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<oai_dc:dc xmlns:dc="http://purl.org/dc/elements/1.1/" xmlns:oai_dc="http://www.openarchives.org/OAI/2.0/oai_dc/" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xsi:schemaLocation="http://www.openarchives.org/OAI/2.0/oai_dc/ http://www.openarchives.org/OAI/2.0/oai_dc.xsd">
  <dc:contributor>Collin A. Eagles-Smith</dc:contributor>
  <dc:contributor>Michael T. Tate</dc:contributor>
  <dc:contributor>David P. Krabbenhoft</dc:contributor>
  <dc:creator>Chris S. Eckley</dc:creator>
  <dc:date>2021</dc:date>
  <dc:description>&lt;p&gt;&lt;span&gt;Forest soils are among the world’s largest repositories for long-term accumulation of atmospherically deposited mercury (Hg), and understanding the potential for&amp;nbsp;remobilization&amp;nbsp;through gaseous emissions, aqueous dissolution and runoff, or erosive particulate transport to down-gradient aquatic ecosystems is critically important for projecting ecosystem recovery. Forestry operations, especially clear-cut logging where most of the vegetaiton is removed, can influence Hg mobility/fluxes, foodweb dynamics, and bioaccumulation processes. This paper measured surface-air Hg fluxes from catchments in the Pacific Northwest, USA, to determine if there is a difference between forested and logged catchments. These measurements were conducted as part of a larger project on the impact of forestry operations on Hg cycling which include measurements of&amp;nbsp;water fluxes&amp;nbsp;as well as impacts on biota. Surface-air Hg fluxes were measured using a commonly applied dynamic&amp;nbsp;flux chamber&amp;nbsp;(DFC) method that incorporated diel and seasonal variability in elemental Hg (Hg&lt;/span&gt;&lt;sup&gt;0&lt;/sup&gt;&lt;span&gt;) fluxes at multiple forested and harvested catchments. The results showed that the forested ecosystem had depositional Hg&lt;/span&gt;&lt;sup&gt;0&lt;/sup&gt;&lt;span&gt;&amp;nbsp;fluxes throughout most of the year (annual mean:&amp;nbsp;−0.26&amp;nbsp;ng/m&lt;/span&gt;&lt;sup&gt;2&lt;/sup&gt;&lt;span&gt;/h). In contrast, the harvested catchments showed mostly emission of Hg&lt;/span&gt;&lt;sup&gt;0&lt;/sup&gt;&lt;span&gt;&amp;nbsp;(annual mean: 0.63&amp;nbsp;ng/m&lt;/span&gt;&lt;sup&gt;2&lt;/sup&gt;&lt;span&gt;/h). Differences in solar radiation reaching the soil was the primary driver resulting in a shift from net deposition to emission in harvested catchments. The surface-air Hg fluxes were larger than the fluxes to water as runoff and accounted for 97% of the differences in Hg sequestered in forested versus harvested catchments.&lt;/span&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1016/j.envpol.2021.116869</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Elsevier</dc:publisher>
  <dc:title>Surface-air mercury fluxes and a watershed mass balance in forested and harvested catchments</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>