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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>Frank T. van Manen</dc:contributor>
  <dc:contributor>Joseph D. Clark</dc:contributor>
  <dc:creator>John R. Boetsch</dc:creator>
  <dc:date>2003</dc:date>
  <dc:description>&lt;p&gt;We investigated the applicability of biometric habitat modeling to rare plant inventory and conservation by developing and field testing a geographically explicit model for &lt;i&gt;Cardamine clematitis Shuttleworth&lt;/i&gt; ex A. Gray (mountain bittercress), an endemic plant of the southern Blue Ridge Mountains, USA. For each of 187 confirmed coordinates for &lt;i&gt;C. clematitis&lt;/i&gt; in Great Smoky Mountains National Park, 13 habitat variables were measured with a geographic information system. These data were used to calculate Mahalanobis distances for each 30-m x 30-m pixel within the study area; small values of Mahalanobis distance represented site conditions similar to those of known locations of &lt;i&gt;C. clematitis&lt;/i&gt;, whereas larger distance values represented dissimilar conditions. Following model development, we tested model performance by sampling 120 randomly distributed plots for&lt;i&gt; C. clematitis&lt;/i&gt; presence. Logistic regression showed that Mahalanobis distance values were strongly related to C. clematitis occurrence (P = 0.039). Overall, 75% of all known occurrences of &lt;i&gt;C. clematitis&lt;/i&gt; had associated Mahalanobis distance values below 17.7, and 95% of all occurrences were below 33.8; the median Mahalanobis distance value for the study area as a whole was 40.0. A habitat suitability cutoff value was defined which identified roughly 23,640 ha (19.5% of the study area) as suitable habitat. Although the model successfully predicted species absence in test plots with high Mahalanobis distance values, many sites with low values did not contain &lt;i&gt;C. clematitis&lt;/i&gt;. Only 16.2% of test plots below the habitat suitability cutoff contained &lt;i&gt;C. clematitis&lt;/i&gt;. The absence of &lt;i&gt;C. clematitis&lt;/i&gt; from sites with low Mahalanobis distance values (low specificity) is not necessarily indicative of a poor model; metapopulation processes (e.g., recolonizations, local extinctions) have been shown to play a major role in presence or absence of many plant species. That may be partially the case with our model as evidenced by a relationship between &lt;i&gt;C. clematitis&lt;/i&gt; presence and habitat patch size. &lt;br /&gt;&lt;br /&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:language>en</dc:language>
  <dc:publisher>Natural Areas Association</dc:publisher>
  <dc:title>Predicting rare plant occurrence in Great Smoky Mountains National Park, USA</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>