<?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>L. Brown</dc:contributor>
  <dc:contributor>J. Harden</dc:contributor>
  <dc:contributor>J. Klein</dc:contributor>
  <dc:contributor>R. Middleton</dc:contributor>
  <dc:creator>M.J. Pavich</dc:creator>
  <dc:date>1986</dc:date>
  <dc:description>&lt;p&gt;&lt;span&gt;The distribution and residence time of cosmogenic&amp;nbsp;&lt;/span&gt;&lt;sup&gt;10&lt;/sup&gt;&lt;span&gt;Be in clay-rich soil horizons is fundamental to understanding and modelling the migration of&amp;nbsp;&lt;/span&gt;&lt;sup&gt;10&lt;/sup&gt;&lt;span&gt;Be on terrestrial sediments and in groundwater solutions. We have analyzed seven profiles of clay-rich soils developed from terrace sediments of the Merced River, California. The terraces and soils of increasing age are used to compare the&amp;nbsp;&lt;/span&gt;&lt;sup&gt;10&lt;/sup&gt;&lt;span&gt;Be inventory with a simple model of accumulation, decay and erosion. The data show that the distribution of&amp;nbsp;&lt;/span&gt;&lt;sup&gt;10&lt;/sup&gt;&lt;span&gt;Be varies with soil horizon clay content, that the residence time of&amp;nbsp;&lt;/span&gt;&lt;sup&gt;10&lt;/sup&gt;&lt;span&gt;Be in these horizons exceeds 10&lt;/span&gt;&lt;sup&gt;5&lt;/sup&gt;&lt;span&gt;&amp;nbsp;years, and that to a rough approximation the inventory of&amp;nbsp;&lt;/span&gt;&lt;sup&gt;10&lt;/sup&gt;&lt;span&gt;Be in a thoroughly sampled soil profile fits the equation:&amp;nbsp;&lt;/span&gt;&lt;i&gt;N&lt;/i&gt;&lt;span&gt;&amp;nbsp;= (&lt;/span&gt;&lt;i&gt;q&lt;/i&gt;&lt;span&gt;&amp;nbsp;−&amp;nbsp;&lt;/span&gt;&lt;i&gt;Em&lt;/i&gt;&lt;span&gt;)(1 −&amp;nbsp;&lt;/span&gt;&lt;i&gt;e&lt;/i&gt;&lt;sup&gt;−&lt;i&gt;λι&lt;/i&gt;&lt;/sup&gt;&lt;span&gt;)/&lt;/span&gt;&lt;i&gt;λ&lt;/i&gt;&lt;span&gt;&amp;nbsp;where&amp;nbsp;&lt;/span&gt;&lt;i&gt;q&lt;/i&gt;&lt;span&gt;&amp;nbsp;is delivery rate,&amp;nbsp;&lt;/span&gt;&lt;i&gt;E&lt;/i&gt;&lt;span&gt;&amp;nbsp;is erosion rate,&amp;nbsp;&lt;/span&gt;&lt;i&gt;m&lt;/i&gt;&lt;span&gt;&amp;nbsp;is the concentration of&amp;nbsp;&lt;/span&gt;&lt;sup&gt;10&lt;/sup&gt;&lt;span&gt;Be in the eroding surface layer, λ is the decay constant, and&amp;nbsp;&lt;/span&gt;&lt;i&gt;t&lt;/i&gt;&lt;span&gt;&amp;nbsp;is the age of the depositional unit from which the soil has developed. The general applicability of this model is uncertain and warrants further testing in well-calibrated terrace sequences.&lt;/span&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1016/0016-7037(86)90134-1</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Elsevier</dc:publisher>
  <dc:title>10Be distribution in soils from Merced River terraces, California</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>