<?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>G. Street</dc:contributor>
  <dc:contributor>Francisco Vilella</dc:contributor>
  <dc:contributor>T. Jones-Farrand</dc:contributor>
  <dc:contributor>M. S. Wiggers</dc:contributor>
  <dc:contributor>K. O. Evans</dc:contributor>
  <dc:creator>C. Ramirez-Reyes</dc:creator>
  <dc:date>2021</dc:date>
  <dc:description>&lt;p&gt;&lt;span&gt;Locating additional occurrences of at-risk species can inform assessments of their status and conservation needs (including potential legal protections). The perennial bearded beaksedge (&lt;/span&gt;&lt;i&gt;Rhynchospora crinipes&lt;/i&gt;&lt;span&gt;) ranges from Mississippi to North Carolina, but known occurrences are limited. Because of the species' apparent rarity, a model to identify areas with suitable habitat conditions for the species will allow conservationists to effectively prioritize and allocate scarce surveying resources. We used known occurrence records, a suite of environmental datasets, and four species distribution modeling techniques (generalized additive, GAM; maximum entropy, MaxEnt; generalized boosted, GBM; and weighted ensemble) to generate maps to inform surveys for&amp;nbsp;&lt;/span&gt;&lt;i&gt;R. crinipes&lt;/i&gt;&lt;span&gt;. The ensemble approach improved predictive performance (AUC-PR = 0.95) compared to other techniques (individual model AUC-PR ranged from 0.7 to 0.8). We also obtained quantitative insights on the species' habitat relationships, including the likelihood of&amp;nbsp;&lt;/span&gt;&lt;i&gt;R. crinipes&lt;/i&gt;&lt;span&gt;'s presence near Atlantic white cedar (&lt;/span&gt;&lt;i&gt;Chamaecyparis thyoides&lt;/i&gt;&lt;span&gt;) habitat and floodplains, which is consistent with prior field observations. The ensemble model indicated that 3.6% of the study area could be suitable habitat, but only 0.38% had high suitability. Small stream riparian habitats and Atlantic swamp forests in Alabama, Florida, and Georgia had the highest proportion of suitable areas. Prioritizing surveys in areas with model-indicated high habitat suitability is expected to reveal additional&amp;nbsp;&lt;/span&gt;&lt;i&gt;R. crinipes&lt;/i&gt;&lt;span&gt;&amp;nbsp;occurrences. We suggest surveying efforts for other at-risk species may benefit from using an ensemble modeling approach to identify and prioritize survey areas and improve ecological knowledge of these species.&lt;/span&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.3375/043.041.0108</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>The Natural Areas Association</dc:publisher>
  <dc:title>Ensemble species distribution model identifies survey opportunities for at-risk bearded beaksedge (Rhynchospora crinipes) in the southeastern United States</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>