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Experimental evidence for recovery of mercury-contaminated fish populations

Journal Article · · Nature (London)
 [1];  [2];  [3];  [4];  [5];  [2];  [2];  [6];  [7];  [8];  [9];  [10];  [11];  [12];  [5];  [2];  [13];  [14];  [15];  [3] more »;  [2];  [3];  [14];  [8];  [2];  [13] « less
  1. Freshwater Institute, Winnipeg, MB (Canada). Fisheries and Oceans Canada; Queen's Univ., Kingston, ON (Canada); IISD Experimental Lakes Area, Winnipeg, MB (Canada)
  2. Freshwater Institute, Winnipeg, MB (Canada). Fisheries and Oceans Canada
  3. Freshwater Institute, Winnipeg, MB (Canada). Fisheries and Oceans Canada; IISD Experimental Lakes Area, Winnipeg, MB (Canada)
  4. Univ. of Montreal, QC (Canada)
  5. Univ. of Wisconsin, Madison, WI (United States)
  6. Univ. of Western Ontario, London, ON (Canada)
  7. Smithsonian Environmental Research Center, Edgewater, MD (United States)
  8. Univ. of Alberta, Edmonton, AB (Canada)
  9. Univ. of Regina, SK (Canada)
  10. Reed Harris Environmental, Oakville, ON (Canada)
  11. Univ. of Maryland Center for Environmental Science, Solomons, MD (United States)
  12. Trent Univ., Peterborough, ON (Canada)
  13. US Geological Survey, Middleton, WI (United States)
  14. Oak Ridge National Lab. (ORNL), Oak Ridge, TN (United States)
  15. Univ. of Connecticut, Groton, CT (United States)

Anthropogenic releases of mercury (Hg) are a human health issue because the potent toxicant methylmercury (MeHg), formed primarily by microbial methylation of inorganic Hg in aquatic ecosystems, bioaccumulates to high concentrations in fish consumed by humans. Predicting the efficacy of Hg pollution controls on fish MeHg concentrations is complex because many factors influence the production and bioaccumulation of MeHg. Here we conducted a 15-year whole-ecosystem, single-factor experiment to determine the magnitude and timing of reductions in fish MeHg concentrations following reductions in Hg additions to a boreal lake and its watershed. During the seven-year addition phase, we applied enriched Hg isotopes to increase local Hg wet deposition rates fivefold. The Hg isotopes became increasingly incorporated into the food web as MeHg, predominantly from additions to the lake because most of those in the watershed remained there. Thereafter, isotopic additions were stopped, resulting in an approximately 100% reduction in Hg loading to the lake. The concentration of labelled MeHg quickly decreased by up to 91% in lower trophic level organisms, initiating rapid decreases of 38–76% of MeHg concentration in large-bodied fish populations in eight years. Although Hg loading from watersheds may not decline in step with lowering deposition rates, this experiment clearly demonstrates that any reduction in Hg loadings to lakes, whether from direct deposition or runoff, will have immediate benefits to fish consumers.

Research Organization:
Oak Ridge National Laboratory (ORNL), Oak Ridge, TN (United States)
Sponsoring Organization:
USDOE; Electric Power Research Institute; Environment and Climate Change Canada; Fisheries and Oceans Canada; Natural Sciences and Engineering Research Council of Canada; National Science Foundation (NSF); Southern Company; University of Alberta; USEPA; Wisconsin Focus on Enregy
Grant/Contract Number:
AC05-00OR22725
OSTI ID:
1843680
Journal Information:
Nature (London), Journal Name: Nature (London) Journal Issue: 7891 Vol. 601; ISSN 0028-0836
Publisher:
Nature Publishing GroupCopyright Statement
Country of Publication:
United States
Language:
English

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