
doi: 10.1038/ncomms4035
pmid: 24398909
Natural wetlands are well known for their significant methane emissions. However, trace element emissions via biomethylation and subsequent volatilization from pristine wetlands are virtually unstudied, even though wetlands constitute large reservoirs for trace elements. Here we show that the average volatile fluxes of selenium (<0.12 μg m(-2) day(-1)), sulphur (<37 μg m(-2) day(-1)) and arsenic (<0.54 μg m(-2) day(-1)) from a pristine peatland are considerable and consistent over two summers. We compare these fluxes with the total concentrations in the peat and show that selenium is up to 40 times more efficiently volatilized than arsenic, and over 100 times more efficiently volatilized than sulphur. We further show that the volatilization of selenium and arsenic increases with temperature, implying that emissions of these health-relevant trace elements will increase with global warming. We suggest that biomethylation and volatilization in wetlands play a crucial role in the mobilization and global biogeochemical cycling of trace elements.
biomethylation, atmospheric selenium, Global Warming, Methylation, soil, Arsenic, Selenium, selenium volatilization, sulfide, Temperature, bacterium, Trace Elements, products, speciation, sulfur, Wetlands, Volatilization, Sulfur, Switzerland, yellowstone-national-park
biomethylation, atmospheric selenium, Global Warming, Methylation, soil, Arsenic, Selenium, selenium volatilization, sulfide, Temperature, bacterium, Trace Elements, products, speciation, sulfur, Wetlands, Volatilization, Sulfur, Switzerland, yellowstone-national-park
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