1998
DOI: 10.1897/1551-5028(1998)017<0191:meibcl>2.3.co;2
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Mercury Exposure in Breeding Common Loons (Gavia Immer) in Central Ontario, Canada

Abstract: Abstract-Total Hg concentrations were determined in blood and feather samples of breeding common loons (Gavia immer) and their chicks from 24 lakes in Ontario with a range of water chemistry and fish Hg concentrations. In paired comparisons, males had significantly higher blood (p Ͻ 0.005) and feather (p Ͻ 0.05) Hg concentrations than their female mates. Sex differences in Hg concentrations were attributable to size differences between the two sexes and to the possible transfer of Hg to eggs by females during … Show more

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Cited by 61 publications
(68 citation statements)
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“…The higher Hg concentrations in blood and feathers of male loons compared to females is consistent with findings from elsewhere in North America Meyer et al, 1998;Scheuhammer et al, 1998b;Champoux et al, 2005). Geometric mean blood and feather Hg levels in females were 84% and 76% that of males, respectively.…”
Section: Discussionsupporting
confidence: 88%
“…The higher Hg concentrations in blood and feathers of male loons compared to females is consistent with findings from elsewhere in North America Meyer et al, 1998;Scheuhammer et al, 1998b;Champoux et al, 2005). Geometric mean blood and feather Hg levels in females were 84% and 76% that of males, respectively.…”
Section: Discussionsupporting
confidence: 88%
“…Particular emphasis has been placed on larger species for which trophic status is potentially greatest; such species include the common loon (Meyer et al, 1995Burgess et al, 1998a, b;Evers et al, , 2003Scheuhammer et al, 1998bScheuhammer et al, , 2001Fevold et al, 2003;Burgess and Hobson, in press;Champoux et al, in press), bald eagle (Grier, 1974;Wiemeyer et al, 1984;Frenzel and Anthony, 1989;Bowerman et al, 1994;Anthony et al, 1999;Bowerman et al, 2002), osprey (Cahill et al, 1998;DesGranges et al, 1998), wading birds (Gariboldi et al, 1998;Bouton et al, 1999;Spalding et al, 2000b;Henny et al, 2002), and seabirds (Braune, 1987;Burger and Gochfeld, 1995;Furness, 1995, 1997;Braune et al, 2001). Other foodweb pathways important for MeHg transfer are generally of lesser concern because trophic status of the endpoint species is generally lower than piscivores.…”
Section: Species Hg Exposure Patternsmentioning
confidence: 99%
“…Therefore, we selected a NEHC of 0.5 μg/g developed specifically to estimate mercury risk to bald eagles , which resulted in considerably lower estimates of risk to bald eagles at our sites; only nine sites had mercury concentrations >0.5 μg/g. However, there is evidence that piscivorous birds are being negatively affected by mercury in fish elsewhere (e.g., Scheuhammer and Blancher 1994;Scheuhammer et al 1998;Nocera and Taylor 1998). One might therefore argue that bald eagle populations would be increasing more rapidly if not for mercury, which would support the use of the lower TRVs.…”
Section: Dieldrin -Mink Dieldrin -Bald Eaglementioning
confidence: 99%
“…Bald eagles and mink consume large, adult fish such as those collected and analyzed in this study and are therefore reasonable receptors. The risk of contaminants to other piscivorous wildlife such as belted kingfisher (Ceryle alcyon), Caspian tern (Sterna caspia), or common loons (Gavia immer) may be overestimated if these species are used in the model, because they consume smaller fish that are presumed to have lower contaminant concentrations than larger fish because of their shorter lifespans, higher growth rates, and higher metabolism (Scheuhammer et al 1998;Rose et al 1999). It is also unlikely that the diet of adult bald eagles or mink would be entirely composed of fish from one site, which is tacitly assumed in this approach.…”
Section: Dieldrin -Mink Dieldrin -Bald Eaglementioning
confidence: 99%