TY - JOUR
T1 - Trends in mercury wet deposition and mercury air concentrations across the U.S. and Canada
AU - Weiss-Penzias, Peter S.
AU - Gay, David A.
AU - Brigham, Mark E.
AU - Parsons, Matthew T.
AU - Gustin, Mae S.
AU - ter Schure, Arnout
N1 - Funding Information:
We thank the many state, provincial, federal, and non-governmental institutions that collaboratively fund and provide logistical support the MDN, NTN, AMNet, and other networks, which provided much of data for this study. This paper was made possible by funding support through EPRI. We thank the following for contributing data to this project: Eric Edgerton, Winston Luke, Mark Castro, Kevin Crist, Rob Tordon, Dirk Felton, Gary Conley, Ryan Callison, Kevin Perry, Bowen Call, Miriam Pendleton, Eric Miller, Alexandra Steffen, Martin Pilote, Dan Jaffe, Daniel Obrist, Sarah Rothenberg, Key-Young Choe, and Mike Abbott. We thank Greg Wetherbee and Greg Lorenz for their quality control analysis on Hg concentration data from the MDN. We thank Leonard Levin for helpful comments and for providing the EPRI Hg emissions data, and John Jansen, Janet Carter, Keith Lucey, and Mark Nilles for helpful comments on the manuscript. We also thank three anonymous reviewers for their constructive comments. This work was conducted as a part of the Western North American Mercury Synthesis Working Group supported by the John Wesley Powell Center for Analysis and Synthesis, funded by the U.S. Geological Survey. Any use of trade, firm, or product names is for descriptive purposes only and does not imply endorsement by the U.S. Government.
Publisher Copyright:
© 2016 Elsevier B.V.
PY - 2016/10/15
Y1 - 2016/10/15
N2 - This study examined the spatial and temporal trends of mercury (Hg) in wet deposition and air concentrations in the United States (U.S.) and Canada between 1997 and 2013. Data were obtained from the National Atmospheric Deposition Program (NADP) and Environment Canada monitoring networks, and other sources. Of the 19 sites with data records from 1997–2013, 53% had significant negative trends in Hg concentration in wet deposition, while no sites had significant positive trends, which is in general agreement with earlier studies that considered NADP data up until about 2010. However, for the time period 2007–2013 (71 sites), 17% and 13% of the sites had significant positive and negative trends, respectively, and for the time period 2008–2013 (81 sites) 30% and 6% of the sites had significant positive and negative trends, respectively. Non-significant positive tendencies were also widespread. Regional trend analyses revealed significant positive trends in Hg concentration in the Rocky Mountains, Plains, and Upper Midwest regions for the recent time periods in addition to significant positive trends in Hg deposition for the continent as a whole. Sulfate concentration trends in wet deposition were negative in all regions, suggesting a lower importance of local Hg sources. The trend in gaseous elemental Hg from short-term datasets merged as one continuous record was broadly consistent with trends in Hg concentration in wet deposition, with the early time period (1998–2007) producing a significantly negative trend (− 1.5 ± 0.2% year− 1) and the recent time period (2008–2013) displaying a flat slope (− 0.3 ± 0.1% year− 1, not significant). The observed shift to more positive or less negative trends in Hg wet deposition primarily seen in the Central-Western regions is consistent with the effects of rising Hg emissions from regions outside the U.S. and Canada and the influence of long-range transport in the free troposphere.
AB - This study examined the spatial and temporal trends of mercury (Hg) in wet deposition and air concentrations in the United States (U.S.) and Canada between 1997 and 2013. Data were obtained from the National Atmospheric Deposition Program (NADP) and Environment Canada monitoring networks, and other sources. Of the 19 sites with data records from 1997–2013, 53% had significant negative trends in Hg concentration in wet deposition, while no sites had significant positive trends, which is in general agreement with earlier studies that considered NADP data up until about 2010. However, for the time period 2007–2013 (71 sites), 17% and 13% of the sites had significant positive and negative trends, respectively, and for the time period 2008–2013 (81 sites) 30% and 6% of the sites had significant positive and negative trends, respectively. Non-significant positive tendencies were also widespread. Regional trend analyses revealed significant positive trends in Hg concentration in the Rocky Mountains, Plains, and Upper Midwest regions for the recent time periods in addition to significant positive trends in Hg deposition for the continent as a whole. Sulfate concentration trends in wet deposition were negative in all regions, suggesting a lower importance of local Hg sources. The trend in gaseous elemental Hg from short-term datasets merged as one continuous record was broadly consistent with trends in Hg concentration in wet deposition, with the early time period (1998–2007) producing a significantly negative trend (− 1.5 ± 0.2% year− 1) and the recent time period (2008–2013) displaying a flat slope (− 0.3 ± 0.1% year− 1, not significant). The observed shift to more positive or less negative trends in Hg wet deposition primarily seen in the Central-Western regions is consistent with the effects of rising Hg emissions from regions outside the U.S. and Canada and the influence of long-range transport in the free troposphere.
KW - Gaseous elemental mercury
KW - Mercury
KW - Mercury deposition network
KW - North America
KW - Precipitation
KW - Sulfate
KW - Trends
KW - Wet deposition
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U2 - 10.1016/j.scitotenv.2016.01.061
DO - 10.1016/j.scitotenv.2016.01.061
M3 - Article
C2 - 26803218
AN - SCOPUS:84955445022
SN - 0048-9697
VL - 568
SP - 546
EP - 556
JO - Science of the Total Environment
JF - Science of the Total Environment
ER -