4.8 Article

Quantification of Spatial and Temporal Trends in Atmospheric Mercury Deposition across Canada over the Past 30 Years

Journal

ENVIRONMENTAL SCIENCE & TECHNOLOGY
Volume 55, Issue 23, Pages 15766-15775

Publisher

AMER CHEMICAL SOC
DOI: 10.1021/acs.est.1c04034

Keywords

pan-Canadian; mercury; sediment proxy; archive; model; in situ measurements; anthropogenic pollution

Funding

  1. Environment and Climate Change Canada's under the Clean Air Regulatory Agenda (CARA)
  2. Climate Change and Air Pollutants (CCAP) programs

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The study found that anthropogenic atmospheric Hg deposition in western Canada is showing a synchronous decreasing trend, while increasing in the east, with spatial patterns mainly driven by longitude and proximity to point sources. Recent sediment-derived Hg fluxes were consistent with wet deposition monitoring results, validating the reliability of the research method.
Mercury (Hg) is a pollutant of concern across Canada and transboundary anthropogenic Hg sources presently account for over 95% of national anthropogenic Hg deposition. This study applies novel statistical analyses of 82 high-resolution dated lake sediment cores collected from 19 regions across Canada, including nearby point sources and in remote regions and spanning a full west-east geographical range of similar to 4900 km (south of 60 degrees N and between 132 and 64 degrees W) to quantify the recent (1990-2018) spatial and temporal trends in anthropogenic atmospheric Hg deposition. Temporal trend analysis shows significant synchronous decreasing trends in post-1990 anthropogenic Hg fluxes in western Canada in contrast to increasing trends in the east, with spatial patterns largely driven by longitude and proximity to known point source(s). Recent sediment-derived Hg fluxes agreed well with the available wet deposition monitoring. Sediment-derived atmospheric Hg deposition rates also compared well to the modeled values derived from the Hg model, when lake sites located nearby (<100 km) point sources were omitted due to difficulties in comparison between the sediment-derived and modeled values at deposition hot spots. This highlights the applicability of multi-core approaches to quantify spatio-temporal changes in Hg deposition over broad geographic ranges and assess the effectiveness of regional and global Hg emission reductions to address global Hg pollution concerns.

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