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loblolly pine stands of varying ages and under different management in South
Carolina, plots occupied by Bachman's sparrows consistently had low volumes of vegetation from 7 to 13 feet (2–4 m) above ground compared to unoccupied sites. In middle-aged and mature forests of Georgia composed primarily of loblolly pine, Bachman sparrow densities were negatively associated with tree/shrub volume and vegetation volume from 7 to <16 feet (3 to <5 m). In loblolly and shortleaf pine plantations of Arkansas, Bachman's sparrow breeding areas had significantly lower percent canopy cover (p<0.001), shorter woody vegetation (p≤0.01) and fewer trees (p<0.001) and shrubs (p≤0.05) than unoccupied sites. In south-central Missouri, Bachman's sparrows occurred in glades with less than 30% woody cover, and occupied glades had significantly (p≤0.05) lower percentages of deciduous and coniferous saplings, deciduous and coniferous trees, and total woody vegetation. Mid-story density was marginally (p=0.055) greater on unoccupied sites, and Bachman's sparrow abundance was significantly (p=0.043) negatively correlated (r= –0.446) with mid-story density in longleaf pine woodlands of northwestern Florida. However, relative abundance of Bachman's sparrows was not significantly (p=0.107) associated with canopy cover and there were no significant (p=0.133) differences in canopy cover between occupied and unoccupied sites.
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from 1.21 to 4.16 offspring per pair per year across sites and years. In a South
Carolina longleaf pine community, daily survival rate of Bachman's sparrow nests in 1995 was 0.952, which was significantly (p=0.04) higher than the 1996 daily nest survival rate of 0.889. Earlier nesting attempts (before June 15, n=15) had significantly (p=0.05) higher survival rates than those started later in the year (n=11). Daily nest survival rate was 0.922 during incubation and 0.973 during the nestling stage. In central Arkansas, daily success rate during the incubation period was 0.965, while in the nestling period it was 0.919. In the glades of south-central Missouri, 8 female Bachman's sparrows fledged an average of 1.5 young per season over 2 years. Predation accounted for 80% of egg loss on study sites in Arkansas and 94% of nest failures on sites in central Florida. Daily survival rates of nests in the Sandhills of North Carolina were 0.947 and 0.951. Nest survival in North Carolina and South Carolina declined significantly later in the breeding season.
599:, which resulted in a lower volume of vegetation from 3 to 7 feet (1–2 m) above ground. The authors suggest that the lack of vegetation in this height range may have limited perches, resulting in fewer birds on the site. An investigation of Bachman's sparrow habitat characteristics in 1- to 6-year-old loblolly pine stands of eastern Texas led to recommendations that 2 to 5 tall (>39 feet (12 m)) trees/100 ha remain on a clearcut for Bachman sparrow singing perches. In Georgia, the lack of vegetation from 10 to <16 feet (3 to <5 m) was suggested as a possible reason for the absence of Bachman's sparrows from open field vegetation. However, across the southeast, vegetation density from 3 to 6 feet (0.91–1.8 m) above ground varies widely on sites occupied by Bachman's sparrows, suggesting their requirements for the density of this vegetation layer are comparatively flexible.
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Mississippi and
Alabama have been thought to migrate south during winter. Historical records suggest that Bachman's sparrows that once bred from Illinois to Pennsylvania did migrate to the south. Records of Bachman's sparrow occurrence on breeding grounds and specimens of subspecies collected outside their normal breeding range suggest that spring migration occurs from mid-March to May and fall migration occurs from late August through to late October. However, migration of Bachman's sparrows in the northern part of their current range is not well understood and it may be that suitable habitat conditions do not necessitate migration. Because of their secretive nature, determining the presence of Bachman's sparrows is difficult outside of the breeding season, when individuals rarely sing and perch visibly. However, examination of
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across sites of different ages and management regimes. In
Georgia, Bachman sparrow densities ranged from 0 to 0.92 birds/ha on sites ranging from an open field to middle-aged and mature forests composed primarily of loblolly pine. In a south-central Florida community composed of saw palmetto, scrub palmetto, and threeawn, Bachman's sparrow density averaged 1 male/33 ha. In dry prairie of central Florida, Bachman's sparrow densities varied from 0.92 to 3.24 territories/10 ha across sites and years. Bachman's sparrow densities calculated from breeding bird censuses in longleaf pine forests was >15 territories/40 ha, while densities from winter bird population studies were from 6 to 10 individuals/40 ha.
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pine-grassland restoration stands in
Mississippi increased as size of areas with long burning rotations, short-harvest rotations, and no removal of hardwoods decreased (p=0.05) and as the perimeter to area ratio of these areas increased (p=0.02). In South Carolina, distance from source populations significantly (p≤ 0.05) influenced the ability of Bachman's sparrows to colonize recent clearcuts in both years on one study area and in 1 of 2 years in another study area. The authors suggest that the presence of corridors in the latter study area may have resulted in distance being less influential.
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unoccupied sites in
Arkansas, Alabama, Florida, South Carolina and North Carolina. In 17- to 28-year- old slash pine plantations of northwestern Florida that had been burned within 4 years, Bachman's sparrow abundance was significantly (p=0.043) correlated (r=0.46) with relative volume of grass. In longleaf and loblolly pine stands of varying ages and under different management in South Carolina, areas occupied by Bachman's sparrows consistently had high vegetation volumes ≤3 feet (1 m) above ground. Sites occupied by Bachman's sparrows in longleaf pine woodlands of Florida managed for the
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traditionally managed stands. In 1- to 6-year-old loblolly pine stands of eastern Texas, herbaceous ground cover (p=0.003) was greater in study areas occupied by
Bachman's sparrows. In south-central Missouri, glades occupied by Bachman's sparrows had significantly more grass (p=0.03) and forb cover (p=0.0005) than unoccupied glades. However, vegetation densities below 3 feet (0.9 m) and percent ground and grass cover in areas occupied by Bachman's sparrow did not differ significantly (p>0.05) from unoccupied areas of loblolly and shortleaf pine plantations in Arkansas.
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feet (1 m) above ground as recently burned pineland sites that were occupied by
Bachman's sparrow. Although measurements were not taken, observations of Bachman's sparrow in clearcuts in eastern Texas suggest they may favor tall grass in clumpy rather that uniform distribution. In loblolly and shortleaf pine plantations of Arkansas, explanations suggested for a lack of evidence of ground layer features influencing selection of breeding territories included importance of habitat characteristics that were not measured, such as patchiness of the
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587:>4 inches (10 cm) in diameter removed (0.4 territories/40 ha) in a loblolly pine forest of South Carolina. Haggerty suggests that litter may provide habitat for Bachman's sparrow prey, but that too much litter could interfere with foraging. In loblolly and shortleaf pine plantations of Arkansas, litter cover (78%) and depth (0.5 inches (1.2 cm) on sites occupied by Bachman's sparrows were significantly (p≤0.01) lower than litter cover (88.9%) and depth (1.6 inches (4.2 cm)) on unoccupied sites.
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sparrow density was 22.3 pairs/km . In an area in South
Carolina composed of longleaf and loblolly pine, Bachman's sparrow occurred at significantly (p=0.002) higher density in clearcuts than middle-aged (22–50 years) stands, while in another area clearcuts had relatively low densities of Bachman's sparrows. Vegetation differences between the 2 sites are likely to explain the difference. The site with relatively low densities of Bachman's sparrows had been rolled with a
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agricultural fields up into the early 1900s, Bachman's sparrows rapidly expanded their range and began breeding in
Illinois, Indiana, Ohio, West Virginia, Virginia, Maryland, and parts of Pennsylvania. However, this trend reversed during the 1930s as much of the eastern deciduous forest recovered. Bachman's sparrows are thought to have been extirpated from Virginia in the early 2000s, and North Carolina is now the northern periphery of their eastern range.
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from the 9.7-day average period between a failed nest and a subsequent nest attempt. On average, females attempted 3.1 nests per season. The maximum number of attempts per season was five. The maximum number of nests attempted in longleaf pine habitat of South Carolina was also five. After two successful nests, a female attempted three times to raise a third brood. Limited evidence suggests that three broods per season may occur occasionally.
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at the base of small trees, forbs, and other grass species. Bachman's sparrow nests are dome-shaped with an opening typically oriented to the north. However, there is some variation in nest shape and on the Arkansas study site above, only 7% of nests were not either partially or completely domed. Bachman's sparrow nest shape may vary geographically, as nests found farther north in their historic range were infrequently domed.
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624:(p<0.05) correlated (r=–0.22) with distance to edge. However, in dry prairie of central Florida the difference in Bachman's sparrow densities in edge and core habitat was not significant (p≥0.36), and both edge and core habitat were considered population sinks. In North Carolina, Bachman's sparrow occupancy increased at intermediate distances (~250 meters) from wildlife openings.
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grass that is too dense may impede movement. Further, though Bachman's sparrows select home ranges with a relatively low density of woody vegetation, individual birds seem to select microhabitat within their range with greater density of woody vegetation. This may be due to the importance of woody song perches for males and woody vegetation as escape cover.
1966:"The relative importance of multiscale factors in the distribution of Bachman's Sparrow and the implications for ecosystem conservationImportancia relativa de los factores a múltiples escalas en la distribución de Peucaea aestivalis y las implicancias para la conservación de los ecosistemasMultiscale factors influence Bachman's Sparrow distribution"
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from 20 April to 26 July was 80.0%. In another radio telemetry study, four mortalities out of 38 Bachman's sparrows were documented over two years. The overall breeding season survival rate was estimated as 0.893. According to a literature review, Bachman's sparrows have been captured that were at least three years old.
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In the dry prairie of central Florida, Bachman's sparrows used clumps of saw-palmetto that had "natural" burrows significantly (p<0.001) more than would be expected based on availability. The authors suggest that Bachman's sparrows in prairie habitat use burrows as areas of refuge from predators.
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Despite an emphasis on grass and herbaceous vegetation under 3 feet, recent studies have shown that Bachman's sparrows show a threshold level response to grass density and actually decline in regions where grass is too dense. Because Bachman's sparrows often walk across the ground instead of flying,
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Values of nest success reported for Bachman's sparrows vary. Daily nest survival rate of Bachman's sparrow ranged from 0.89 to 0.96 across sites and years in the dry prairie of central Florida. On average 3.13 birds were fledged per successful Bachman's sparrow nest. Estimates of productivity ranged
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Bachman's sparrows exhibit some fidelity to breeding sites. Over a two-year period in shortleaf and loblolly pine plantations of central Arkansas, 6 of 34 adults returned to areas where they had a territory in a previous year. This varied across years, with a 29% return rate of adult birds banded in
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Bachman's sparrow nests are constructed on the ground by females and are primarily made of grasses. All nests (n=71) found in a study in shortleaf and loblolly pine plantations of Arkansas were built on the ground. Most nests (70%) were built at the base of bluestem clumps, although nests were found
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Bachman's sparrows typically raise 2 broods per breeding season and will renest after failed attempts. In shortleaf and loblolly pine plantations of Arkansas, the average time between fledging of the 1st brood and starting the second brood was 12.3 days. This was not significantly (p=0.39) different
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Amount of litter and debris on a site may influence Bachman's sparrow habitat selection. Percent litter cover was consistently high (>58%) on sites occupied by Bachman's sparrow in Arkansas, Alabama, Florida, South Carolina and North Carolina. Although statistical significance was not tested due
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Bachman's sparrows' selection of a dense layer of herbaceous vegetation is widely documented. Vegetation density was greater below 3 feet (0.9 m) than above 3 feet (0.9 m) and percent ground cover and percent grass cover were consistently higher (>58%) on sites occupied by Bachman's sparrow than
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Time since fire is an important factor in Bachman's sparrow habitat use. In Florida, Bachman's sparrows abandoned sites that were greater than 5 years post fire. In North Carolina, occupancy of Bachman's sparrows decreased with years since fire. Several studies suggest that optimal sites are those
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Survival of Bachman's sparrows during the breeding season has been investigated in a South Carolina study area dominated by longleaf pine. Recapture of banded birds resulted in a monthly survival rate during the breeding season of 0.94. Using radio telemetry, average survival of Bachman's sparrows
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varies from three to five. Average clutch size on a site in Arkansas was 3.9, while in a longleaf pine community in South Carolina mean clutch size was 3.6. Both of these studies found significant (p≤0.02) decreases in clutch size as the breeding season progressed. On a dry prairie site in Florida
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Bachman's sparrows occur primarily in the southeastern United States from the central region of peninsular Florida north to southeastern North Carolina and west through portions of Tennessee, Kentucky and Missouri to eastern Oklahoma and eastern Texas. Following forest conversion and the spread of
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Bachman's sparrow density during the breeding season has been estimated in several habitats. On clearcuts of various ages with relatively abundant loblolly pine in eastern Texas, maximum Bachman sparrow density was 1.9/10 ha. In South Carolina, Bachman's sparrow densities ranged from 0 to 0.48/ha
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The ability of the Bachman's sparrow to detect and colonize areas before they are no longer suitable may depend on the size and isolation of the habitat. In south-central Missouri, only glades ≥ 29 acres (11.7 ha) were occupied by Bachman's sparrows. The probability of Bachman's sparrow occupying
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Bachman's sparrow inhabits areas with open overstories. In sites in eastern Texas of varying age since clearcutting, study areas occupied by Bachman's sparrows had significantly (p<0.01) fewer short (≤ 10 feet (3m)) and tall (>10 feet (3m)) trees than unoccupied study areas. In longleaf and
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of the ground layer may affect habitat suitability by influencing foraging success and the availability of food and nesting material. In Georgia, Bachman's sparrows did not occur in open areas with uniformly dense herbaceous vegetation, despite these sites having a similar volume of vegetation ≤3
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spp.) ≤ 2 feet (0.5 m) above ground, was also significantly (p=0.004) greater on occupied compared to unoccupied sites. Bachman's sparrows were significantly (p≤0.01) more abundant in mixed pine-grassland restoration stands in Mississippi, which had greater understory, grass, and forb cover, than
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Bachman's sparrows may be dependent on landscape level factors at a large scale. An occupancy study in North Carolina used repeated point counts (n=232 points) to examine the impact of patch fragmentation and size on occupancy. They found that occupancy was very strongly correlated to percent of
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Territory size of Bachman's sparrows varies. In Missouri glades, reports of average Bachman's sparrow breeding territory range from 1.5 acres (0.62 ha, n=13) to 7 acres (2.9 ha, n=7). In loblolly and shortleaf pine plantations of central Arkansas, mean home range size (n=25) during the breeding
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There is evidence that Bachman sparrow may select sites with some tall vegetation. In north-central Florida, densities of Bachman's sparrows in young (2–4 years) slash pine plantations with artificial snags added (n=3) was 31.4 pairs/km, while in similar vegetation without snags (n=3) Bachman's
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Engstrom, R. Todd. 1993. Characteristic mammals and birds of longleaf pine forests. In: Hermann, Sharon M., ed. The longleaf pine ecosystem: ecology, restoration and management: Proceedings, 18th Tall Timbers fire ecology conference; 1991 May 30 – June 2; Tallahassee, FL. Tallahassee, FL: Tall
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Bachman's sparrows' association with edge habitat is uncertain. In eastern Texas clearcuts with relatively abundant loblolly pine, sites with Bachman's sparrow territories were significantly (p<0.01) closer to the edge of the study area and the number of Bachman's sparrows was significantly
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In shortleaf and loblolly pine plantations in Arkansas, females incubated eggs for 13 to 14 days. The average nestling period was 9 days, and the average period between fledging and independence was 25 days. Both parents care for the young during these periods. A review suggests that Bachman's
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Reviews and a field guide summarize the limited information available on Bachman's sparrow migration. Bachman's sparrows in the southern portion of their range are resident, while those in Missouri, Arkansas, eastern Oklahoma, Tennessee, Virginia, parts of North Carolina, and extreme northern
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Stober, Jonathan M.; Krementz, David G. 2000. Survival and reproductive biology of the Bachman's Sparrow. In: Proceedings of the annual conference of the Southeastern Association of Fish and Wildlife Agencies; 2000 October 28 – November 1; Baton Rouge, LA. 54. Tallahassee, FL: Southeastern
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Bachman's sparrows forage on the ground for plant seeds and arthropods. In a predominately loblolly and shortleaf pine habitat of eastern Texas, all Bachman's sparrow foraging observations were on the ground and a literature review states that Bachman's sparrows rarely forage in shrubs.
717:). Insects comprise more of the Bachman's sparrow diet in spring and fall than in winter. Stomach contents of Bachman's sparrow collected in eastern Texas in summer (n=5) and fall (n=11) had a greater abundance of insects than those collected in winter (n=4).
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Bachman's sparrows' breeding season typically begins in April and continues through August. The earliest date for Bachman's sparrow eggs in Florida is 14 April and the latest date is 4 August. The earliest Bachman's sparrow nest found during a study in
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Information on Bachman's sparrow nest predators can be found in the Predators section of this summary. Cowbirds, nest abandonment, and prescribed fire are other known causes of nest failure. There are several accounts of Bachman's sparrow exhibiting
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Haggerty, Thomas M. (1998). "Vegetation Structure of Bachman's Sparrow Breeding Habitat and Its Relationship to Home Range (Estructura de la Vegetación del Habitat de Anidamiento de Aimophila aestivalis y su Relación con el Área Que Ocupa)".
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Wan Ramle, Wan A. Kadir. 1987. Vegetational characteristics of early successional sites utilized for breeding by the Bachman's Sparrow (Aimophila aestivalis) in eastern Texas. Nacogdoches, TX: Stephen F. Austin State University.
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Dunning, John B. 1993. Bachman's Sparrow. In: Poole, A.; Stettenheim, P.; Gill, F., eds. The Birds of North America. No. 38. Philadelphia, PA: The Academy of Natural Sciences; Washington, DC: The American Ornithologists' Union:
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and two individuals chased away an approaching cotton rat. There have also been some reports of Bachman's sparrows which feign injury or imitate the movement of a snake, even emitting a hissing noise, at the approach of danger.
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Several studies have investigated the importance of landscape attributes on Bachman's sparrows. For a discussion of the possible importance of patchiness of vegetation within a site see the habitat characteristics section.
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spp.), Bachman's sparrow territories (n=6) averaged 12.5 acres (5.1 ha). In winter (November–January), the average home range size of 8 Bachman's sparrows was 1.6 acres (0.65 ha) in the dry prairie of central Florida.
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Brooks, Robert Alexander. 1987. Avifaunal populations of regenerating clearcut areas in eastern Texas, with emphasis on the Bachman's Sparrow and Prairie Warbler. Nacogdoches, TX: Stephen F. Austin State University.
457:(n=9) average clutch size was 3.44 and on another (n=5) it was 3.6. In shortleaf and loblolly pine plantations of Arkansas, females laid an average of 11.6 eggs (n=20) over the course of the breeding season.
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Jones, Clark D.; Cox, James A.; Toriani-Moura, Emily; Cooper, Robert J. (June 2013). "Nest-Site Characteristics of Bachman's Sparrows and Their Relationship To Plant Succession Following Prescribed Burns".
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Fish, Alexander C.; Moorman, Christopher E.; DePerno, Christopher S.; Schillaci, Jessica M.; Hess, George R. (February 2018). "Predictors of Bachman's Sparrow Occupancy at its Northern Range Limit".
741:) prey on adult Bachman's sparrows. Species responsible for nest predation are not generally known. Evidence in some studies suggest mammalian predators and snakes eat Bachman's sparrow nestlings.
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Winiarski, Jason M.; Moorman, Christopher E.; Carpenter, John P. (September 2017). "Bachman's Sparrows at the northern periphery of their range: home range size and microhabitat selection".
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Gobris, Nancy M. 1992. Habitat occupancy during the breeding season by Bachman's Sparrow at Piedmont National Wildlife Refuge in central Georgia. Athens, GA: University of Georgia. Thesis
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Van Lear, David H.; Carroll, W. D.; Kapeluck, P. R.; Johnson, Rhett (2005-06-06). "History and restoration of the longleaf pine-grassland ecosystem: Implications for species at risk".
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Dunning, John B.; Borgella, Rene; Clements, Krista & Meffe, Gary K. (1995). "Patch Isolation, Corridor Effects, and Colonization by a Resident Sparrow in a Managed Pine Woodland".
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and species composition. In a predominantly longleaf pine forest in Georgia, Bachman's sparrows were significantly (p=0.04) more abundant in areas where ground cover was primarily
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Engstrom, R. Todd; Crawford, Robert L.; Baker, W. Wilson (1984). "Breeding Bird Populations in Relation to Changing Forest Structure following Fire Exclusion: A 15-Year Study".
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Reviews and an investigation of the Bachman sparrow's diet in eastern Texas summarize the species that comprise the Bachman's sparrow's diet. A variety of grass seeds such as
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Bachman's sparrows inhabit areas with a dense layer of ground vegetation and open mid-stories with scattered shrubs and saplings, including young clearcuts and open pine (
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colored breast and whitish belly. These are mid-sized New World sparrows, measuring 12.2–16.2 cm (4.8–6.4 in) and weighing 18.4–23 g (0.65–0.81 oz).
2069:"Effects of Hurricane Katrina and Salvage Logging on Bachman's SparrowEfectos del Huracán Katrina y de la Subsiguiente Extracción de Madera sobre Aimophila aestivalis"
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A 2019 study in Florida video-monitored 65 nests and recorded 37 individual depredation events by 12 total species. Most (51%) of nest predation was caused by snakes (
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habitat of South Carolina was 10 April, while the latest nest found was early in the incubation stage on 5 August. In a study of Bachman's sparrow reproduction in
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that have been burned within the previous 3 years, which highlights the importance of frequent fire regimes for the successful conservation of Bachman's sparrow.
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plantations of Arkansas, egg laying started as early as 17 April and continued until 26 August. However, 85% of clutches were started in May, June, or July.
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Chambers, Rachel J. 1994. Habitat relations of Bachman's sparrows and other birds on Missouri glades. Columbia, MO: University of Missouri-Columbia. Thesis
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Rutledge, Brandon T. & Conner, L. Mike (2002). "Potential effects of groundcover restoration on breeding bird communities in longleaf pine stands".
529:) had significantly (p=0.007) higher vegetation densities ≤ 2 feet (0.5 m) than unoccupied sites in the study area. Grass density, primarily bluestems (
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TUCKER, JAMES W.; ROBINSON, W. DOUGLAS; GRAND, JAMES B. (October 2004). "Influence of Fire on Bachman's Sparrow, an Endemic North American Songbird".
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Perkins, Dustin W.; Vickery, Peter D. & Shriver, W. Gregory (2003). "Spatial Dynamics of Source-Sink Habitats: Effects on Rare Grassland Birds".
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Winiarski, Jason M.; Fish, Alexander C.; Moorman, Christopher E.; Carpenter, John P.; DePerno, Christopher S.; Schillaci, Jessica M. (August 2017).
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season was 6 acres (2.5 ha). In on a south-central Florida site with saw palmetto and scrub palmetto (Sabal etonia) interspersed amongst threeawn (
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brown upperparts and crown with gray and black streaking on the nape, back and primaries. The face is gray with a rufous brown eyestripe. It has a
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Bachman's sparrow is primarily a non-migratory resident, but it may retreat from some of the most northerly territories. The species is mainly a
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Wood, Douglas R.; Burger, L. Wes Jr.; Bowman, Jacob L. & Hardy, Carol L. (2004). "Avian community response to pine—grassland restoration".
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habitat within 3 kilometers. This sensitivity to habitat in the surrounding landscape may be related to dispersal but is not yet understood.
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to small sample size, Bachman's sparrows occurred at higher densities in control plots (1.5 territories/40 ha) than plots that had downed
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Martin, Alexander C.; Zim, Herbert S.; Nelson, Arnold L. (1951). American wildlife and plants. New York: McGraw-Hill Book Company, Inc.
807:). In shortleaf and loblolly pine plantations of central Arkansas, 5% of 38 nest failures were due to brown-headed cowbird parasitism.
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Dean, Tylan F. & Vickery, Peter D. (2003). "Bachman's Sparrows use burrows and palmetto clumps as escape refugia from predators".
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National Geographic Society. 1999. Field guide to the birds of North America. 3d ed. Washington, DC: The National Geographic Society
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364:, with habitat loss one of the major factors often cited in its decline. Habitat degradation due to later stages of forest
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data from recent decades suggests that several populations of Bachman's sparrows remain in North Carolina for the winter.
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2687:(A. Poole, Ed.). Ithaca: Cornell Laboratory of Ornithology; Retrieved from The Birds of North American Online database
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Stevenson, Henry M.; Anderson, Bruce H. (1994). The birdlife of Florida. Gainesville, FL: University of Florida Press
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Dunning, John B. Jr. & Watts, Bryan D. (1990). "Regional differences in habitat occupancy by Bachman's Sparrow".
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Haggerty, Thomas M. (1995). "Nest-site selection, nest design, and nest-entrance orientation in Bachman's Sparrow".
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spp.), and threeawns are eaten by Bachman's sparrows as well as seeds of several other taxa, including blueberries (
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1983 and none of the adults banded in 1984 returning to the site in 1985. No juveniles (n=60) returned to the site.
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Sauer, J.R.; Niven, D.K.; Hines, J.E.; Ziolkowski, Jr., D.J.; Pardieck, K.L.; Fallon, J.E.; Link, W.A. (2019).
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Mumford, Russell E.; Keller, Charles E. 1984. The birds of Indiana. Bloomington, IN: Indiana University Press
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Malone, Kristen; Jones, Harrison; Betancourt, Adriana; Terhune II, Theron; Sieving, Kathryn (2019-07-31).
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data suggest that the species has declined since the survey began in 1966. The species' dependence on
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1650:"Scrub-Successional Bird Community Dynamics in Young and Mature Longleaf Pine-Wiregrass Savannahs"
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2604:. Laurel, Maryland: U.S. Geological Survey Patuxent Wildlife Research Center. Version 2.07.2019
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Pulliam, H. Ronald; Mills, G. Scott (November 1977). "The Use of Space by Wintering Sparrows".
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Plentovich, Sheldon; Tucker, James W. Jr.; Holler, Nicholas R. & Hill, Geoffrey E. (1998).
1740:"Vegetation structure of Bachman's Sparrow breeding habitat and its relationship to home range"
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1370:"Aspects of the breeding biology and productivity of Bachman's Sparrow in central Arkansas"
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spp). Arthropods in the Bachman's sparrow's diet include grasshoppers and crickets (order
369:
357:
54:
2671:
875:
2395:
2496:. Relative Risk Assessments for Decision –Making Related To Uncharacteristic Wildfire.
1203:
Brooks, Maurice (1938). "Bachman's Sparrow in the North-Central Portion of Its Range".
753:
435:
346:
234:
3199:
2973:
1631:
884:
537:
439:
431:
329:
59:
3030:
2478:
2368:
2184:
2102:
2048:
1999:
1926:
1577:
937:
NatureServe Network Biodiversity Location Data accessed through NatureServe Explorer
3084:
2903:
777:
714:
596:
318:
3120:
482:. One study recorded video evidence of a Bachman's sparrow successfully leading a
3057:
2890:
2505:
1239:
2986:
2947:
2836:
2690:
1781:"Enhancing Bachman's Sparrow Habitat via Management of Red-Cockaded Woodpeckers"
820:
757:
725:
Data demonstrating which species prey on Bachman's sparrow are lacking. However
710:
706:
487:
2827:
3025:
2352:
1598:"Video documentation of predators and nest defense at Bachman's Sparrow nests"
749:
702:
694:
666:
531:
2513:
2470:
2430:
2254:
2219:
2176:
2130:
2094:
2085:
2040:
1991:
1828:"Managing mid–rotation pine plantations to enhance Bachman's sparrow habitat"
1623:
1614:
1597:
1569:
1513:
1263:
1216:
1982:
1560:
1543:
683:
575:
146:
106:
2685:
Bachman’s Sparrow (Aimophila aestivalis). The Birds of North America Online
2602:"The North American Breeding Bird Survey, Results and Analysis 1966 - 2019"
1964:
Taillie, Paul J.; Peterson, M. Nils; Moorman, Christopher E. (2015-05-01).
792:(14%). Predators were not identified for 17 additional depredation events.
391:
breeds furthest east, from southeast South Carolina to peninsular Florida.
1826:
Tucker, James W. Jr.; Hill, Geoffrey E. & Holler, Nicholas R. (1998).
3182:
3051:
2821:
2462:
789:
785:
677:
564:
310:
126:
3094:
1415:
3143:
2929:
2862:
2723:
2572:
2546:"Feeding Ecology of Three Resident Sympatric Sparrows in Eastern Texas"
2422:
2360:
2305:
2262:
2211:
2138:
1918:
1846:
1807:
1758:
1713:
1673:
1463:
1388:
1271:
1224:
1113:
698:
671:
166:
1869:"A geographic study of the vegetation structure of Bachman's Sparrow (
3066:
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2032:
769:
765:
350:
325:
116:
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1799:
1665:
1649:
1455:
1255:
2916:
993:
2911:
689:
635:
418:
3107:
815:
The Bachman's sparrow is considered to be near threatened by the
2601:
1502:
Effects of Ground-based Military Training on Bachman's Sparrow (
816:
361:
336:
136:
2802:
2694:
1240:"Thirty-Two Years of Bird Migration at Raleigh, North Carolina"
375:
The song begins as a clear whistle, followed by a short trill.
869:
867:
569:), compared to relatively disturbed communities of bluestems (
486:
away from its nest. In the same study, three individuals used
2169:
10.2193/0022-541x(2004)068[1114:iofobs]2.0.co;2
1911:
10.2193/0091-7648(2004)032[0819:ACRTPR]2.0.CO;2
1285:
368:
has also been attributed to the decline of this species.
1508:(MSc thesis). Raleigh: North Carolina State University.
403:
occurs in the westernmost region of the species' range.
2067:
Brooks, Matthew E.; Stouffer, Philip C. (2010-11-01).
1648:
Krementz, David G. & Christie, Jeffrey S. (1999).
976:
Dunning, Jr., John B. (2006). Rodewald, P. G. (ed.).
2544:
Allaire, Pierre N. & Fisher, Charles D. (1975).
3041:
2811:
1325:
Association of Fish and Wildlife Agencies: 383–390.
899:10.2305/IUCN.UK.2020-3.RLTS.T22721256A179939235.en
831:for habitat complicates conservation management.
549:Factors such as the patchiness of vegetation and
461:sparrows probably breed the year after hatching.
387:Among the three subspecies of Bachman's sparrow,
1016:, John B. Dunning Jr. (ed.). CRC Press (1992),
3221:Native birds of the Southeastern United States
317:. This species was named in honor of Reverend
2706:
8:
1286:"eBird - Discover a new world of birding..."
2672:Bachman's (or Pinewoods) sparrow bird sound
2626:National Audubon Watch List species account
3226:Endemic birds of the Eastern United States
2799:
2713:
2699:
2691:
233:
70:
48:
29:
20:
2084:
1981:
1877:Journal of the Alabama Academy of Science
1613:
1559:
897:
2640:Integrated Taxonomic Information System
1363:
1361:
1359:
1357:
1355:
1353:
1351:
1169:
863:
857:United States Department of Agriculture
2586:
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1940:
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1058:
1056:
1054:
1052:
1050:
399:to Mississippi and north to Kentucky.
3206:IUCN Red List near threatened species
2539:
2537:
2535:
2533:
2444:
2442:
2440:
2319:
2317:
2315:
2150:
2148:
2062:
2060:
2058:
2013:
2011:
2009:
1959:
1957:
1955:
1953:
1951:
1591:
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1537:
1535:
1533:
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1034:
1032:
1030:
7:
1500:Fish, Alexander Christopher (2017).
1091:
1089:
1087:
1085:
922:
920:
918:
916:
2396:10.1046/j.1523-1739.1995.09030542.x
885:IUCN Red List of Threatened Species
939:. Arlington, Virginia: NatureServe
14:
2021:The Wilson Journal of Ornithology
1014:CRC Handbook of Avian Body Masses
978:"Bachman's Sparrow: Introduction"
844: This article incorporates
839:
819:and vulnerable to extinction by
93:
2666:Bachman's sparrow photo gallery
2656:on the Internet Bird Collection
2527:Timbers Research, Inc.: 127–138
874:BirdLife International (2020).
335:Their breeding habitat is open
3211:NatureServe vulnerable species
2157:Journal of Wildlife Management
1788:Journal of Wildlife Management
1654:Journal of Wildlife Management
1602:Avian Conservation and Ecology
1444:Journal of Wildlife Management
226:Peucaea aestivalis illinoensis
222:Peucaea aestivalis aestivalis
1:
2494:Forest Ecology and Management
389:Peucaea aestivalis aestivalis
349:, but it will also take some
2506:10.1016/j.foreco.2005.02.014
2341:Journal of Field Ornithology
2200:Journal of Field Ornithology
2119:Journal of Field Ornithology
1867:Haggerty, Thomas M. (2000).
1747:Journal of Field Ornithology
1738:Haggerty, Thomas M. (1998).
1368:Haggerty, Thomas M. (1988).
1098:"Breeding birds of Virginia"
927:NatureServe (7 April 2023).
823:as of 2023. North American
795:Bachman's sparrow nests are
764:), followed by mesomammals (
224:Peucaea aestivalis bachmani
1404:The Southwestern Naturalist
1102:Virginia Journal of Science
713:), and leafhoppers (family
407:Timing of major life events
3247:
986:Cornell Lab of Ornithology
982:The Birds of North America
687:spp.), pines, and sedges (
315:southeastern United States
2732:
2353:10.1648/0273-8570-74.1.26
2294:Wildlife Society Bulletin
1899:Wildlife Society Bulletin
1835:Wildlife Society Bulletin
892:: e.T22721256A179939235.
271:(Lichtenstein, MHC, 1823)
264:
257:
241:
232:
219:
214:
195:
188:
90:Scientific classification
88:
68:
46:
37:
28:
23:
2654:Bachman's sparrow videos
2086:10.1525/cond.2010.100019
1615:10.5751/ACE-01409-140206
1096:Watts, Bryan D. (2015).
797:occasionally parasitized
372:may assist in recovery.
356:This bird is considered
3231:Birds described in 1823
2683:Dunning, J. B. (2006).
2662:(for the United States)
2451:Southeastern Naturalist
1983:10.1650/CONDOR-14-137.1
1561:10.1650/condor-16-220.1
1238:Brimley, C. S. (1917).
705:), caterpillars (order
607:Landscape level effects
523:red-cockaded woodpecker
516:Habitat characteristics
370:Prescribed forest burns
279:Lichtenstein, MHC, 1823
846:public domain material
640:
24:Bachman's sparrow
801:brown-headed cowbirds
639:
632:Territory and density
573:spp.) and silkgrass (
480:nest defense behavior
297:), also known as the
3072:aimophila-aestivalis
3043:Aimophila aestivalis
2634:Aimophila aestivalis
2463:10.1656/058.017.0108
2384:Conservation Biology
1871:Aimophila aestivalis
959:"Peucaea aestivalis"
852:Aimophila aestivalis
825:Breeding Bird Survey
675:sp.), crowngrasses (
393:Peucaea a. bachmanii
276:Fringilla aestivalis
268:Aimophila aestivalis
2780:Peucaea sumichrasti
2411:The Wilson Bulletin
1873:) breeding habitat"
1377:The Wilson Bulletin
1205:The Wilson Bulletin
585:coarse woody debris
551:species composition
40:Conservation status
3031:Peucaea-aestivalis
2843:Peucaea aestivalis
2813:Peucaea aestivalis
2766:Peucaea mystacalis
2738:Peucaea aestivalis
2212:10.1111/jofo.12215
1506:) Breeding Ecology
1504:Peucaea aestivalis
1114:10.25778/31dc-jz42
984:. Ithaca, NY, US:
931:Peucaea aestivalis
878:Peucaea aestivalis
727:short-tailed hawks
701:), beetles (order
697:), spiders (order
669:, bristlegrasses (
641:
294:Peucaea aestivalis
199:Peucaea aestivalis
181:P. aestivalis
3193:
3192:
3013:Open Tree of Life
2805:Taxon identifiers
2796:
2795:
2773:Peucaea ruficauda
2759:Peucaea humeralis
829:seral communities
774:hispid cotton rat
772:; 19%), rodents (
735:American kestrels
527:Picoides borealis
504:Preferred habitat
401:P. a. illinoensis
299:pinewoods sparrow
289:Bachman's sparrow
286:
285:
280:
272:
207:Lichtenstein, MHC
83:
63:
3238:
3186:
3185:
3173:
3172:
3160:
3159:
3147:
3146:
3134:
3133:
3124:
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3111:
3110:
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3062:
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3034:
3033:
3021:
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3008:
3007:
2995:
2994:
2982:
2981:
2969:
2968:
2956:
2955:
2943:
2942:
2940:bachmans-sparrow
2933:
2932:
2920:
2919:
2907:
2906:
2894:
2893:
2884:
2883:
2871:
2870:
2868:DAD22BB68CF2206A
2858:
2857:
2847:
2846:
2845:
2832:
2831:
2830:
2800:
2787:Peucaea carpalis
2752:Peucaea cassinii
2745:Peucaea botterii
2721:Sparrows in the
2715:
2708:
2701:
2692:
2650:
2648:
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2267:
2266:
2241:(6): 1393–1399.
2230:
2224:
2223:
2195:
2189:
2188:
2163:(4): 1114–1123.
2152:
2143:
2142:
2113:
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2106:
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2064:
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2052:
2033:10.1676/12-119.1
2015:
2004:
2003:
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843:
842:
739:Falco sparverius
733:) and possibly
731:Buteo brachyurus
709:), wasps (order
560:Beyrich threeawn
556:herbaceous layer
397:P. a. aestivalis
307:American sparrow
303:oakwoods sparrow
278:
270:
252: Year-round
251:
245:
237:
201:
98:
97:
77:
74:
73:
57:
52:
51:
33:
21:
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3241:
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3237:
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3196:
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3181:
3178:Observation.org
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2678:Further reading
2644:
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2565:10.2307/4084555
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2247:10.2307/1935091
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1800:10.2307/3802298
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1666:10.2307/3802793
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1456:10.2307/3802716
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1256:10.2307/4072214
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1095:
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926:
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914:
904:
902:
873:
872:
865:
849:
840:
837:
813:
782:eastern woodrat
723:
659:
634:
609:
518:
512:spp.) forests.
506:
497:
471:
469:Nesting success
427:
414:
409:
395:occurs west of
381:
358:near threatened
253:
249:
247:
243:
225:
223:
210:
203:
197:
184:
92:
84:
75:
71:
64:
55:Near Threatened
53:
49:
42:
17:
16:Species of bird
12:
11:
5:
3244:
3242:
3234:
3233:
3228:
3223:
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2783:
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2688:
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2669:
2663:
2657:
2651:
2628:
2621:
2620:External links
2618:
2616:
2615:
2592:
2578:
2559:(2): 260–269.
2529:
2519:
2500:(1): 150–165.
2484:
2457:(1): 104–116.
2436:
2417:(3): 437–450.
2401:
2374:
2326:
2311:
2300:(2): 354–360.
2284:
2268:
2225:
2206:(3): 250–261.
2190:
2144:
2108:
2079:(4): 744–753.
2054:
2027:(2): 293–300.
2005:
1976:(2): 137–146.
1947:
1932:
1905:(3): 819–829.
1886:
1852:
1841:(2): 342–348.
1813:
1794:(1): 347–354.
1764:
1719:
1708:(3): 463–472.
1679:
1660:(3): 803–814.
1637:
1583:
1554:(3): 361–374.
1519:
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1469:
1450:(3): 588–599.
1421:
1394:
1383:(2): 247–255.
1327:
1300:
1277:
1250:(3): 296–308.
1230:
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1145:
1119:
1108:(3): 223–276.
1081:
1065:
1026:
1022:978-0849342585
1006:
994:10.2173/bna.38
968:
950:
912:
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836:
833:
812:
809:
805:Molothrus ater
754:gray rat snake
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246: Breeding
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186:
185:
178:
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172:
171:
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159:
154:
150:
149:
144:
140:
139:
134:
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129:
124:
120:
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114:
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2100:
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2061:
2059:
2055:
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2014:
2012:
2010:
2006:
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1979:
1975:
1971:
1967:
1960:
1958:
1956:
1954:
1952:
1948:
1941:
1939:
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1933:
1928:
1924:
1920:
1916:
1912:
1908:
1904:
1900:
1893:
1891:
1887:
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1882:
1878:
1874:
1872:
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1859:
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538:Schizachyrium
534:
533:
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511:
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488:ptiloerection
485:
481:
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466:
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455:
451:
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440:loblolly pine
437:
433:
432:longleaf pine
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312:
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305:, is a small
304:
300:
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295:
290:
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266:
265:
263:
260:
256:
240:
236:
231:
228:
227:
218:
213:
208:
202:
200:
194:
191:
190:Binomial name
187:
183:
182:
177:
174:
173:
170:
169:
165:
162:
161:
158:
157:Passerellidae
155:
152:
151:
148:
147:Passeriformes
145:
142:
141:
138:
135:
132:
131:
128:
125:
122:
121:
118:
115:
112:
111:
108:
105:
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2633:
2606:. Retrieved
2595:
2556:
2552:
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2497:
2493:
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2344:
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2072:
2024:
2020:
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1969:
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1880:
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1870:
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1407:
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1288:
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1009:
997:. Retrieved
981:
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941:. Retrieved
936:
930:
903:. Retrieved
889:
883:
877:
851:
838:
814:
811:Conservation
804:
794:
784:; 16%), and
778:cotton mouse
743:
738:
730:
724:
715:Cicadellidae
688:
682:
676:
670:
667:panicgrasses
664:
660:
651:
645:
642:
626:
622:
618:
614:
610:
601:
597:drum chopper
593:
589:
581:
574:
570:
563:
548:
544:
536:
530:
526:
519:
509:
507:
498:
476:
472:
463:
459:
452:
448:
444:
428:
415:
400:
396:
392:
388:
386:
382:
379:Distribution
374:
355:
344:
334:
324:Adults have
323:
319:John Bachman
302:
298:
293:
292:
288:
287:
275:
267:
221:
220:
198:
196:
180:
179:
167:
18:
2987:NatureServe
2948:iNaturalist
2837:Wikispecies
2645:24 February
999:30 December
905:12 November
821:NatureServe
758:cottonmouth
746:black racer
711:Hymenoptera
707:Lepidoptera
657:Food habits
567:beyrichiana
484:cottonmouth
454:Clutch size
215:Subspecies
80:NatureServe
76:Vulnerable
3200:Categories
3026:Xeno-canto
2390:(3): 542.
2073:The Condor
1970:The Condor
1548:The Condor
1294:2020-02-24
1179:0813012880
1141:0253107369
835:References
750:corn snake
703:Coleoptera
695:Orthoptera
571:Andropogon
532:Andropogon
366:succession
3058:Q21127377
2514:0378-1127
2471:1528-7092
2431:870465050
2255:0012-9658
2220:0273-8570
2177:0022-541X
2131:0273-8570
2095:0010-5422
2041:1559-4491
1992:0010-5422
1632:201201252
1624:1712-6568
1570:0010-5422
1514:984128181
1289:ebird.org
1264:0004-8038
1217:0043-5643
790:blue jays
786:fire ants
762:coachwhip
721:Predators
684:Vaccinium
576:Pityopsis
535:spp. and
436:shortleaf
412:Migration
347:granivore
175:Species:
113:Kingdom:
107:Eukaryota
3157:11094816
3108:45511228
3052:Wikidata
2992:2.105170
2979:22721256
2881:22721256
2876:BirdLife
2828:Q2229917
2822:Wikidata
2608:16 April
2479:90841653
2369:85819967
2185:85718569
2103:11010598
2049:86787230
2000:18305033
1927:86276066
1578:90815321
1416:30054395
943:16 April
678:Paspalum
646:Aristida
565:Aristida
495:Survival
425:Breeding
309:that is
259:Synonyms
153:Family:
127:Chordata
123:Phylum:
117:Animalia
103:Domain:
60:IUCN 3.1
3216:Peucaea
3144:2491946
3005:1538625
2930:7341544
2863:Avibase
2724:Peucaea
2573:4084555
2553:The Auk
2423:4161959
2361:4131084
2324:Thesis.
2306:3784491
2263:1935091
2235:Ecology
2139:4514284
1919:3784806
1847:3784060
1808:3802298
1759:4514284
1714:4087909
1702:The Auk
1674:3802793
1464:3802716
1389:4162564
1272:4072214
1244:The Auk
1225:4156717
963:Avibase
699:Araneae
672:Setaria
579:spp.).
360:by the
351:insects
340:forests
313:to the
311:endemic
209:, 1823)
168:Peucaea
163:Genus:
143:Order:
133:Class:
78: (
58: (
3170:179386
3128:FEIS:
3116:EURING
3092:ECOS:
3067:ARKive
3018:292633
2966:997733
2937:GNAB:
2917:bacspa
2891:bacspa
2856:bacspa
2660:Stamps
2571:
2512:
2477:
2469:
2429:
2421:
2367:
2359:
2304:
2261:
2253:
2218:
2183:
2175:
2137:
2129:
2101:
2093:
2047:
2039:
1998:
1990:
1945:Thesis
1925:
1917:
1845:
1806:
1757:
1712:
1672:
1630:
1622:
1576:
1568:
1512:
1462:
1414:
1387:
1270:
1262:
1223:
1215:
1177:
1139:
1020:
780:, and
770:bobcat
766:coyote
760:, and
326:rufous
250:
244:
3183:78453
3152:IRMNG
3121:18110
3085:5TV45
2953:73172
2912:eBird
2904:4FF33
2888:BOW:
2727:genus
2668:VIREO
2569:JSTOR
2549:(PDF)
2475:S2CID
2419:JSTOR
2365:S2CID
2357:JSTOR
2302:JSTOR
2259:JSTOR
2181:S2CID
2135:JSTOR
2099:S2CID
2045:S2CID
1996:S2CID
1923:S2CID
1915:JSTOR
1843:JSTOR
1831:(PDF)
1804:JSTOR
1784:(PDF)
1755:JSTOR
1743:(PDF)
1710:JSTOR
1670:JSTOR
1628:S2CID
1608:(2).
1574:S2CID
1460:JSTOR
1412:JSTOR
1385:JSTOR
1373:(PDF)
1268:JSTOR
1221:JSTOR
848:from
690:Carex
510:Pinus
419:eBird
3165:ITIS
3139:GBIF
3131:aiae
3095:6177
3000:NCBI
2974:IUCN
2961:ITIS
2925:GBIF
2647:2008
2610:2023
2510:ISSN
2467:ISSN
2427:OCLC
2251:ISSN
2216:ISSN
2173:ISSN
2127:ISSN
2091:ISSN
2037:ISSN
1988:ISSN
1620:ISSN
1566:ISSN
1510:OCLC
1260:ISSN
1213:ISSN
1175:ISBN
1137:ISBN
1063:1–16
1018:ISBN
1001:2016
945:2023
907:2021
890:2020
817:IUCN
788:and
768:and
438:and
362:IUCN
337:pine
330:buff
137:Aves
3103:EoL
3080:CoL
2899:CoL
2852:ABA
2561:doi
2502:doi
2498:211
2459:doi
2392:doi
2349:doi
2243:doi
2208:doi
2165:doi
2081:doi
2077:112
2029:doi
2025:125
1978:doi
1974:117
1907:doi
1796:doi
1706:107
1662:doi
1610:doi
1556:doi
1552:119
1452:doi
1381:100
1252:doi
1110:doi
990:doi
894:doi
799:by
301:or
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3180::
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3154::
3141::
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2557:92
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1913:.
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1100:.
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