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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>S.M. Krieger</dc:contributor>
  <dc:contributor>J. R. Walters</dc:contributor>
  <dc:contributor>J.A. Collazo</dc:contributor>
  <dc:creator>J. C. Allen</dc:creator>
  <dc:date>2006</dc:date>
  <dc:description>&lt;p&gt;&lt;span&gt;We determined the effects of fire history and a riparian-upland gradient on the breeding bird community at Fort Bragg Military Installation in North Carolina, one of the largest remnant areas of the endangered longleaf pine (&lt;/span&gt;&lt;i&gt;Pinus palustris&lt;/i&gt;&lt;span&gt;) ecosystem. Study sites were classified into two treatments: fire-intense (areas experiencing growing-season burns) and fire-suppressed (areas lacking fires). Within each treatment, bird and vegetation data were recorded at point-count stations positioned at three distances from streamhead pocosins to characterize the riparian-upland habitat gradient: 0, 75, and ≥150 m. Total bird abundance and species richness varied significantly along the riparian-upland gradient, with pocosins contributing greatly to avian biodiversity. Our data revealed strong effects of fire history and riparian-upland gradient on bird species, which we described in terms of breeding-bird assemblages. Members of the open longleaf assemblage (e.g., Red- cockaded Woodpecker [&lt;/span&gt;&lt;i&gt;Picoides borealis&lt;/i&gt;&lt;span&gt;], Bachman's Sparrow [&lt;/span&gt;&lt;i&gt;Aimophila aestivalis&lt;/i&gt;&lt;span&gt;]) were most common in fire-intense areas and at upland locations. Members of the fire-suppressed assemblage (e.g., Wood Thrush [&lt;/span&gt;&lt;i&gt;Hylocichla mustelina&lt;/i&gt;&lt;span&gt;], Ovenbird [&lt;/span&gt;&lt;i&gt;Seiurus aurocapilla&lt;/i&gt;&lt;span&gt;]) were confined to pocosins in fire-intense areas, but became more abundant in fire-suppressed areas. Members of the pocosin assemblage (e.g., Eastern Towhee [&lt;/span&gt;&lt;i&gt;Pipilo erythropthalamus&lt;/i&gt;&lt;span&gt;], Common Yellowthroat [&lt;/span&gt;&lt;i&gt;Geothlypis trichas&lt;/i&gt;&lt;span&gt;]) were largely confined to pocosins and, in some cases, were most abundant in fire-intense pocosins. Fire suppression increased structural diversity of vegetation and promoted one breeding-bird assemblage (fire-suppressed), but at the expense of two others (open longleaf, pocosin). Continued management of Fort Bragg to promote longleaf pine restoration is essential for supporting conservation of the open-longleaf bird assemblage; in addition, it will benefit the pocosin assemblage.&lt;/span&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1642/0004-8038(2006)123[1110:AOBBWF]2.0.CO;2</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>American Ornithological Society</dc:publisher>
  <dc:title>Associations of breeding birds with fire-influenced and riparian-upland gradients in a longleaf pine ecosystem</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>