Abstract
Alkylated mercury species (monomethylmercury, MeHg, and dimethylmercury, DMeHg) exhibit significant bioaccumulation, and pose significant risks to ecosystems and human health. Although decades of research have been devoted to understanding MeHg formation and degradation, little is known about the DMeHg formation in aquatic systems. Here, we combine complementary experimental and computational approaches to examine MeHg speciation and DMeHg formation in sulfidic aqueous solutions, with an emphasis on the formation and decomposition of the binuclear bis(methylmercuric(ii)) sulfide complex (CH3Hg)2S. Experimental data indicate that the reaction 2CH3Hg+ + HS- (CH3Hg)2S + H+ has a logK = 26.0 ± 0.2. Thus, the binuclear (CH3Hg)2S complex is likely to be the dominant MeHg species under high MeHg concentrations typically used in experimental investigations of MeHg degradation by sulfate-reducing bacteria (SRB). Our finding of a significant abiotic removal mechanism for MeHg in sulfidic solutions through the formation of relatively insoluble (CH3Hg)2S suggests careful reexamination of reported "oxidative demethylation" of MeHg by SRB and perhaps other obligate anaerobes. We provide evidence for slow decomposition of (CH3Hg)2S to DMeHg and HgS, with a first-order rate constant k = 1.5 ± 0.4 × 10-6 h-1. Quantum chemical calculations suggest that the reaction proceeds by a novel mechanism involving rearrangement of the (CH3Hg)2S complex facilitated by strong Hg-Hg interactions that activate a methyl group for intramolecular transfer. Predictions of DMeHg formation rates under a variety of field and laboratory conditions indicate that this pathway for DMeHg formation will be significant in laboratory experiments utilizing high MeHg concentrations, favoring (CH3Hg)2S formation. In natural systems with relatively high MeHg/[H2S]T ratios (the oxic/anoxic interface, for example), DMeHg production may be observed, and warrants further investigation.
Original language | English |
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Pages (from-to) | 584-594 |
Number of pages | 11 |
Journal | Environmental Science: Processes and Impacts |
Volume | 20 |
Issue number | 4 |
DOIs | |
State | Published - Apr 2018 |
Funding
We thank So Jonsson and Scott Brooks for substantive comments on earlier versions of the manuscript, Ryne C. Johnston and Liyuan Liang for helpful discussions, and T. Andrew Mobley for insightful suggestions. This research was funded through the Grinnell College Mentored Advanced Project program. This work was also supported by the U.S. Department of Energy (DOE) Office of Science, Biological and Environmental Research, Subsurface Biogeochemical Research (SBR) Program through the Mercury Science Focus Area Program (SFA) at Oak Ridge National Laboratory (ORNL). ORNL is managed by UT-Battelle LLC for the U.S. DOE under contract number DE-AC05-00OR22725. This research also benetted from computational resources and expertise at the Environmental Molecular Sciences Laboratory (EMSL), a U. S. DOE Office of Science User Facility sponsored by the Office of Biological and Environmental Research (BER) and located at Pacic Northwest National Laboratory (PNNL), through Rapid Access award 50011 to JMP. PNNL is a multi-program national laboratory operated for the U.S. DOE by Battelle under contract DE-AC05-76RL01830.
Funders | Funder number |
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Office of Biological and Environmental Research | |
Office of Science, Biological and Environmental Research | SBR |
U. S. DOE Office of Science User Facility | |
U.S. DOE | DE-AC05-00OR22725 |
UT-Battelle LLC | |
U.S. Department of Energy | |
Battelle | DE-AC05-76RL01830 |
Biological and Environmental Research | 50011, PNNL |
Oak Ridge National Laboratory | ORNL |
Stephen F. Austin State University |