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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 R. Thompson III</dc:contributor>
  <dc:contributor>Rolf R. Koford</dc:contributor>
  <dc:contributor>Frank A. La Sorte</dc:contributor>
  <dc:contributor>Hope D. Woodward</dc:contributor>
  <dc:contributor>Jane A. Fitzgerald</dc:contributor>
  <dc:creator>Robert B. Jacobson</dc:creator>
  <dc:date>2012</dc:date>
  <dc:description>&lt;p&gt;&lt;span&gt;Of 6 million ha of prairie that once covered northern and western Missouri, &amp;lt;36,500&amp;thinsp;ha remain, with planted, managed, and restored grasslands comprising most contemporary grasslands. Most grasslands are used as pasture or hayfields. Native grasses largely have been replaced by fescue (&lt;/span&gt;&lt;i&gt;Festuca&lt;/i&gt;&lt;span&gt;&amp;nbsp;spp.) on most private lands (almost 7 million ha). Previously cropped fields set aside under the Conservation Reserve Program (CRP) varied from a mix of cool-season grasses and forbs, or mix of native warm-season grasses and forbs, to simple tall-grass monocultures. We used generalized linear mixed models and distance sampling to assess abundance of 8 species of breeding grassland birds on 6 grassland types commonly associated with farm practices in Missouri and located in landscapes managed for grassland-bird conservation. We selected Bird Conservation Areas (BCAs) for their high percentage of grasslands and grassland-bird species, and for &amp;lt;5% forest cover. We used an information-theoretic approach to assess the relationship between bird abundance and 6 grassland types, 3 measures of vegetative structure, and 2 landscape variables (% grassland and edge density within a 1-km radius). We found support for all 3 levels of model parameters, although there was less support for landscape than vegetation structure effects likely because we studied high-percentage-grassland landscapes (BCAs). Henslow's sparrow (&lt;/span&gt;&lt;i&gt;Ammodramus henslowii&lt;/i&gt;&lt;span&gt;) counts increased with greater percentage of grassland, vegetation height-density, litter depth, and shrub cover and lower edge density. Henslow's sparrow counts were greatest in hayed native prairie. Dickcissel (&lt;/span&gt;&lt;i&gt;Spiza americana&lt;/i&gt;&lt;span&gt;) counts increased with greater vegetation height-density and were greatest in planted CRP grasslands. Grasshopper sparrow (&lt;/span&gt;&lt;i&gt;A. savannarum&lt;/i&gt;&lt;span&gt;) counts increased with lower vegetation height, litter depth, and shrub cover. Based on distance modeling, breeding densities of Henslow's sparrow, dickcissel, and grasshopper sparrow in the 6 grassland types ranged 0.9&amp;ndash;2.6, 1.4&amp;ndash;3.2, and 0.1&amp;ndash;1.5&amp;thinsp;birds/ha, respectively. We suggest different grassland types and structures (vegetation height, litter depth, shrub cover) are needed to support priority grassland-bird species in Missouri.&lt;/span&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1002/jwmg.264</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>The Wildlife Society</dc:publisher>
  <dc:title>Habitat and landscape effects on abundance of Missouri's grassland birds</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>