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  <style face="normal" font="default" size="100%">We used an ordination approach to identify factors important to the organization of breeding bird communities in three floodplains: Cache River, Arkansas (AR), Iatt Creek, Louisiana (LA), and the Coosawhatchie River, South Carolina (SC), USA.We used 5-min point counts to sample birds in each study area each spring from 1995 to 1998, and measured ground-surface elevations and a suite of other habitat variables to investigate bird distributions and community characteristics in relation to important environmental gradients. In both AR and SC, the average number of Neotropical migrant species detected was lowest in semipermanently flooded Nyssa aquatica Linnaeus habitats and greatest in the highest elevation floodplain zone. Melanerpes carolinus Linnaeus, Protonotaria citrea Boddaert, Quiscalus quiscula Linnaeus, and other species were more abundant in N. aquatica habitats, whereas Wilsonia citrina Boddaert, Oporornis formosus Wilson, Vireo griseus Boddaert, and others were more abundant in drier floodplain zones. In LA, there were no significant differences in community metrics or bird species abundances among forest types. Canonical correspondence analyses revealed that structural development of understory vegetation was the most important factor affecting bird distributions in all three study areas; however, potential causes of these structural gradients differed. In AR and SC, differences in habitat structure were related to the hydrologic gradient, as indexed by ground-surface elevation. In LA, structural variations were related mainly to the frequency of canopy gaps. Thus, bird communities in all three areas appeared to be organized primarily in response to repeated localized disturbance. Our results suggest that regular disturbance due to flooding plays an important role in structuring breeding bird communities in floodplains subject to prolonged inundation, whereas other agents of disturbance (e.g., canopy gaps) may be more important in headwater systems subject to only shortduration flooding. Management for avian community integrity in these systems should strive to maintain forest zonation and natural disturbance regimes.</style> 
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  <style face="normal" font="default" size="100%">Advancing the fundamental sciences: proceedings of the Forest Service National Earth Sciences Conference, San Diego, CA, 18-22 October 2004</style> 
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  <title>
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  <style face="normal" font="default" size="100%" /> 
  </alt-title>
  <short-title>
  <style face="normal" font="default" size="100%" /> 
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  <style face="normal" font="default" size="100%" /> 
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  <style face="normal" font="default" size="100%">89-97</style> 
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  <style face="normal" font="default" size="100%">141</style> 
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  <style face="normal" font="default" size="100%" /> 
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  <style face="normal" font="default" size="100%">Pedodiversity</style> 
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  <style face="normal" font="default" size="100%">Soil richness</style> 
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  <keyword>
  <style face="normal" font="default" size="100%">Soil classification</style> 
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  <keyword>
  <style face="normal" font="default" size="100%">Soil geomorphology classification</style> 
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  <style face="normal" font="default" size="100%">Richness-area relationship</style> 
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  <year>
  <style face="normal" font="default" size="100%">2007</style> 
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  <style face="normal" font="default" size="100%">The study of pedodiversity and soil richness depends on the notion of soils as discrete entities. Soil classifications are often criticized in this regard because they depend in part on arbitrary or subjective criteria. In this study soils were categorized on the basis of the presence or absence of six lithological and morphological characteristics. Richness vs. area relationships, and the general pattern of soil variability and diversity, were then compared to analyses of pedodiversity based on Soil Taxonomy. The study area consists of sixteen 0.13-ha plots on forested sideslopes of the Ouachita Mountains, Arkansas, with a minimum of 20 classified soil pits per plot. An ad hoc classification was developed, from the standpoint of soil geomorphology and studies of the coevolution of soils and landscapes, and based on the regional environmental framework. Soils were classified based on (1) underlying geology (shale, sandstone bedrock, or transported sandstone rock fragments), and on the presence or absence of ( 2) texture contrast subsoils, (3) eluvial horizons, (4) surface and/or subsurface stone lines or zones, (5) lithological contrasts between soil and underlying geology, and (6) redoximorphic features. The soil geomorphic classification (SGC) yielded 40 different soil types (out of 288 possible different combinations of the criteria), compared to 19 different series or taxadjuncts identified by standard soil classification. However, 21 of the SGC soil types had only one or two representatives. Individual plots contained five to 11 different SGC soil types with extensive local variability. A standard power-function relationship between soil richness (S) and area or number of samples (A) provided the best fit for most plots (S=cAb). The exponent b was slightly higher than for the taxonomy-based analysis, but in general the analyses lead to similar conclusions with respect to the relationship between richness and area, and the relative importance of local, within-plot versus regional, between-plot variability. Res ults support the view that soils can be viewed and treated as discrete entities, that richness assessments are not necessarily extremely sensitive to the classification used, and that highly localized variability may be critical to pedodiversity. The suggested criteria for identifying discrete soil types are given, based on qualitative morphological differences and state factor relations, contiguity, and connectivity.</style> 
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  <style face="normal" font="default" size="100%">15th Central Hardwood Forest Conference</style> 
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  <year>
  <style face="normal" font="default" size="100%">2007</style> 
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  <style face="normal" font="default" size="100%">Asheville, NC</style> 
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  <style face="normal" font="default" size="100%">Recovery activities for species of conservation concern may be directed to acquire and protect habitats known to contain the species, or to produce suitable habitats or locations suspected to be capable of supporting populations of the species. Management of those habitats ultimately becomes necessary, especially where production of additional habitats is deemed necessary. The Cerulean Warbler Technical Group (CWTG) is working to maintain current Cerulean Warbler (Dendroica cerulea (Wilson), Aves: Parulidae) populations and ultimately to double them within the Partners in Flight North American Conservation Plan. This species’ population has declined as much as 70 percent since 1965, as measured by our only rangewide yardstick of breeding distribution and trends, the Breeding Bird Survey. These birds were listed as Vulnerable in the prestigious Threatened Birds of the World in 2004. Previously a candidate species under provisions of the U.S. Endangered Species Act (ESA), a petition to list them as Threatened u nder ESA was lodged in 2000. Ongoing CWTG research activities address three fronts in development of guidelines for habitat management: response of breeding populations to controlled manipulations of existing stands for vegetation management, distribution of the birds among Society of American Foresters’ Forest Cover Types, and suggestion of specific practices to improve habitat suitability of particular stands. These practices will vary geographically throughout the species’ range, but will focus on common structural elements (e.g., patchy emergent tree canopies) that occur in a variety of forest types. Work on breeding habitats indicates that silvicultural manipulation of the vegetation ultimately will become an important management tool for the species. The studies are, however, in their early stages, permitting us to suggest possible guidelines and illustrate possible objectives and potential consequences. We are not yet in position to specify outcomes of application of particular prescriptions with defin ed confidence limits.</style> 
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  <style face="normal" font="default" size="100%">Jones, K. C.</style> 
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  <style face="normal" font="default" size="100%">Roth, K.L.</style> 
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  <style face="normal" font="default" size="100%">Islam, K.</style> 
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  <style face="normal" font="default" size="100%">Hamel, Paul B.</style> 
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  <style face="normal" font="default" size="100%">Smith, C. G., III</style> 
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  <title>
  <style face="normal" font="default" size="100%">Incidence of nest material kleptoparasitism involving Cerulean Warblers</style> 
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  <style face="normal" font="default" size="100%" /> 
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  <style face="normal" font="default" size="100%" /> 
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  <style face="normal" font="default" size="100%" /> 
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  <style face="normal" font="default" size="100%">271-275</style> 
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  <style face="normal" font="default" size="100%">119</style> 
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  <number>
  <style face="normal" font="default" size="100%">2</style> 
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  <keywords /> 
  <dates>
  <year>
  <style face="normal" font="default" size="100%">2007</style> 
  </year>
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  <style face="normal" font="default" size="100%" /> 
  </pub-location>
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  <style face="normal" font="default" size="100%">Wilson Journal of Ornithology</style> 
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  <style face="normal" font="default" size="100%">We document 21 observations of interspecific stealing of nesting material involving Cerulean Warblers (Dendroica cerulea), Red-eyed Vireos (Vireo olivaceus), Blue-gray Gnatcatchers (Polioptila caerulea), Northern Parulas (Parula americana), Black-throated Green Warblers (D. virens), American Redstarts (Setophaga ruticilla), and Orchard Orioles (Icterus spurius) that occurred during studies of Cerulean Warbler breeding biology. These incidents involved a variety of combinations of nest owner and nest material thief suggesting that each of these species is both a perpetrator and recipient of this behavior in our study areas. Kleptoparasitic incidents occurred at all stages of the nesting cycle from nest-building through post-fledging. Two possible motivations for this behavior are related to saving time in finding nest materials and collecting this material for nest construction.</style> 
  </abstract>
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  <url>
  <style face="normal" font="default" size="100%" > http://www.treesearch.fs.fed.us/pubs/28921</style>
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  <style face="normal" font="default" size="100%">2007</style> 
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  <style face="normal" font="default" size="100%">Forest Watershed Science;Forest Values</style> 
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  <style face="normal" font="default" size="100%">3</style> 
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  <style face="normal" font="default" size="100%">For the incised, sand-bed streams of north-central Mississippi, USA, fish predation is one plausible mechanism to explain both relatively low crayfish densities and differences in stream size occupied by various native crayfishes. I conducted two mesocosm experiments to test effects of a fish predator (channel catfish, Ictalurus punctatus) on the survival and size structure of native crayfishes (primarily Pro