Mercury in abiotic matrices of clear lake, california: human health and ecotoxicological implications

• Published in: Ecological applications Vol. 18; no. 8 Suppl; pp. A128 - A157
• Main Authors: Suchanek, Thomas H, Collin A. Eagles-Smith, Darell G. Slotton, E. James Harner, David P. Adam
• Format: Journal Article
• Language: English
• Published: United States Ecological Society of America 01.12.2008
• Subjects: autumn; benthic organisms; California; Ecosystem; ecotoxicology; environmental health; Fresh Water - chemistry; Geologic Sediments - chemistry; groundwater; guidelines; human health; Humans; lakes; mercury; Mercury - chemistry; Mercury - toxicity; methylation; methylmercury compounds; Mining; physicochemical properties; remediation; Safe Drinking Water Act; seasonal variation; sediments; spring; sublethal effects; sulfates; sulfur; summer; surface water; Time Factors; United States Environmental Protection Agency; Water Pollutants, Chemical - chemistry; Water Pollutants, Chemical - toxicity; water pollution; water quality; winter; California; Great Lakes
• ISSN: 1051-0761; 1939-5582
• DOI: 10.1890/06-1477.1

Mercury (Hg) from Hg mining at Clear Lake, California, USA, has contaminated water and sediments for over 130 years and has the potential to affect human and environmental health. With total mercury (TotHg) concentrations up to 438 mg/kg (dry mass) in surficial sediments and up to 399 ng/L in lake water, Clear Lake is one of the most Hg‐contaminated lakes worldwide. Particulate Hg in surface water near the mine ranges from 10 000 to 64 000 ng/g; TotHg declines exponentially with distance from the Sulphur Bank Mercury Mine. From 1992 to 1998, no significant long‐term trends for TotHg or methylmercury (MeHg) in sediments or water were observed, but peaks of both TotHg and MeHg occurred following a 1995 flooding event. Sediments and water exhibit summer/fall maxima and winter/spring minima for MeHg, but not TotHg. Sediment TotHg has not declined significantly a decade after remediation in 1992. At the mine site, aqueous TotHg reached 374 000 ng/L in unfiltered groundwater. Pore water sulfate in sediments varies seasonally from 112 mg/L in summer/fall (when Hg methylation is highest) to 3300 mg/L in winter. While TotHg is exceptionally high in both sediments and water, MeHg is substantially lower than would be expected based on the bulk Hg loading to the lake and in comparison with other sites worldwide. Total mercury in Clear Lake water does not exceed the Safe Drinking Water Act criteria, but it sometimes greatly exceeds human health criteria established by the Great Lakes Initiative, U.S. Environmental Protection Agency water quality guidelines, and the California Toxics Rule criterion. Methylmercury concentrations exceed the Great Lakes Initiative criterion for MeHg in water at some sites only during summer/fall. Relative to ecological health, Clear Lake sediments greatly exceed the National Oceanic and Atmospheric Administration's benthic fauna Sediment Quality Guidelines for toxic effects, as well as the more concensus‐based Threshold Effects Concentration criteria. Based on these criteria, Hg‐contaminated sediments and water from Clear Lake are predicted to have some lethal and sublethal effects on specific resident aquatic species. However, based on unique physical and chemical characteristics of the Clear Lake environment, MeHg toxicity may be significantly less than anticipated from the large inorganic Hg loading.