Application of mercury isotopes for tracing trophic transfer and internal distribution of mercury in marine fish feeding experiments

Feeding experiments were performed to investigate mercury (Hg) isotope fractionation during trophic transfer and internal distribution of total Hg (THg) in marine fish on exposure to natural seafood. Young‐of‐the‐year amberjack ( Seriola dumerili ) were fed with either blackfin tuna ( Thunnus atlant...

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Bibliographic Details
Published in:Environmental Toxicology and Chemistry
Main Authors: Kwon, Sae Yun, Blum, Joel D, Chirby, Michelle A., Chesney, Edward J.
Format: Article in Journal/Newspaper
Language:unknown
Published: Wiley Periodicals, Inc. 2013
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Online Access:https://hdl.handle.net/2027.42/100149
https://doi.org/10.1002/etc.2313
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Summary:Feeding experiments were performed to investigate mercury (Hg) isotope fractionation during trophic transfer and internal distribution of total Hg (THg) in marine fish on exposure to natural seafood. Young‐of‐the‐year amberjack ( Seriola dumerili ) were fed with either blackfin tuna ( Thunnus atlanticus 2647 ng/g THg) or brown shrimp ( Farfantepenaeus aztecus 25.1 ng/g THg) for 80 d or 50 d, respectively, and dissected for muscle, liver, kidney, brain, and blood. After 30 d of tuna consumption, Hg isotopes (δ 202 Hg and Δ 199 Hg) of the amberjack organs shifted to the tuna value (δ 202 Hg = 0.55‰, Δ 199 Hg = 1.54‰,), demonstrating the absence of Hg isotope fractionation. When amberjack were fed a shrimp diet, there was an initial mixing of the amberjack organs toward the shrimp value (δ 202 Hg = −0.48‰, Δ 199 Hg = 0.32‰), followed by a cessation of further shifts in Δ 199 Hg and a small shift in δ 202 Hg. The failure of Δ 199 Hg to reach the shrimp value can be attributed to a reduction in Hg bioaccumulation from shrimp resulting from feeding inhibition and the δ 202 Hg shift can be attributed to a small internal fractionation during excretion. Given that the feeding rate and Hg concentration of the diet can influence internal Hg isotope distribution, these parameters must be considered in biosentinel fish studies. Environ Toxicol Chem 2013;32:2322–2330. © 2013 SETAC Peer Reviewed http://deepblue.lib.umich.edu/bitstream/2027.42/100149/1/etc2313.pdf