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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>Gopal Bhatt</dc:contributor>
  <dc:contributor>Lewis C. Linker</dc:contributor>
  <dc:contributor>Jesse Bash</dc:contributor>
  <dc:contributor>Paul Capel</dc:contributor>
  <dc:contributor>Gary W. Shenk</dc:contributor>
  <dc:creator>Douglas A. Burns</dc:creator>
  <dc:date>2021</dc:date>
  <dc:description>&lt;p&gt;&lt;span&gt;The Chesapeake Bay watershed has been the focus of pioneering studies of the role of atmospheric nitrogen (N) deposition as a nutrient source and driver of estuarine trophic status. Here, we review the history and evolution of scientific investigations of the role of atmospheric N deposition, examine trends from wet and&amp;nbsp;&lt;a title="Learn more about dry deposition from ScienceDirect's AI-generated Topic Pages" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/dry-deposition" data-mce-href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/dry-deposition"&gt;dry deposition&lt;/a&gt;&amp;nbsp;networks, and present century-long (1950–2050) atmospheric N deposition estimates. Early investigations demonstrated the importance of&amp;nbsp;&lt;a title="Learn more about atmospheric deposition from ScienceDirect's AI-generated Topic Pages" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/atmospheric-deposition" data-mce-href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/atmospheric-deposition"&gt;atmospheric deposition&lt;/a&gt;&amp;nbsp;as an N source to the Bay, providing 25%–40% among all major N sources. These early studies led to the unprecedented inclusion of targeted decreases in atmospheric N deposition as part of the multi-stakeholder effort to reduce N loads to the Bay. Emissions of nitrogen oxides (NO&lt;/span&gt;&lt;sub&gt;x&lt;/sub&gt;&lt;span&gt;) and deposition of wet nitrate, oxidized dry N, and dry ammonium (NH&lt;/span&gt;&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;+&lt;/sup&gt;&lt;span&gt;) sharply and synchronously declined by 60%–73% during 1995–2019. These decreases largely resulted from implementation of Title IV of the 1990 Clean Air Act Amendments, which began in 1995. Wet NH&lt;/span&gt;&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;+&lt;/sup&gt;&lt;span&gt;&amp;nbsp;deposition shows no significant trend during this period. The century-long atmospheric N deposition estimates indicate an increase in total atmospheric N deposition in the Chesapeake watershed from 1950 to a peak of ~15&amp;nbsp;kg&amp;nbsp;N/ha/yr in 1979, trailed by a slight decline of &amp;lt;10% through the mid-1990s, and followed by a sharp decline of about 40% thereafter through 2019. An additional 21% decline in atmospheric N deposition is projected from 2015 to 2050. A comparison of the Potomac River and James River watersheds indicates higher atmospheric N deposition in the Potomac, likely resulting from greater emissions from higher proportions of agricultural and urban land in this basin. Atmospheric N deposition rose from 30% among all N sources to the Chesapeake Bay watershed in 1950 to a peak of 40% in 1973, and a decline to 28% by 2015. These data highlight the important role of atmospheric N deposition in the Chesapeake Bay watershed and present a potential opportunity for decreases in deposition to contribute to further reducing N loads and improving the trophic status of tidal waters.&lt;/span&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1016/j.atmosenv.2021.118277</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Elsevier</dc:publisher>
  <dc:title>Atmospheric nitrogen deposition in the Chesapeake Bay watershed: A history of change</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>