<?xml version='1.0' encoding='utf-8'?>
<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>V. H. Rivera-Monroy</dc:contributor>
  <dc:contributor>A. J. Nyman</dc:contributor>
  <dc:contributor>Megan K. La Peyre</dc:contributor>
  <dc:creator>E. R. Hillman</dc:creator>
  <dc:date>2020</dc:date>
  <dc:description>&lt;p&gt;&lt;span&gt;Submerged aquatic vegetation (SAV) thrives across the estuarine salinity gradient providing valuable ecosystem services. Within the saline portion of estuaries, seagrass areas are frequently cited as hotspots for their role in capturing and retaining organic carbon (C&lt;/span&gt;&lt;sub&gt;org&lt;/sub&gt;&lt;span&gt;). Non-seagrass SAV, located in the fresh to brackish estuarine areas, may also retain significant soil C&lt;/span&gt;&lt;sub&gt;org&lt;/sub&gt;&lt;span&gt;, yet their role remains unquantified. Given rapidly occurring landscape and salinity changes due to human and natural disturbances, landscape level carbon pool estimates from estuarine SAV habitat blue carbon estimates are needed. We assessed C&lt;/span&gt;&lt;sub&gt;org&lt;/sub&gt;&lt;span&gt;&amp;nbsp;stocks in SAV habitat soils from estuarine freshwater to saline habitats (interior deltaic) to saline barrier islands (Chandeleur Island) within the Mississippi River Delta Plain (MRDP), Louisiana, USA. SAV habitats contain C&lt;/span&gt;&lt;sub&gt;org&lt;/sub&gt;&lt;span&gt;&amp;nbsp;stocks equivalent to those reported for other estuarine vegetation types (seagrass, salt marsh, mangrove). Interior deltaic SAV C&lt;/span&gt;&lt;sub&gt;org&lt;/sub&gt;&lt;span&gt;&amp;nbsp;stocks (231.6&amp;nbsp;±&amp;nbsp;19.5&amp;nbsp;Mg C&lt;/span&gt;&lt;sub&gt;org&lt;/sub&gt;&lt;span&gt;&amp;nbsp;ha&lt;/span&gt;&lt;sup&gt;−1&lt;/sup&gt;&lt;span&gt;) were similar across the salinity gradient, and significantly higher than at barrier island sites (56.6&amp;nbsp;±&amp;nbsp;10.4&amp;nbsp;Mg C&lt;/span&gt;&lt;sub&gt;org&lt;/sub&gt;&lt;span&gt;&amp;nbsp;ha&lt;/span&gt;&lt;sup&gt;−1&lt;/sup&gt;&lt;span&gt;). Within the MRDP, shallow water SAV habitat covers up to an estimated 28,000&amp;nbsp;ha, indicating that soil C&lt;/span&gt;&lt;sub&gt;org&lt;/sub&gt;&lt;span&gt;&amp;nbsp;storage is potentially 6.4&amp;nbsp;±&amp;nbsp;0.1 Tg representing an unaccounted C&lt;/span&gt;&lt;sub&gt;org&lt;/sub&gt;&lt;span&gt;&amp;nbsp;pool. Extrapolated across Louisiana, and the Gulf of Mexico, this represents a major unaccounted pool of soil C&lt;/span&gt;&lt;sub&gt;org&lt;/sub&gt;&lt;span&gt;. As marshes continue to erode, the ability of coastal SAV habitat to offset some of the lost carbon sequestration may be valuable. Our estimates of C&lt;/span&gt;&lt;sub&gt;org&lt;/sub&gt;&lt;span&gt;&amp;nbsp;sequestration rates indicated that conversion of eroding marsh to potential SAV habitat may help to offset the reduction of C&lt;/span&gt;&lt;sub&gt;org&lt;/sub&gt;&lt;span&gt;&amp;nbsp;sequestration rates. Across Louisiana, we estimated SAV to offset this loss by as much as 79,000&amp;nbsp;Mg C yr&lt;/span&gt;&lt;sup&gt;−1&lt;/sup&gt;&lt;span&gt;&amp;nbsp;between the 1960s and 2000s.&lt;/span&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1016/j.scitotenv.2020.137217</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Elsevier</dc:publisher>
  <dc:title>Estuarine submerged aquatic vegetation habitat provides organic carbon storage across a shifting landscape</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>