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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>Julio Betancourt</dc:contributor>
  <dc:contributor>Mitchel P. McClaran</dc:contributor>
  <dc:contributor>Stuart E. Marsh</dc:contributor>
  <dc:creator>Aaryn D. Olsson</dc:creator>
  <dc:date>2012</dc:date>
  <dc:description>&lt;b&gt;Aim&lt;/b&gt;  Biological invasions facilitate ecosystem transformation by altering the structure and function, diversity, dominance and disturbance regimes. A classic case is the grass&amp;ndash;fire cycle in which grass invasion increases the frequency, scale and/or intensity of wildfires and promotes the continued invasion of invasive grasses. Despite wide acceptance of the grass&amp;ndash;fire cycle, questions linger about the relative roles that interspecific plant competition and fire play in ecosystem transformations.  &lt;b&gt;Location&lt;/b&gt;  Sonoran Desert Arizona Upland of the Santa Catalina Mountains, Arizona, USA.  &lt;b&gt;Methods&lt;/b&gt;  We measured species cover, density and saguaro (&lt;i&gt;Carnegiea gigantea&lt;/i&gt;) size structure along gradients of &lt;i&gt;Pennisetum ciliare&lt;/i&gt; invasion at 10 unburned/ungrazed &lt;i&gt;P. ciliare&lt;/i&gt; patches. Regression models quantified differences in diversity, cover and density with respect to &lt;i&gt;P. ciliare&lt;/i&gt; cover, and residence time and a Fisher's exact test detected demographic changes in saguaro populations. Because &lt;i&gt;P. ciliare&lt;/i&gt; may have initially invaded locations that were both more invasible and less diverse, we ran analyses with and without the plots in which initial infestations were located.  &lt;b&gt;Results&lt;/b&gt;  Richness and diversity decreased with &lt;i&gt;P. ciliare&lt;/i&gt; cover as did cover and density of most dominant species. Richness and diversity declined with increasing time since invasion, suggesting an ongoing transformation. The proportion of old-to-young &lt;i&gt;Carnegiea gigantea&lt;/i&gt; was significantly lower in plots with dominant &lt;i&gt;P. ciliare&lt;/i&gt; cover.  &lt;b&gt;Main conclusions&lt;/b&gt;  Rich desert scrub (15&amp;ndash;25 species per plot) was transformed into depauperate grassland (2&amp;ndash;5 species per plot) within 20 years following &lt;i&gt;P. ciliare&lt;/i&gt; invasion without changes to the fire regime. While the onset of a grass&amp;ndash;fire cycle may drive ecosystem change in the later stages and larger scales of grass invasions of arid lands, competition by &lt;i&gt;P. ciliare&lt;/i&gt; can drive small-scale transformations earlier in the invasion. Linking competition-induced transformation rates with spatially explicit models of spread may be necessary for predicting landscape-level impacts on ecosystem processes in advance of a grass&amp;ndash;fire cycle.</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1111/j.1472-4642.2011.00825.x</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Blackwell Publishing</dc:publisher>
  <dc:title>Sonoran Desert ecosystem transformation by a C&lt;sub&gt;4&lt;/sub&gt; grass without the grass/fire cycle</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>