2 e_1_2_7_51_2 e_1_2_7_97_2 e_1_2_7_32_2 e_1_2_7_74_2 e_1_2_7_20_2 e_1_2_7_55_2 e_1_2_7_36_2 e_1_2_7_132_2 e_1_2_7_136_2 Lind B (e_1_2_7_59_2) 1988; 1 e_1_2_7_5_2 Khera KS (e_1_2_7_14_2) 1979 e_1_2_7_129_2 e_1_2_7_106_2 e_1_2_7_9_2 Newton I (e_1_2_7_96_2) 1988; 81 e_1_2_7_102_2 Fimreite N (e_1_2_7_78_2) 1971 e_1_2_7_121_2 e_1_2_7_62_2 e_1_2_7_43_2 e_1_2_7_66_2 e_1_2_7_47_2 e_1_2_7_89_2 e_1_2_7_140_2 Nixon T (e_1_2_7_17_2) 1994 e_1_2_7_28_2 Spalding MG (e_1_2_7_85_2) 1991 e_1_2_7_144_2 Rao PV (e_1_2_7_70_2) 1989; 9 e_1_2_7_148_2 U.S. Environmental Protection Agency (e_1_2_7_126_2) 1983 Inouye M (e_1_2_7_26_2) 1985; 7 e_1_2_7_114_2 e_1_2_7_110_2 e_1_2_7_50_2 e_1_2_7_92_2 e_1_2_7_25_2 Merigan WH (e_1_2_7_30_2) 1983; 5 e_1_2_7_54_2 e_1_2_7_73_2 e_1_2_7_21_2 e_1_2_7_35_2 e_1_2_7_77_2 e_1_2_7_39_2 e_1_2_7_133_2 e_1_2_7_137_2 e_1_2_7_107_2 Kerper LE (e_1_2_7_58_2) 1992; 262 Walsh PM (e_1_2_7_98_2) 1990 e_1_2_7_103_2 Tejning S (e_1_2_7_95_2) 1967; 8 e_1_2_7_6_2 e_1_2_7_18_2 e_1_2_7_122_2 e_1_2_7_61_2 e_1_2_7_80_2 Chang LW (e_1_2_7_12_2) 1984 e_1_2_7_42_2 e_1_2_7_65_2 e_1_2_7_84_2 e_1_2_7_10_2 e_1_2_7_46_2 e_1_2_7_69_2 e_1_2_7_141_2 e_1_2_7_27_2 e_1_2_7_145_2 e_1_2_7_119_2 Eccles CU (e_1_2_7_13_2) 1987 Rice DC (e_1_2_7_31_2) 1992; 13 Falter R (e_1_2_7_118_2) 1966; 354 e_1_2_7_111_2 Lindqvist O (e_1_2_7_130_2) 1991; 55 e_1_2_7_91_2 e_1_2_7_22_2 e_1_2_7_34_2 e_1_2_7_57_2 e_1_2_7_99_2 e_1_2_7_38_2 Wobeser G (e_1_2_7_7_2) 1976; 40 e_1_2_7_134_2 Chiba K (e_1_2_7_138_2) 1983; 55 |
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| Snippet | Wildlife may be exposed to mercury (Hg) and methylmercury (MeHg) from a variety of environmental sources, including mine tailings, industrial effluent,... Abstract Wildlife may be exposed to mercury (Hg) and methylmercury (MeHg) from a variety of environmental sources, including mine tailings, industrial... |
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| SubjectTerms | Analytical methods Animal, plant and microbial ecology Applied ecology Biological and medical sciences Ecotoxicology, biological effects of pollution Freshwater Fundamental and applied biological sciences. Psychology General aspects Methylmercury Review Wildlife |
| Title | Effects of mercury on wildlife: A comprehensive review |
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