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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>M. S. Schulz</dc:contributor>
  <dc:contributor>D.V. Vivit</dc:contributor>
  <dc:contributor>T.D. Bullen</dc:contributor>
  <dc:contributor>J. Fitzpatrick</dc:contributor>
  <dc:creator>A. F. White</dc:creator>
  <dc:date>2012</dc:date>
  <dc:description>&lt;p id="sp005"&gt;Biotic/abiotic interactions between soil mineral nutrients and annual grassland vegetation are characterized for five soils in a marine terrace chronosequence near Santa Cruz, California. A Mediterranean climate, with wet winters and dry summers, controls the annual cycle of plant growth and litter decomposition, resulting in net above-ground productivities of 280–600&amp;nbsp;g&amp;nbsp;m&lt;sup&gt;−2&lt;/sup&gt;&amp;nbsp;yr&lt;sup&gt;−1&lt;/sup&gt;. The biotic/abiotic (A/B) interface separates seasonally reversible nutrient gradients, reflecting biological cycling in the shallower soils, from downward chemical weathering gradients in the deeper soils. The A/B interface is pedologically defined by argillic clay horizons centered at soil depths of about one meter which intensify with soil age. Below these horizons, elevated solute Na/Ca, Mg/Ca and Sr/Ca ratios reflect plagioclase and smectite weathering along pore water flow paths. Above the A/B interface, lower cation ratios denote temporal variability due to seasonal plant nutrient uptake and litter leaching. Potassium and Ca exhibit no seasonal variability beneath the A/B interface, indicating closed nutrient cycling within the root zone, whereas Mg variability below the A/B interface denotes downward leakage resulting from higher inputs of marine aerosols and lower plant nutrient requirements.&lt;/p&gt;&lt;p id="sp010"&gt;The fraction of a mineral nutrient annually cycled through the plants, compared to that lost from pore water discharge, is defined their respective fluxes&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;i&gt;F&lt;/i&gt;&lt;sub&gt;j,plants&lt;/sub&gt;&amp;nbsp;=&amp;nbsp;&lt;i&gt;q&lt;/i&gt;&lt;sub&gt;j,plants&lt;/sub&gt;/(&lt;i&gt;q&lt;/i&gt;&lt;sub&gt;j,plants&lt;/sub&gt;&amp;nbsp;+&amp;nbsp;&lt;i&gt;q&lt;/i&gt;&lt;sub&gt;j,discharge&lt;/sub&gt;) with average values for K and Ca (&lt;i&gt;F&lt;/i&gt;&lt;sub&gt;K,plants&lt;/sub&gt;&amp;nbsp;=&amp;nbsp;0.99;&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;i&gt;F&lt;/i&gt;&lt;sub&gt;Ca,plants&lt;/sub&gt;&amp;nbsp;=&amp;nbsp;0.93) much higher than for Mg and Na (&lt;i&gt;F&lt;/i&gt;&lt;sub&gt;Mg,plants&lt;/sub&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;0.64;&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;i&gt;F&lt;/i&gt;&lt;sub&gt;Na,plants&lt;/sub&gt;&amp;nbsp;=&amp;nbsp;0.28). The discrimination against Rb and Sr by plants is described by fractionation factors (&lt;i&gt;K&lt;/i&gt;&lt;sub&gt;Sr/Ca&lt;/sub&gt;&amp;nbsp;=&amp;nbsp;0.86;&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;i&gt;K&lt;/i&gt;&lt;sub&gt;Rb/K&lt;/sub&gt;&amp;nbsp;=&amp;nbsp;0.83) which are used in Rayleigh fractionation-mixing calculations to fit seasonal patterns in solute K and Ca cycling.&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;i&gt;K&lt;/i&gt;&lt;sub&gt;Rb/K&lt;/sub&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;and&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;span class="math"&gt;&lt;span id="MathJax-Element-1-Frame" class="MathJax_SVG" data-mathml="&lt;math xmlns=&amp;quot;http://www.w3.org/1998/Math/MathML&amp;quot;&gt;&lt;mrow is=&amp;quot;true&amp;quot;&gt;&lt;msub is=&amp;quot;true&amp;quot;&gt;&lt;mrow is=&amp;quot;true&amp;quot;&gt;&lt;mi is=&amp;quot;true&amp;quot;&gt;K&lt;/mi&gt;&lt;/mrow&gt;&lt;mrow is=&amp;quot;true&amp;quot;&gt;&lt;msup is=&amp;quot;true&amp;quot;&gt;&lt;mrow is=&amp;quot;true&amp;quot; /&gt;&lt;mrow is=&amp;quot;true&amp;quot;&gt;&lt;mn is=&amp;quot;true&amp;quot;&gt;24&lt;/mn&gt;&lt;/mrow&gt;&lt;/msup&gt;&lt;mtext is=&amp;quot;true&amp;quot;&gt;Mg&lt;/mtext&gt;&lt;mo is=&amp;quot;true&amp;quot;&gt;/&lt;/mo&gt;&lt;msup is=&amp;quot;true&amp;quot;&gt;&lt;mrow is=&amp;quot;true&amp;quot; /&gt;&lt;mrow is=&amp;quot;true&amp;quot;&gt;&lt;mn is=&amp;quot;true&amp;quot;&gt;22&lt;/mn&gt;&lt;/mrow&gt;&lt;/msup&gt;&lt;mtext is=&amp;quot;true&amp;quot;&gt;Mg&lt;/mtext&gt;&lt;/mrow&gt;&lt;/msub&gt;&lt;/mrow&gt;&lt;/math&gt;"&gt;&lt;span class="MJX_Assistive_MathML"&gt;K24Mg/22Mg&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;values (derived from isotope data in the literature) fall within fractionation envelopes bounded by inputs from rainfall and mineral weathering.&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;i&gt;K&lt;/i&gt;&lt;sub&gt;Sr/Ca&lt;/sub&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;and&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;span class="math"&gt;&lt;span id="MathJax-Element-2-Frame" class="MathJax_SVG" data-mathml="&lt;math xmlns=&amp;quot;http://www.w3.org/1998/Math/MathML&amp;quot;&gt;&lt;mrow is=&amp;quot;true&amp;quot;&gt;&lt;msub is=&amp;quot;true&amp;quot;&gt;&lt;mrow is=&amp;quot;true&amp;quot;&gt;&lt;mi is=&amp;quot;true&amp;quot;&gt;K&lt;/mi&gt;&lt;/mrow&gt;&lt;mrow is=&amp;quot;true&amp;quot;&gt;&lt;msup is=&amp;quot;true&amp;quot;&gt;&lt;mrow is=&amp;quot;true&amp;quot; /&gt;&lt;mrow is=&amp;quot;true&amp;quot;&gt;&lt;mn is=&amp;quot;true&amp;quot;&gt;44&lt;/mn&gt;&lt;/mrow&gt;&lt;/msup&gt;&lt;mtext is=&amp;quot;true&amp;quot;&gt;Ca&lt;/mtext&gt;&lt;mo is=&amp;quot;true&amp;quot;&gt;/&lt;/mo&gt;&lt;msup is=&amp;quot;true&amp;quot;&gt;&lt;mrow is=&amp;quot;true&amp;quot; /&gt;&lt;mrow is=&amp;quot;true&amp;quot;&gt;&lt;mn is=&amp;quot;true&amp;quot;&gt;40&lt;/mn&gt;&lt;/mrow&gt;&lt;/msup&gt;&lt;mtext is=&amp;quot;true&amp;quot;&gt;Ca&lt;/mtext&gt;&lt;/mrow&gt;&lt;/msub&gt;&lt;/mrow&gt;&lt;/math&gt;"&gt;&lt;span class="MJX_Assistive_MathML"&gt;K44Ca/40Ca&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;fractionation factors fall outside these envelopes indicating that Ca nutrient cycling is closed to these external inputs. Small net positive K and Ca fluxes (6–14&amp;nbsp;mol&amp;nbsp;m&lt;sup&gt;−2&lt;/sup&gt;&amp;nbsp;yr&lt;sup&gt;−1&lt;/sup&gt;), based on annual mass balances, indicate that the soils are accumulating mineral nutrients, probably as a result of long-term environmental disequilibrium.&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1016/j.gca.2011.10.029</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Elsevier</dc:publisher>
  <dc:title>The impact of biotic/abiotic interfaces in mineral nutrient cycling: A study of soils of the Santa Cruz chronosequence, California</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>