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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>Jason J. Rohweder</dc:contributor>
  <dc:contributor>Molly Van Appledorn</dc:contributor>
  <dc:contributor>Shelby A. Weiss</dc:contributor>
  <dc:contributor>Matthew Trumper</dc:contributor>
  <dc:contributor>Lyle J. Guyon</dc:contributor>
  <dc:creator>Nathan R. De Jager</dc:creator>
  <dc:date>2026</dc:date>
  <dc:description>&lt;h3 class="c-article__sub-heading" data-test="abstract-sub-heading"&gt;Context&lt;/h3&gt;&lt;p&gt;Different rates of floodplain forest recruitment and mortality can reveal important changes in ecosystem processes that drive forest dynamics, resulting in net changes in forest cover, thereby influencing a wide range of river habitat and morphological characteristics.&lt;/p&gt;&lt;h3 class="c-article__sub-heading" data-test="abstract-sub-heading"&gt;Objectives&lt;/h3&gt;&lt;p&gt;We evaluated characteristics of forest change areas in the Upper Mississippi River System.&lt;/p&gt;&lt;h3 class="c-article__sub-heading" data-test="abstract-sub-heading"&gt;Methods&lt;/h3&gt;&lt;p&gt;An overlay technique was used to map patches of forest loss, gain, and persistence between 2010 and 2020 in relation to a series of explanatory variables.&lt;/p&gt;&lt;h3 class="c-article__sub-heading" data-test="abstract-sub-heading"&gt;Results&lt;/h3&gt;&lt;p&gt;We quantified a net decline in forest cover ranging from 3.2 to 16.8% in the uppermost five study reaches, and a net increase in forest cover ranging from 0.5 to 4.6% in the southernmost three reaches. Patches of forest loss and persistence were similarly tall (&amp;gt; 15&amp;nbsp;m), dense (&amp;gt; 90% cover), silver maple (&lt;i&gt;Acer saccharinum&lt;/i&gt;) dominated forests, whereas forest gain patches were short (&amp;lt; 15&amp;nbsp;m), less dense (&amp;lt; 66% cover) and more likely to be dominated by willow (&lt;i&gt;Salix)&lt;/i&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;species. Both forest loss and gain patches were smaller than forest persistence patches and were typically found in areas with low neighborhood forest density (&amp;lt; 50% forested 10&amp;nbsp;ha neighborhood). Areas that experienced more than three flood events per growing season, more than 100 consecutive days of inundation during a single flood event, and more than 60 mean total days of inundation per growing season from 2011 to 2020 showed a net loss of forest cover in all study reaches. In contrast, net increases in forest cover were restricted to areas that experienced less than a single flood event per growing season, less than 40 consecutive days of inundation during a single flood event and less than 30 mean total days of inundation per growing season from 2011 to 2020.&lt;/p&gt;&lt;h3 class="c-article__sub-heading" data-test="abstract-sub-heading"&gt;Conclusions&lt;/h3&gt;&lt;p&gt;Forest mortality along these river reaches is associated with forest fragmentation and an increasingly wetter hydrological regime.&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1007/s10980-025-02286-8</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Springer</dc:publisher>
  <dc:title>Patterns of floodplain forest mortality and recruitment along the Upper Mississippi and Illinois Rivers: Associations with forest fragmentation and flood inundation</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>