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Pipilo erythrophthalmus


SPECIES: Pipilo erythrophthalmus


  Will Cook,

Meyer, Rachelle. 2006. Pipilo erythrophthalmus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: [].



eastern towhee

Pipilo erythrophthalmus (Linnaeus) is the scientific name for eastern towhee, a member of the Emberizidae family [3]. In 1995, the American Ornithologists' Union split the rufous-sided towhee (P. erythrophthalmus) into the eastern and spotted towhee (P. maculatus) [2]. Hybridization between the 2 species occurs along riparian corridors in the Great Plains, especially on the Platte River [42,82]. The 4 eastern towhee subspecies recognized by the American Ornithological Union [1] are:

P. e. ssp. erythrophthalmus (Linnaeus)
P. e. ssp. alleni Coues
P. e. ssp. canaster Howell
P. e. ssp. rileyi Koelz



No special status



SPECIES: Pipilo erythrophthalmus
The eastern towhee occurs throughout the eastern United States. Occurrences from southern Saskatchewan and Quebec south to Florida, and west to eastern Texas are noted in a literature review. Populations north of southern New England through northern Indiana and Illinois to southern Iowa are primarily summer residents [42]. A general range map for the eastern towhee is available at Cornell's All About Birds, and a summer distribution map of the eastern towhee from Breeding Bird Survey data (1966-1996) can be found at Patuxent Wildlife Research Center.

Pipilo e. erythrophthalmus occurs in the most northerly part of the eastern towhee's distribution in the summer, and migrates to the southern and eastern portion of the species' range in the winter. The other subspecies are largely residents [69]. Pipilo e. canaster occurs from south-central Louisiana, north to northeastern Louisiana east through Mississippi, extreme southwestern Tennessee, northern Alabama and Georgia, central South Carolina to western North Carolina, and south to northwestern Florida and east along the Gulf Coast [1]. The range of P. e. rileyi extends from northern Florida through southern Georgia and coastal South Carolina to east-central North Carolina. Pipilo e. alleni occurs in peninsular Florida [69].

The following lists are based on eastern towhee distribution information and the habitat characteristics and plant species composition of vegetation communities eastern towhees are known to occupy. There is not conclusive evidence that eastern towhees occur in all the habitat types listed, and some community types, especially those in the western portion of the eastern towhee's range, may have been omitted. Abundance of eastern towhees in the community types listed is quite variable. Some plant communities support eastern towhees only in stands of specific ages or types, while others provide suitable habitat throughout. See Preferred Habitat/Cover for more detail.

FRES10 White-red-jack pine
FRES11 Spruce-fir
FRES12 Longleaf-slash pine
FRES13 Loblolly-shortleaf pine
FRES14 Oak-pine
FRES15 Oak-hickory
FRES16 Oak-gum-cypress
FRES17 Elm-ash-cottonwood
FRES18 Maple-beech-birch
FRES19 Aspen-birch
FRES39 Prairie
FRES41 Wet grasslands

STATES/PROVINCES: (key to state/province abbreviations)



14 Great Plains

K074 Bluestem prairie
K076 Blackland prairie
K077 Bluestem-sacahuista prairie
K078 Southern cordgrass prairie
K079 Palmetto prairie
K080 Marl everglades
K081 Oak savanna
K082 Mosaic of K074 and K100
K083 Cedar glades
K084 Cross Timbers
K089 Black Belt
K091 Cypress savanna
K092 Everglades
K093 Great Lakes spruce-fir forest
K094 Conifer bog
K095 Great Lakes pine forest
K096 Northeastern spruce-fir forest
K097 Southeastern spruce-fir forest
K098 Northern floodplain forest
K099 Maple-basswood forest
K100 Oak-hickory forest
K101 Elm-ash forest
K102 Beech-maple forest
K103 Mixed mesophytic forest
K104 Appalachian oak forest
K105 Mangrove
K106 Northern hardwoods
K107 Northern hardwoods-fir forest
K108 Northern hardwoods-spruce forest
K109 Transition between K104 and K106
K110 Northeastern oak-pine forest
K111 Oak-hickory-pine
K112 Southern mixed forest
K113 Southern floodplain forest
K114 Pocosin
K115 Sand pine scrub
K116 Subtropical pine forest

12 Black spruce
13 Black spruce-tamarack
14 Northern pin oak
16 Aspen
17 Pin cherry
18 Paper birch
19 Gray birch-red maple
20 White pine-northern red oak-red maple
21 Eastern white pine
22 White pine-hemlock
23 Eastern hemlock
24 Hemlock-yellow birch
25 Sugar maple-beech-yellow birch
26 Sugar maple-basswood
27 Sugar maple
28 Black cherry-maple
30 Red spruce-yellow birch
31 Red spruce-sugar maple-beech
32 Red spruce
33 Red spruce-balsam fir
34 Red spruce-Fraser fir
38 Tamarack
39 Black ash-American elm-red maple
40 Post oak-blackjack oak
42 Bur oak
43 Bear oak
44 Chestnut oak
45 Pitch pine
46 Eastern redcedar
50 Black locust
51 White pine-chestnut oak
52 White oak-black oak-northern red oak
53 White oak
55 Northern red oak
57 Yellow-poplar
58 Yellow-poplar-eastern hemlock
59 Yellow-poplar-white oak-northern red oak
60 Beech-sugar maple
61 River birch-sycamore
62 Silver maple-American elm
63 Cottonwood
64 Sassafras-persimmon
65 Pin oak-sweetgum
69 Sand pine
70 Longleaf pine
71 Longleaf pine-scrub oak
72 Southern scrub oak
73 Southern redcedar
74 Cabbage palmetto
75 Shortleaf pine
76 Shortleaf pine-oak
78 Virginia pine-oak
79 Virginia pine
80 Loblolly pine-shortleaf pine
81 Loblolly pine
82 Loblolly pine-hardwood
83 Longleaf pine-slash pine
84 Slash pine
85 Slash pine-hardwood
87 Sweetgum-yellow-poplar
88 Willow oak-water oak-diamondleaf (laurel) oak
91 Swamp chestnut oak-cherrybark oak
92 Sweetgum-willow oak
93 Sugarberry-American elm-green ash
94 Sycamore-sweetgum-American elm
95 Black willow
96 Overcup oak-water hickory
98 Pond pine
100 Pondcypress
101 Baldcypress
102 Baldcypress-tupelo
103 Water tupelo-swamp tupelo
104 Sweetbay-swamp tupelo-redbay
105 Tropical hardwoods
106 Mangrove
108 Red maple
109 Hawthorn
110 Black oak
111 South Florida slash pine

601 Bluestem prairie
710 Bluestem prairie
711 Bluestem-sacahuista prairie
717 Little bluestem-Indiangrass-Texas wintergrass
726 Cordgrass
731 Cross timbers
732 Cross timbers
801 Savanna
802 Missouri prairie
803 Missouri glades
805 Riparian
806 Gulf Coast salt marsh
807 Gulf Coast fresh marsh
808 Sand pine scrub
809 Mixed hardwood and pine
810 Longleaf pine-turkey oak hills
811 South Florida flatwoods
812 North Florida flatwoods
813 Cutthroat seeps
814 Cabbage palm flatwoods
815 Upland hardwood hammocks
816 Cabbage palm hammocks
817 Oak hammocks
818 Florida salt marsh
819 Freshwater marsh and ponds
820 Everglades flatwoods
822 Slough

In addition to the community types listed above, eastern towhee occurs in vegetation of disturbed areas, such as old-field successional vegetation and shrubby areas of power line right-of-ways. In northwestern Arkansas, eastern towhees occurred in old-field vegetation where dwarf sumac (Rhus copallina) occurred at a frequency of 28.6%, winged elm (Ulmus alata) at a frequency of 21%, and black cherry (Prunus serotina) at a frequency of 19.2% [7]. Shrubby vegetation along power lines is commonly used by eastern towhees [37,105]. For example in Maryland, eastern towhee territories along a power line right-of-way corresponded with shrubby areas comprised of species such as Allegheny blackberry (Rubus allegheniensis) and blueberry (Vaccinium spp.). Other species included hawthorn (Crataegus spp.), red maple (Acer rubrum), black cherry, and black locust (Robinia pseudoacacia) [37].


SPECIES: Pipilo erythrophthalmus


  G. K. Peck, Environment Canada

Arrival and departure of eastern towhees into summer breeding grounds (see General Distribution) varies with location. According a to literature review, eastern towhees typically arrive in New York in early April and leave by the middle of November [17]. A review of eastern towhee in New Hampshire describes arrival in late April to May with the majority of eastern towhees departing in September [34]. Further south, on the border of Tennessee and North Carolina, migration to high-elevation areas within the Great Smoky Mountains begins as early as March. Eastern towhees typically leave these sites in October [88]. The Pipilo e. erythrophthalmus subspecies is the most migratory of the subspecies [69].

Breeding begins in spring and continues to late summer. Reports of eastern towhees nesting as early as late March in Florida and Georgia, in mid- to late April in some midwestern states, and as late as mid-May in northern New England were summarized in a literature review [42]. Literature reviews also report nest construction by the female, which takes about 3 to 5 days [34,42]. Egg laying typically occurs until August. For example, a review of eastern towhee in Indiana notes nesting from 15 April to 20 August [67]. However, a literature review of eastern towhee in Florida included a report of an eastern towhee nest observed on 2 September 1983 that contained 2 eggs [86]. According to several literature reviews, eastern towhees may renest after failed nesting attempts and can raise 2, and in the south sometimes 3, broods per season [34,42,86].

In a literature review, Greenlaw [42] reports mean breeding territory size of 4 acres (1.6 ha) (range 1.6-6 acres (0.64-2.44 ha), n=24) in a mesic oak (Quercus spp.) forest where eastern towhees occurred at a density of 21 males/40 ha. In a xeric pine (Pinus spp.)-oak woodland where eastern towhee density was 32 males/40 ha, mean eastern towhee territory size was 3 acres (1.2 ha) (range 1.8-4 acres (0.71-1.65 ha), n=20) [42]. In Massachusetts, mean male eastern towhee territory size was about 1.3 acres (0.52 ha), and female eastern towhee territory size was 1.1 acres (0.45 ha). Territory size changed over the course of the breeding season and was not significantly (p>0.05) affected by reductions in food availability of 30% or less [97]. During the winter eastern towhees are not as territorial and may be seen in mixed species flocks [42]. Daily movement of eastern towhees in loblolly (P. taeda) and longleaf pine (P. palustris) forests and clearcuts in South Carolina averaged 325 feet (99 m) per day. Only 2 females, out of 11 females and 9 males, stayed within the stand where they were captured for the duration of a 10-week study [52].

Eastern towhees have fairly strong fidelity to breeding territories. In an oak forest in New Jersey, adult eastern towhee return rates were 20% the 1st year after banding and 43% in subsequent years. Between 1960 and 1967, the maximum number of eastern towhee returns to the site was 5 [57]. In a Pennsylvania woodlot observed between 1962 and 1967, an eastern towhee returned to the site for 4 consecutive years [79].

Several literature reviews report eastern towhee clutch sizes from 2 to 6 eggs, with means ranging from 2.45 to 3.6 eggs per nest [34,42,67,86]. All 5 eastern towhee nests on Sanibel Island, Florida, contained 3 eggs [74]. Eastern towhees in 2 pitch pine (P. rigida) barrens sites in New Jersey and New York had a later median egg laying date (mid-June) and significantly (p<0.05) smaller average early nest clutch sizes (NJ=2.67, NY=3.25) than those in an oak-hickory (Carya spp.) site, which had a median egg-laying date in early June and an average early nest clutch size of 3.88. Food availability likely explains at least some of the differences between the 2 habitat types [41].

Reviews also note that eggs are incubated by the female for 12 or 13 days. After hatching both parents feed the young, which fledge 10 to 12 days later and are dependent on parental care for about another month [34,42,67,86].

A wide range of eastern towhee nest success values have been reported. On Sanibel Island, 1 of the 5 eastern towhee nests observed was successful. In Louisiana, average daily nest success rate was 95.3% on a bottomland hardwood forest site. The same study found a 92.6% average daily nest success rate in a 6-year-old managed cottonwood (Populus spp.) plantation in Alabama [93]. Average eastern towhee nest success across mixed bigtooth (P. grandidentata) and quaking aspen (P. tremuloides) stands of varying ages in Pennsylvania was 48.1% [103]. In South Carolina, only 1 of 10 nests was successful, and the mean daily nest survival rate was 62.9%. This low value was explained by high levels of predation. Due to lower nest success rates of Bachman's sparrow (Aimophila aestivalis) than the previous year, it is suggested that eastern towhee nest success may have been measured during a comparatively poor year [52].

Compared to nests, adult towhee survival rates are high. Average weekly adult survival rate of eastern towhees in a South Carolina study area was 99.3%. This rate was obtained from radio-marked eastern towhees and represented the pooled survival of both sexes and from 2 South Carolina sites, young and mature stands of loblolly and longleaf pine [52]. Between 1962 and 1967 in Pennsylvania, annual survival of breeding eastern towhees calculated from mistnetting recaptures was 58% [79]. According to a literature review, both males and females become reproductively mature in their 2nd year [42]. Eastern towhees of over 12 years old have been reported in the wild [51].

Eastern towhees range from near sea level [13] to as high as 6,500 ft (1,980 m) along the border of Tennessee and North Carolina during the summer [88]. A literature review reports eastern towhees up to 3,000 feet (900 m) in New Hampshire [34].

Eastern towhees spend the majority of their time near the ground. For instance, in Pennsylvania in spring, observations of eastern towhees below 3 feet (1 m) from the ground occurred significantly (p<0.05) more than expected based on random spatial distribution, and observations above 3 feet (1 m) occurred significantly (p<0.05) less than would be expected [102]. In a Louisiana bottomland forest 62% of eastern towhee observations were within 2 feet (0.6 m) of the ground, and only 4% were observed above 25 feet (7.6 m). In the spring this changed, with detections of eastern towhees below 25 feet (7.6 m) declining from 70% to 65% and detections in the canopy (>25 ft (>7.6 m)) increasing from 4% to 7% [24].

Eastern towhees occur in many habitats, from tallgrass prairies [106] and marshes [13] to mature forests [52]. However, eastern towhees are most common in early successional stands, habitat edges (see Effects of spatial arrangement/area), and areas with similar vegetation structure throughout eastern forests.

In most communities eastern towhees are more abundant in young successional stands. Several studies found increased eastern towhee abundance on early successional sites compared to later-successional sites [28,30,49,56,91,102]. Mean number of breeding eastern towhees (0.70 bird/50-m radius) and nest success rate (58%) were higher in a 15-year-old clearcut in west Virginia, than in other treatments, including a stand comprised of yellow-poplar (Liriodendron tulipifera), black cherry, red maple, sugar maple (Acer saccharum), and white ash (Fraxinus americana) that was not harvested [28]. In a southern Missouri oak-hickory forest, eastern towhees were not present before clearcutting or in the nearby uncut forest after cutting, but occurred at a mean density of 9.3 birds/10 ha in a 3-year-old clearcut [91]. A study of stands of varying ages in central New York found that eastern towhee density peaked in early successional stands [49]. The following table shows higher frequencies of eastern towhees in young (≤17 years old) compared to mature (≥40 years old) stands of varying community types in South Carolina [56].

  Cove-hardwood Mixed pine-hardwood Upland hardwood White pine (Pinus strobus) Southern yellow pine
Young 0.17 0.54 0.57 0.56 0.33
Mature 0.0 0.09 0.06 0.0 0.13

Although eastern towhees generally prefer young successional sites, variation between habitat types and years has been observed. Krementz and Powell [52] found higher relative abundance of eastern towhee in young (2-6 years old) stands of loblolly and longleaf pine than mature (32-98 years old) stands when investigated in 1995. However, in stands compared in 1996, the 95% confidence intervals of eastern towhee relative abundance on the 2 sites had a substantial degree of overlap. The degree to which eastern towhee responds to succession is influenced by habitat. For example, in Pennsylvania there was a significant (p<0.05) difference between eastern towhee densities (number/10 ha) between mature mixed-oak forest and stands that had been clearcut about 5 years previously. However, eastern towhee densities did not differ significantly between a 1-year old mixed aspen (Populus tremuloides, P. grandidentata) clearcut, a 5-year old aspen clearcut, and a mature aspen stand [101]. Eastern towhee abundance has been shown to peak at different times in different habitats. For instance, although in central hardwood forests eastern towhees were most abundant in regenerating stands, in loblolly and shortleaf pine forest they were most common in pole timber and mature stands [25]. In addition, Bell and Whitmore [8] concluded that early successional is likely too broad of a term for describing optimal towhee habitat, since high density of small trees was negatively associated with eastern towhee density in the eastern panhandle of West Virginia.

Eastern towhees seem to prefer sites with characteristics generally associated with early successional vegetation, such as low canopy cover and dense understory. Negative correlations between eastern towhee abundance and various measurements of overstory density have been found in several studies [7,8,20,101]. Average density of eastern towhees across 6 habitat types in Pennsylvania was significantly (p<0.05) negatively correlated with density of overstory trees and basal area of overstory trees [101]. Number of eastern towhees in a western Virginia hardwood forest was also significantly (p<0.05) inversely correlated with total percent canopy cover [20]. In a loblolly pine forest in South Carolina, the average number of eastern towhee breeding territories per experimental unit was significantly (p0.008) negatively correlated with mid-story (10-46 feet (3-14 m)) pine (Pinus spp.) and deciduous volume [59].

Many studies have demonstrated a positive correlation between eastern towhee abundance and understory density. In a loblolly pine forest in South Carolina, understory (0-10 ft (0-3 m)) pine volume was significantly (p<0.001) positively correlated with the average number of eastern towhee territories per experimental unit [59]. Yahner [101] found the average density of eastern towhees over 6 habitat types was significantly (p<0.05) positively correlated with density of short (2-5 foot (0.5-1.5 m)) shrubs. In east-central Florida slash pine (P. elliottii) flatwoods with understories dominated by myrtle oak (Q. myrtifolia) and sand live oak (Q. geminata) and in scrub sites with scattered slash pine and cabbage palmetto (Sabal palmetto), eastern towhee densities were significantly (p=0.01) negatively correlated with mean shrub height [14].

Coarse woody debris favors eastern towhee populations. In a loblolly pine forest in South Carolina, experimental removal of downed coarse woody debris resulted in a significant (p=0.042) decline in eastern towhee breeding territories [59]:

Downed woody debris density (stems/ha) Eastern towhee density (birds/300 m²)
Treatment 9.3 0.1
Control 96.3 1.9

Eastern towhees may associate with and avoid certain plants. In riparian vegetation in Iowa, eastern towhee density was significantly (p≤0.01) positively associated with total plant and vine species richness and negatively correlated with forb and deciduous tree species richness [85]. In West Virginia, eastern towhees were associated with plant species that occurred on drier ridgetops, such as blackberry (p<0.02), black cherry (p<0.002), and black locust (p<0.04). These sites tended to have open canopies and low tree density. Eastern towhee density was negatively associated with plants of the moister parts of this study area, such as black tupelo (Nyssa sylvatica, p<0.006), red maple (p<0.001), and witch hazel (p<0.03) [8]. In central New Jersey eastern towhees were significantly (p=0.03) more abundant in gray dogwood (Cornus racemosa) shrubland than either eastern redcedar (Juniperus virginiana) or multiflora rose (Rosa multiflora) shrublands [89].

Nesting habitat: Eastern towhees typically nest on or near the ground. Several literature reviews note the predominance of eastern towhee nests below 5 feet (1.5 m) [34,42,67,86]. In a study of cowbird parasitism on Sanibel Island, all 5 eastern towhee nests located were within 6 feet (2 m) of the ground [74]. Nests as high as 18 feet (5.5 m) have been reported in literature reviews [34,42,67]. Nests higher off the ground in mixed aspen stands of varying ages in Pennsylvania had significantly (p<0.001) lower nest success. Of 13 unsuccessful eastern towhee nests, 11 were greater than 1 foot (0.5 m) above the ground. [103].

Compared to random plots in oak-hickory vegetation in West Virginia (n=421), eastern towhee nesting areas were more likely to contain more grapes (Vitis spp., p=0.0069), fewer small (0-3 inches dbh (0-7.6 cm)) saplings (p<0.001), and fewer large (>15 inches dbh (>38.1 cm)) live trees (p=0.011) [9].

In West Virginia, there were no significant (p>0.05) differences in habitat surrounding successful and unsuccessful nests. Large snags (≥9 inches dbh (22.9 cm)) did not have an effect on nesting success [9]. Nesting success was not significantly (p>0.05) affected by stand age or distance to edge in even-aged mixed-aspen stands in Pennsylvania. The table below shows the density of nests and the number of successful nests in stands of varying ages [103].

Total Young (5-6 years) Intermediate (9-10 years) Mature (60 years)
Number of nests 27 13 12 2
Nest density (nests/10 ha) ---- 8.7 8.0 1.3
Number successful 13 7 6 0

Eastern towhees nest in a variety of species including grape and blueberry (Vaccinium spp.). The majority of nests observed in South Carolina loblolly and longleaf pine forests and clearcuts were located in grape, tree sparkleberry (V. arboreum), and oak (Quercus spp.) [52]. On an oak-hickory site in West Virginia, 27% of 41 eastern towhee nests were found in grape, 17% in blackberry (Rubus spp.), 12% in greenbrier (Smilax spp.), and 12% in mountain-laurel (Kalmia latifolia). Nests also occurred in Virginia creeper (Parthenocissus quinquefolia), spice bush (Lindera benzoin), and azalea (Rhododendron spp.) [9]. In a power line right-of-way in Pennsylvania, the 6 eastern towhee nests observed occurred in Allegheny blackberry, witch-hazel (Hamamelis virginiana), blueberry (Vaccinium spp.), white oak (Q. alba), eastern hayscented fern (Dennstaedtia punctilobula) and sweetfern (Comptonia peregrina) combined, and on ground level [105]. According to literature reviews eastern towhee nests located on the ground are embedded in litter in dry areas and typically occur at the base of grasses, forbs, low shrubs, or small trees [42,67].

Foraging Habitat: Selection of forging habitat by eastern towhees has been investigated in Massachusetts and New Jersey. When gleaning in a southeastern Massachusetts pitch pine barren, eastern towhees preferred species such as pitch pine, bear oak (Q. ilicifolia), and other deciduous trees, mainly oaks. Ericaceous species were avoided. Use differed significantly (p<0.001) from availability [66]. On 2 New Jersey sites, eastern towhee foraging preference switched over the course of the breeding season [15]. On a site dominated by oaks, primarily black oak (Q. velutina), eastern towhees used oaks in May, as would be expected due to their density. However, in June and July, as relative arthropod biomass declined in oaks, use of oaks was less than would be expected. On a pitch pine-dominated site, use of oaks (primarily bear oak and blackjack oak (Q. marilandica)) was greater than would be expected in May, but was proportionate to availability in June and July. These negative correlations between date and oak use were significant (p<0.025) for both sites. Use of the oak-dominated site also decreased significantly (p<0.05) through the summer. [15].

Effects of spatial arrangement/area: Eastern towhees appear to prefer edge habitats in many areas. For instance, the mean abundance of eastern towhees in a baldcypress (Taxodium distichum)- clearcut edge in northern Florida was 18, while eastern towhees did not occur in either the baldcypress forest or the clearcut. At the interface of the baldcypress stand and a 13-year-old planted slash pine stand, mean abundance of eastern towhees was 22 breeding birds, while in the planted slash pine stand the average abundance was 15 breeding birds [64]. Density of eastern towhees was found to decline with distance from the edge of a power line right-of-way and an oak-hickory forest in eastern Tennessee. At the edge eastern towhees occurred at a density of just over 10 pairs/40 ha, while 197 feet (60 m) from the edge eastern towhee density had dropped to 1 pair/40 ha [53]. In addition, in experimentally clearcut Pennsylvanian forests comprised of white oak, northern red oak (Q. rubra), chestnut oak (Q. prinus), scarlet oak (Q. coccinea), red maple, quaking aspen, bigtooth aspen, and pitch pine [104], male towhees were detected significantly (p<0.05) more often than expected in the areas where the spatial arrangement of clearcuts was most patchy [58].

Several studies have addressed the effect of the size of habitat patches on eastern towhees. In mixed-oak forest in New Jersey, eastern towhee frequency generally increased with patch size, although eastern towhees were detected in all plot sizes (0.5-59 acres (0.2- 24 ha)) except 0.02-acre (0.01 ha) plots [35]. On a site in South Carolina, eastern towhee frequency of occurrence increased as clearcut size increased from <2.5 acres (<1 ha) to clearcut sizes from 21 to about 32 acres (8.5-12.8 ha). On another site eastern towhee frequency declined as clearcut size increased from 19 to 33 acres (7.6-13.2 ha) to 48 to 62 acres (19.5-25.2 ha) [56]. Eastern towhees only bred in riparian vegetation patches in Iowa that were at least 650 feet (200 m) wide [85]. In southern and eastern Pennsylvania eastern towhee nest success was not significantly (p≥0.10) different on sites with gradual edges and those with more distinct edges between "wildlife habitat openings" and oak-hickory forest [26].

Eastern towhees primarily eat on the ground, although they also glean from vegetation. In a southeastern Massachusetts pitch pine barren, 73.5% of male and 80.4% of female foraging observations were on the ground [66]. When foraging on the ground eastern towhees use a scratching technique where both feet kick back simultaneously [40,86]. In a laboratory study 4 eastern towhees used this method to successfully obtain seed buried almost 1 inch (2.25 cm) deep [98]. When foraging above ground the majority of time is spent gleaning foliage [66]. In Massachusetts, 22.5% of male and 16.3% of female foraging observations were of food being gleaned from foliage. Eastern towhees were also observed gleaning from twigs, branches, and trunks. When gleaning, eastern towhees occurred significantly (p<0.01) more often on the distal half of tree branches compared to using distal and proximal portions equally (see Foraging Habitat). In 0.5% of male and 0.3% of female foraging observations, eastern towhees hovered. Eastern towhees were never observed catching food out of the air [66].

Eastern towhees eat a variety of plant and animal matter. In literature reviews, eastern towhees are reported to eat seeds and fruits, several invertebrates, and occasionally small amphibians, snakes, and lizards [86]. Reviews report eastern towhees foraging at feeders [17,42]. Reviews show that animal matter makes up a larger proportion of the diet in the breeding season [42,63]. In fall and winter, plants make up 79% and 85% of the diet, respectively. This drops to 53% in spring and 43% in summer [63]. Insects such as beetles (Coleoptera), grasshoppers and crickets (Orthoptera), ants, wasps, and bees (Hymenoptera), and moths and caterpillars (Lepidoptera) are common prey items. Eastern towhees eat other invertebrates such as spiders (Araneae), millipedes (Diplopoda), centipedes (Chilopoda), and snails (Gastropoda) to a lesser extent [42,63]. Plants that comprise at least 5% of the eastern towhee diet include ragweed (Ambrosia spp.), oak, smartweed (Polygonum spp.), and corn (Zea mays) in the Northeast and blackberry, oak, panicgrass (Panicum spp.), ragweed, and wax-myrtle (Morella cerifera) in the Southeast [63]. The following table, adapted from Greenlaw's [42] literature review, shows the relative total volume (%) and frequency of occurrence (%, in parentheses) of different food items found in the stomach contents of adult eastern towhees.

Northeastern Region Midwestern Region Southeast Atlantic/Mid-Gulf Region
May-June Sept-Oct May-June Sept-Oct May-June Sept-Oct
Insects (adult) 29.6 (93) 0.6 (40) 49.2 (98) 35.1 (91) 32.8 (95) 2.5 (73)
Insects (immature) 5.4 (24) 0 4.7 (25) 2.4 (13) 13.0 (46) 0
Spiders 0.3 (6) 0.8 (20) 1.3 (17) 0.5 (13) 1.7 (18) 0
Millipedes 0.5 (9) 0.6 (20) 2.8 (15) 0.3 (9) 0.1 (2) 0
Centipedes 0 0.4 (20) 0.1 (2) 0 0 0
Snails 0.3 (3) 0 0.1 (6) 0 0.1 (2) 0
Plant 63.8 (91) 97.6 (100) 42.0 (67) 61.4 (83) 49.8 (79) 97.5 (100)

Many animals prey on eastern towhees and their eggs, including reptiles, mammals, and birds. A literature review summarizes several reports demonstrating that predators are a major cause of nest failure [42]. The highest nest predation rate noted was 88% in a New York study. Mammals that are likely nest predators include northern raccoons (Procyon lotor), domestic cats (Felis catus), and eastern chipmunks (Tamias striatus). Snakes such as bullsnakes (Pituophis catenifer), rat snakes (Elaphe spp.) and garter snakes (Thamnophis spp.) have been reported eating eastern towhee eggs. Weasels (Mustela spp.) and blue jays (Cyanocitta cristata) are also likely nest predators [42]. Several birds are known to prey on adult eastern towhees, including short-tailed (Buteo brachyurus), sharp-shinned (Accipiter striatus), and Cooper's hawks (Accipiter cooperii) [70,87]. At least some mammals also feed on adult eastern towhees. In Maryland, an eastern towhee was found in the stomach contents of a red fox (Vulpes vulpes) [47].

Brown-headed cowbirds (Molothrus ater) parasitize eastern towhee nests. In a South Carolina old field 5 of 19 eastern towhee nests were parasitized [100]. Each parasitized nest contained 1 brown-headed cowbird egg. The desertion rate for parasitized nests was 20%, which was similar to nests that had not been parasitized (21%). Two of the five brown-headed cowbird eggs produced fledglings. The study did not determine if there was a difference in nest success between parasitized and nonparasitized nests [100]. In West Virginia, only 3 of 41 eastern towhee nests were parasitized by the brown-headed cowbird. Average number of fledged young in nonparasitized nests was 2.8, which was similar to the average of 2.7 fledglings per parasitized nest [9]. In a Pennsylvania study site, only 2 of 36 nests were parasitized and both produced eastern towhee fledglings [26]. In a study of nest parasitism on Sanibel Island, none of 5 eastern towhee nests found were parasitized [74].

Greenlaw's [42] literature review provides a detailed summary on eastern towhee behaviors, such as vocalizations, courtship, territoriality (see Timing of Major Life History Events), and migration (see General Distribution).

Data from the Breeding Bird Survey and Christmas Bird Counts show moderate to large declines in eastern towhee populations, especially in the northern part of its range [11,18,44,72]. For example, trends from 3 surveys showed that 1989 population levels were 13% of 1966 levels in the Northeast [44]. A literature review provides some information suggesting the decline has slowed in some areas in recent years [42].

Managing habitat for the eastern towhee and species with similar habitat requirements has been the subject of many articles including [20,22,65,90,104]. Greenlaw's [42] literature review notes the impact of urbanization and agriculture on eastern towhee habitat and asserts the importance of preserving pitch pine barren habitats in the Northeast, where eastern towhees still occur in relatively high densities.


SPECIES: Pipilo erythrophthalmus
Adult eastern towhees are unlikely to suffer directly from fire. It is generally accepted that large, fast-moving fires can result in mortality, but birds typically have the mobility to avoid fire [19,23,76]. Spotted towhees (Pipilo maculatus), birds that are closely related and have similar habits as eastern towhees, were observed alive after a fire in California coastal sage scrub [12].

It is likely that eggs and young birds are much more vulnerable to fire. Although there were no data directly investigating eastern towhee nest mortality due to fire as of early 2006, literature reviews have used life history characteristics to speculate on possible effects of fire on nesting success and bird populations [62,77]. Since eastern towhees nest near the ground, low-severity surface fires during the breeding season could result in considerable nest mortality. However, the degree to which a population would be affected by fire would depend on several factors including occurrence of renesting, season of burn, fire interval, fire uniformity, and fire severity. Since eastern towhees have the tendency to renest, this may mitigate at least some of the impact a breeding-season fire would have [62,77]. Over 2 breeding seasons, 7 of 33 eastern towhee nests observed in a mature loblolly pine forest that had burned between 1 to 2 and 3 to 4 years earlier produced at least 1 fledgling [99]. The daily nest survival rate was 89%, and a mean of 0.68 fledgling was produced per active nest. These values could not be compared to the unburned site due to the lack of nests found there [99]. Higher [93] and lower [52] daily nest survival rates have been reported for eastern towhees in other areas (see Timing of Major Life History Events).

Despite the abundance of articles addressing the effect of fire on eastern towhees, results should be interpreted with caution. As noted by a literature review summarizing songbird responses to fire in southwestern ponderosa pine (Pinus ponderosa) forests [32], there are several limitations to many studies addressing bird response to fire. Many studies focus on breeding communities and use composite statistics, such as species richness. Many are opportunistic, restricted in spatial or temporal scale, include confounding factors and/or lack sufficient replication. Very few compare demographic parameters of a given species between burned and unburned vegetation, which is necessary to determine if the site is meeting the needs of a species [32].

Given that eastern towhees are strongly associated with low woody cover (see Preferred Habitat/Cover), their response is likely influenced by the interaction of habitat type, fire interval, fire uniformity, and fire severity. In habitats such as loblolly-shortleaf pineland and slash pine flatwoods, fairly frequent low-severity fires appear to benefit eastern towhees [14,30,99]. However in habitats such as tallgrass prairie, frequent fires eliminate eastern towhee from the habitat [106], likely due to a decline in shrubby cover. Patchy fires may benefit eastern towhees, due to increased edge (see Effects of spatial arrangement/area) and decreased damage to existing understory vegetation. Due to their cover requirements (see Preferred Habitat/Cover), eastern towhees may be affected by fires severe enough to seriously impact understory vegetation [94]. In cover types where eastern towhees occur primarily in early successional habitat, large stand-replacing fires may create patches that would provide eastern towhee habitat several years after the burn. Eastern towhees have been observed on a sand pine (Pinus clausa) scrub site in Florida 3 to 7 years after it was burned in a severe wildfire and subsequently salvage logged [38].

Eastern towhee's response to fire depends in part on the vegetation community. In some habitat types eastern towhees are present soon after burning, while in other habitat types eastern towhees do not occur on recently burned areas. For example, the average number of eastern towhee detections per census was approximately 5 on an old field pineland in Florida that had been winter-burned annually for approximately 30 years [30]. In Arkansas, eastern towhees occurred at a density of 6 territorial males/40 ha the spring following a winter burn in a field that had been dominated by broomsedge bluestem (Andropogon virginicus) and sassafras (Sassafras albidum) saplings [81]. Eastern towhees were also observed on wetlands burned 6 months earlier [95]. However, in an Indiana oak forest that had been surface burned 1 to 2 years and 3 to 4 years before sampling, eastern towhees were absent despite their occurrence in unburned control plots [5]. Eastern towhees did not occur in annually burned tallgrass prairies, but were observed in unburned (>10 years) tallgrass prairie in some years [106]. Eastern towhees did not occur in frequently burned longleaf pine sandhill plots [75]. In areas of Minnesota where frequent (12-26 fires in 32 years) fires were being used to restore oak savanna once dominated by bur oak (Quercus macrocarpa) and northern pin oak (Q. ellipsoidalis), eastern towhees were associated with unburned vegetation [21].

In some habitats eastern towhees increase after prescribed surface fires. Shortly after fire was excluded from an old-field loblolly-shortleaf (P. echinata) pineland that had previously been burned annually, eastern towhee occurrence increased. Eastern towhee detections per census increased from approximately 5 in postfire year 1 to over 12 in the 4th postfire year. After 4 years eastern towhee detections gradually declined. After 11 years of fire exclusion, eastern towhee detections were less than in the 1st postfire year. Due to eastern towhee absence in a beech-magnolia (Fagus-Magnolia spp.) stand, the authors predicted that as succession continues and the proportion of deciduous canopy increases, eastern towhees will eventually leave the site [30]. In coastal scrub and slash pine flatwoods in east-central Florida, eastern towhee densities were significantly (p=0.007) higher (4.5/ha) on sites that had burned 4 years before the survey than those that had been burned 1 year before (2.3/ha), 2 years before (3.3/ha), or more than 10 years before (2.6/ha) the survey [14]. The habitat with the greatest number of eastern towhees detected on Eglin Air Force Base in Florida was a "mature flatwoods" that had been burned 1 to 5 years before the survey. Eastern towhee detections in this habitat were significantly (p<0.05) greater than in both the burned (1-3 years previously) and unburned (for several decades) sandhills dominated by mature (>50 yr) longleaf pine [92]. In a loblolly pine forest with a mid-story dominated by oaks (Quercus spp.) and hickories (Carya spp.), eastern towhee abundance was significantly (p<0.05) greater on sites that had been burned either 1 year, 2 years, or 3 years before sampling (detections/count/site=3.79) compared to sites that had not been burned for more than 20 years (detections/count/site=1.44). Eastern towhees were also observed at higher frequencies in burned areas (89%) compared to unburned areas (74%) [99]. Three areas in Pennsylvania, one unburned area, one that had been burned 1 year earlier, and one that had been burned 2 years earlier were comprised of various habitats including a bluestem (Andropogon spp.) community, a scrub oak (bear oak and dwarf oak (Q. prinoides) community, a scrub oak-mixed aspen community, a scrub oak-pitch pine community, and a scrub oak-mixed-oak community. Eastern towhees were the most common bird in all three areas, but occurred at the highest density, approximately 0.67 singing male/ha, in the 2-year-old burn. In the unburned it occurred at a density of about 0.43 singing male/ha, and in the 1-year-old burn singing male eastern towhees occurred at a density of about 0.38/ha [83].

Differences in vegetation structure after burning may explain at least some of the variation in eastern towhee's response. A literature review demonstrated that changes in bird communities after fire are associated with the degree of structural change in the vegetation. More structurally complex habitats and more severe fires result in longer periods before the prefire bird community returns. For instance, the prefire bird community is typically restored about 3 years after a grassland fire, while it can take over 30 years for the prefire bird community to return after a stand-replacing forest fire [48]. Data on vegetation in areas where eastern towhee did and did not occur after fire show the effects of much smaller changes in vegetation structure. Vegetation on burned and unburned areas differed in an investigation that found significantly (p<0.05) higher eastern towhee abundance in burned areas. The unburned stands of loblolly pine with an understory of oaks and hickories had significantly (p<0.05) more hardwoods and total trees (≥7.5 cm dbh/ha), more snags and logs (≥7.5 cm/ha), higher percentage canopy closure, higher percentage of leaf litter, and lower percentage of herb cover than burned plots [99]. In contrast, an Indiana study area comprised of oak (Quercus spp.) dominated forests, chestnut oak (Q. prinus) woodlands, oak-hickory forests, and American beech (Fagus grandifolia)-sugar maple forests that were burned twice in 4 years had lower density of small 1 inch (<2.5 cm) dbh live woody stems and less horizontal vegetation cover below 1.6 feet (0.5 m) than the unburned site. In this study, eastern towhees were observed in the unburned vegetation, but not in the burned area [4,5].

Severity of the fire is also likely have a major impact on eastern towhee's response. In a literature review, it is suggested that fires of any severity are likely to affect ground-nesting birds, since even low-severity fire is likely to have large impacts on the vegetation they use [61]. Rotenberry and others [78] hypothesize in a literature review that "cool" and "intermediate" burns could increase food availability and leave adequate vegetation for ground-nesting birds. Data comparing eastern towhee densities among burns of varying severity are lacking. Observations of a pitch pine barren site in New Jersey shortly after a fairly extensive wildfire occurred in late winter/early spring did provide some information. The number of eastern towhees declined in some burned areas and increased in areas adjacent to the burn area. However, in areas within the burn where the vegetation was only slightly damaged and new growth provided cover, eastern towhee abundance was not affected [94]. In South Carolina, average weekly adult eastern towhee survival rates were not significantly (p=0.15) different in young (2-5 years old) longleaf pine stands than in mature (32-97 years old) longleaf pine stands that were occasionally thinned and surface burned under prescription every 3 to 5 years [52]. Eastern towhees were observed on a sand pine scrub site in Florida subject to a stand-replacing fire and salvage logging between 5 and 7 years before sampling. The following table shows the average density (number/km²) of eastern towhees on the burned and salvaged site and on a mature (≥55 years since stand-replacing fire) forest site [38].

Burned and salvaged Mature
Spring 286.1 147.2
Winter 197.2 111.1

Seasonal effect of burning on eastern towhee is uncertain. Literature reviews suggest that burns during the breeding season are likely to have a larger impact on ground-nesting birds, both directly through nest mortality and indirectly through greater and/or more persistent loss of cover than would likely occur from dormant season burns [61,77]. In addition, once territories are established eastern towhees may be less likely to leave a burned area [29]. No studies to date (2006) have compared eastern towhee demographics on sites burned in varying seasons. However, comparisons of eastern towhee abundance on sites burned during dormant and growing seasons have not resulted in detectable effects. On sites burned every 2 to 4 years in pure and mixed stands of longleaf, loblolly, and shortleaf pine in Georgia, eastern towhee abundance on sites burned between April and August (average of 1.54 birds/plot) was not significantly (p=0.32) different from the sites burned between January and March (average of 2.31 birds/plot) [50]. The following table shows the frequency (%) and abundance (total/40-m radius) of eastern towhees on control plots, plots burned in January, and plots burned in June in a dry prairie/shrubland in southwestern Florida [33]:

  Control Winter burn Summer burn
Frequency 44 44 64
Abundance 21 20 25

Fire is likely to have an affect on the availability of eastern towhee food items. Several literature reviews summarize information regarding changes in plant and animal food availability after fire [23,60,78]. Several shrubby species may increase fruit production after fire, although the response is dependent on the species and postfire environmental factors [23]. Seed and fruit production typically increase after fire in southern forests, with peak production from 2 to 6 years after fire. The frequency and season of burning influence plant recovery and fruit production [60]. Lyon and others' [60] review discusses the effect of fire on invertebrates, some of which are eastern towhee prey. Many of the studies found an increase in arthropod availability after understory fires in southern sandhill and loblolly-shortleaf pine forests [60].

Fire ecology: Eastern towhees occur in a variety of habitats with a wide range of fire regimes. However, areas with the highest towhee densities typically undergo low-severity surface fires at an interval of about 4 to 10 years [14,30]. Fires in the southeastern United States frequently occur in summer due to an increase in the occurrence of lightning strikes [73].

Due to their preference for early successional stands (see Preferred Habitat/Cover), eastern towhees are likely to occur in early to intermediate successional stages after stand-replacing fires.

In herbaceous habitats eastern towhees are most likely to occur in areas where fire exclusion [106] has resulted in establishment of some woody shrubs.

Fire regimes: The following table provides fire return intervals for plant communities and ecosystems where eastern towhee is likely to occur. Find fire regime information for the plant communities in which this species may occur by entering the species name in the FEIS home page under "Find Fire Regimes".

Community or Ecosystem Dominant Species Fire Return Interval Range (years)
maple-beech-birch Acer-Fagus-Betula spp. >1,000
silver maple-American elm Acer saccharinum-Ulmus americana <5 to 200
sugar maple Acer saccharum >1,000
sugar maple-basswood Acer saccharum-Tilia americana >1,000 [96]
bluestem prairie Andropogon gerardii var. gerardii-Schizachyrium scoparium <10 [54,71]
bluestem-Sacahuista prairie Andropogon littoralis-Spartina spartinae <10 [71]
mangrove Avicennia nitida-Rhizophora mangle 35-200 [68]
sugarberry-America elm-green ash Celtis laevigata-Ulmus americana-Fraxinus pennsylvanica <35 to 200
beech-sugar maple Fagus spp.-Acer saccharum >1,000 [96]
cedar glades Juniperus virginiana 3-22 [43,71]
tamarack Larix laricina 35-200 [71]
yellow-poplar Liriodendron tulipifera <35 [96]
Everglades Mariscus jamaicensis <10 [68]
Great Lakes spruce-fir Picea-Abies spp. 35 to >200
northeastern spruce-fir Picea-Abies spp. 35-200 [27]
southeastern spruce-fir Picea-Abies spp. 35 to >200 [96]
black spruce Picea mariana 35-200
conifer bog* Picea mariana-Larix laricina 35-200
red spruce* Picea rubens 35-200 [27]
pine-cypress forest Pinus-Cupressus spp. <35 to 200 [6]
shortleaf pine Pinus echinata 2-15
shortleaf pine-oak Pinus echinata-Quercus spp. <10
slash pine Pinus elliottii 3-8
slash pine-hardwood Pinus elliottii-variable <35
sand pine Pinus elliottii var. elliottii 25-45 [96]
South Florida slash pine Pinus elliottii var. densa 1-5
longleaf-slash pine Pinus palustris-P. elliottii 1-4 [68,96]
longleaf pine-scrub oak Pinus palustris-Quercus spp. 6-10 [96]
red-white-jack pine* Pinus resinosa-P. strobus-P. banksiana 10-300 [27,45]
pitch pine Pinus rigida 6-25 [16,46]
pocosin Pinus serotina 3-8
pond pine Pinus serotina 3-8
eastern white pine Pinus strobus 35-200
eastern white pine-eastern hemlock Pinus strobus-Tsuga canadensis 35-200
eastern white pine-northern red oak-red maple Pinus strobus-Quercus rubra-Acer rubrum 35-200
loblolly pine Pinus taeda 3-8
loblolly-shortleaf pine Pinus taeda-P. echinata 10 to <35
Virginia pine Pinus virginiana 10 to <35
Virginia pine-oak Pinus virginiana-Quercus spp. 10 to <35
sycamore-sweetgum-American elm Platanus occidentalis-Liquidambar styraciflua-Ulmus americana <35 to 200 [96]
eastern cottonwood Populus deltoides <35 to 200 [71]
aspen-birch Populus tremuloides-Betula papyrifera 35-200 [27,96]
black cherry-sugar maple Prunus serotina-Acer saccharum >1,000
oak-hickory Quercus-Carya spp. <35
northeastern oak-pine Quercus-Pinus spp. 10 to <35 [96]
oak-gum-cypress Quercus-Nyssa-spp.-Taxodium distichum 35 to >200 [68]
southeastern oak-pine Quercus-Pinus spp. <10
white oak-black oak-northern red oak Quercus alba-Q. velutina-Q. rubra <35
northern pin oak Quercus ellipsoidalis <35
bear oak Quercus ilicifolia <35
bur oak Quercus macrocarpa <10 [96]
oak savanna Quercus macrocarpa/Andropogon gerardii-Schizachyrium scoparium 2-14 [71,96]
chestnut oak Quercus prinus 3-8
northern red oak Quercus rubra 10 to <35
post oak-blackjack oak Quercus stellata-Q. marilandica <10
black oak Quercus velutina <35 [96]
cabbage palmetto-slash pine Sabal palmetto-Pinus elliottii <10 [68,96]
blackland prairie Schizachyrium scoparium-Nassella leucotricha <10 [96]
southern cordgrass prairie Spartina alterniflora 1-3 [71]
baldcypress Taxodium distichum var. distichum 100 to >300
pondcypress Taxodium distichum var. nutans <35 [68]
eastern hemlock-yellow birch Tsuga canadensis-Betula alleghaniensis >200 [96]
elm-ash-cottonwood Ulmus-Fraxinus-Populus spp. <35 to 200 [27,96]
*fire return interval varies widely; trends in variation are noted in the species review

When managing for eastern towhees, fire interval should be carefully considered before implementing a burning plan [14,42]. Surface burns in open woodlands, grasslands, and wetlands at intervals that would eventually reduce low woody cover would likely result in eastern towhee declines. Eastern towhees have been observed to peak 4 years after fire in Florida on an old-field loblolly-shortleaf pineland, in slash pine flatwoods with saw palmetto (Serenoa repens), myrtle oak, and sand live oak in the understory, and in a scrub community comprised of scattered slash pine and cabbage palm [14,30]. The most favorable fire interval for eastern towhee depends on the habitat and other management objectives, but fire intervals of ≤3 yrs will likely result in eastern towhee absence or smaller population sizes. Fire exclusion in these areas is also likely to cause eastern towhee declines. As the canopy closes the low shrubby species that provide cover and food decline. Four years after fire in a Florida old-field loblolly-shortleaf pineland, eastern towhee detections gradually declined. Eleven years after fire eastern towhee detections were less than detections 1 year after fire [30].

Less is known about eastern towhees response to severe fires. In dense-canopied forests, stand-replacing fires may provide patches of early successional vegetation necessary for eastern towhee occurrence. Although there are no data on eastern towhee occurrence in severely burned forest, eastern towhees have increased on sites subjected to other canopy-opening disturbances that may have less effect on the understory, such as wind throw or logging [28,39,91]. On a sand pine scrub site in Florida that was burned in a stand-replacing fire and salvage logged 5 to 7 years earlier, eastern towhees were more abundant than on a mature, control site. The extent to which eastern towhees were responding to the effects salvage logging is unknown [38].

Although it is likely that reasonable inferences regarding eastern towhees response can be made from the impact fire has on understory vegetation, other factors such as a fire's affect on food availability and abundance of predators and competitors should also be considered when using fire as a management tool for eastern towhee [78].

Pipilo erythrophthalmus: REFERENCES

1. American Ornithologists' Union. 1957. Checklist of North American birds. 5th ed. Baltimore, MD: The Lord Baltimore Press, Inc. 691 p. [21235]
2. American Ornithologists' Union. 1995. Fortieth supplement to the American Ornithologists' Union Check-List of North American Birds. The Auk. 112(3): 819-830. [60876]
3. American Ornithologists' Union. 2005. The A.O.U. check-list of North American birds, 7th edition, [Online]. American Ornithologists' Union (Producer). Available: [50863]
4. Aquilani, Steven M.; LeBlanc, David C.; Morrell, Thomas E. 2000. Effects of prescribed surface fires on ground- and shrub-nesting Neotropical migratory birds in a mature Indiana oak forest, USA. Natural Areas Journal. 20(4): 317-324. [41662]
5. Aquilani, Steven M.; Morrell, Thomas E.; LeBlanc, David C. 2003. Breeding bird communities in burned and unburned sites in a mature Indiana oak forest. Proceedings of the Indiana Academy of Science. 112(2): 186-191. [60825]
6. Arno, Stephen F. 2000. Fire in western forest ecosystems. In: Brown, James K.; Smith, Jane Kapler, eds. Wildland fire in ecosystems: Effects of fire on flora. Gen. Tech. Rep. RMRS-GTR-42-vol. 2. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 97-120. [36984]
7. Bay, Michael Daymon. 1994. Effects of area and vegetation on breeding bird communities in early successional oldfields. Fayetteville, AR: University of Arkansas. 128 p. Dissertation. [60700]
8. Bell, Jennifer L.; Whitmore, Robert C. 1997. Eastern towhee numbers increase following defoliation by gypsy moths. The Auk. 114(4): 708-716. [60718]
9. Bell, Jennifer L.; Whitmore, Robert C. 2000. Bird nesting ecology in a forest defoliated by gypsy moths. The Wilson Bulletin. 112(4): 524-531. [60725]
10. Bernard, Stephen R.; Brown, Kenneth F. 1977. Distribution of mammals, reptiles, and amphibians by BLM physiographic regions and A.W. Kuchler's associations for the eleven western states. Tech. Note 301. Denver, CO: U.S. Department of the Interior, Bureau of Land Management. 169 p. [434]
11. Blem, Charles R.; Vandenberg, Kristine M. 1996. Winter abundance of some finches in Virginia: 1965-1993. The Raven. 67(2): 90-95. [60727]
12. Bontrager, David R.; Erickson, Richard A.; Hamilton, Robert A. 1995. Impacts of the October 1993 Laguna Canyon Fire on California gnatcatchers and cactus wrens. In: Keeley, Jon F.; Scott, Tom, eds. Brushfires in California: ecology and resource management: Proceedings; 1994 May 6-7; Irvine, CA. Fairfield, WA: International Association of Wildland Fire: 69-76. [43321]
13. Breininger, David R. 1992. Birds of swale marshes on John F. Kennedy Space Center. Florida Field Naturalist. 20(2): 36-41. [21095]
14. Breininger, David R.; Smith, Rebecca B. 1992. Relationships between fire and bird density in coastal scrub and slash pine flatwoods in Florida. The American Midland Naturalist. 127(2): 233-240. [17993]
15. Brush, Timothy; Stiles, Edmund W. 1990. Habitat use by breeding birds in the New Jersey Pine Barrens. Bulletin of the New Jersey Academy of Science. 35(2): 13-16. [60728]
16. Buchholz, Kenneth; Good, Ralph E. 1982. Density, age structure, biomass and net annual aboveground productivity of dwarfed Pinus rigida Moll. from the New Jersey Pine Barren Plains. Bulletin of the Torrey Botanical Club. 109(1): 24-34. [8639]
17. Bull, John. 1964. Birds of the New York area. New York: Harper & Row. 540 p. [60729]
18. Butcher, Gregory S.; Fuller, Mark R.; McAllister, Lynne S.; Geissler, Paul H. 1990. An evaluation of the Christmas Bird Count for monitoring population trends of selected species. Wildlife Society Bulletin. 18: 129-134. [60730]
19. Chandler, Craig; Cheney, Phillip; Thomas, Philip; [and others]. 1983. Fire in forestry: Vol. I. Forest fire behavior and effects. New York: John Wiley & Sons. 450 p. [12241]
20. Crawford, H. S.; Hooper, R. G.; Titterington, R. W. 1981. Songbird population response to silvicultural practices in central Appalachian hardwoods. Journal of Wildlife Management. 45(3): 680-692. [19282]
21. Davis, Mark A.; Peterson, David W.; Reich, Peter B.; [and others]. 2000. Restoring savanna using fire: impact on the breeding bird community. Restoration Ecology. 8(1): 30-40. [35984]
22. DeGraaf, Richard M.; Yamasaki, Mariko. 2003. Options for managing early-successional forest and shrubland bird habitats in the northeastern United States. Forest Ecology and Management. 185(1-2): 179-191. [48395]
23. Dickson, James G. 2002. Fire and bird communities in the South. In: Ford, W. Mark; Russell, Kevin R.; Moorman, Christopher E., eds. The role of fire in nongame wildlife management and community restoration: traditional uses and new directions: Proceedings of a special workshop; 2000 December 15; Nashville, TN. Gen. Tech. Rep. NE-288. Newtown Square, PA: U.S. Department of Agriculture, Forest Service, Northeastern Research Station: 52-57. [41557]
24. Dickson, James G.; Noble, Robert E. 1978. Vertical distribution of birds in a Louisiana bottomland hardwood forest. The Wilson Bulletin. 90(1): 19-30. [60732]
25. Dickson, James G.; Thompson, Frank R., III; Conner, Richard N.; Franzreb, Kathleen E. 1993. Effects of silviculture on neotropical migratory birds in central and southeastern oak pine forests. In: Finch, Deborah M.; Stangel, Peter W., eds. Status and management of neotropical migratory birds: Proceedings; 1993 September 21-25; Estes Park, CO. Gen. Tech. Rep. RM-229. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 374-385. [24663]
26. Diefenbach, Duane R. 1996. Abundance and nest success of songbirds in simple and complex edge habitats. Final Report Project 06510. Harrisburg, PA: Pennsylvania Game Commission. 7 p. [60733]
27. Duchesne, Luc C.; Hawkes, Brad C. 2000. Fire in northern ecosystems. In: Brown, James K.; Smith, Jane Kapler, eds. Wildland fire in ecosystems: Effects of fire on flora. Gen. Tech. Rep. RMRS-GTR-42-vol. 2. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 35-51. [36982]
28. Duguay, Jeffrey P.; Wood, Petra Bohall; Nichols, Jeffrey V. 2001. Songbird abundance and avian nest survival rates in forests fragmented by different silvicultural treatments. Conservation Biology. 15(5): 1405-1415. [60734]
29. Emlen, John T. 1970. Habitat selection by birds following a forest fire. Ecology. 51(2): 343-345. [60827]
30. 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. The Wilson Bulletin. 96(3): 437-450. [60735]
31. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905]
32. Finch, Deborah M.; Ganey, Joseph L.; Yong, Wang; [and others]. 1997. Effects and interactions of fire, logging, and grazing. In: Block, William M.; Finch, Deborah M., tech. eds. Songbird ecology in southwestern ponderosa pine forests: a literature review. Gen. Tech. Rep. RM-GTR-292. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 103-136. [27990]
33. Fitzgerald, Susan M.; Tanner, George W. 1992. Avian community response to fire and mechanical shrub control in south Florida. Journal of Range Management. 45(4): 396-400. [18808]
34. Foss, Carol R. 1994. Atlas of breeding birds in New Hampshire. Dover, NH: Audubon Society of New Hampshire. 464 p. [60882]
35. Galli, Anne E.; Leck, Charles F.; Forman, Richard T. T. 1976. Avian distribution patterns in forest islands of different sizes in central New Jersey. The Auk. 93: 356-364. [60736]
36. Garrison, George A.; Bjugstad, Ardell J.; Duncan, Don A.; Lewis, Mont E.; Smith, Dixie R. 1977. Vegetation and environmental features of forest and range ecosystems. Agric. Handb. 475. Washington, DC: U.S. Department of Agriculture, Forest Service. 68 p. [998]
37. Gates, J. Edward; Dixon, Kenneth R. 1981. Right-of-way utilization by forest- and corridor-breeding bird populations. In: Arner, Dale, ed. Environmental concerns in right-of-way management: Proceeding of 2nd symposium; 1979 October 16-18; Ann Arbor, MI. Special Study Project WS-78-141: 66-1 to 66-7. [60883]
38. Greenberg, Cathryn H.; Harris, Lawrence D.; Neary, Daniel G. 1995. A comparison of bird communities in burned and salvage-logged, clearcut, and forested Florida sand pine scrub. The Wilson Bulletin. 107(1): 40-54. [26024]
39. Greenberg, Cathryn H.; Lanham, J. Drew. 2001. Breeding bird assemblages of hurricane-created gaps in and adjacent closed canopy forest in the southern Appalachians. Forest Ecology and Management. 154(1-2): 251-260. [60864]
40. Greenlaw, Jon S. 1976. Use of bilateral scratching behavior by Emberizines and Icterids. The Condor. 78(1): 94-97. [60874]
41. Greenlaw, Jon S. 1978. The relation of breeding schedule and clutch size to food supply in the rufous- sided towhee. The Condor. 80(1): 24-33. [60737]
42. Greenlaw, Jon S. 1996. Easter towhee--Pipilo erythrophthalmus. In: Poole, A.; Gill, F., eds. The birds of North America. No. 262: 1-32. [60750]
43. Guyette, Richard; McGinnes, E. A., Jr. 1982. Fire history of an Ozark glade in Missouri. Transactions, Missouri Academy of Science. 16: 85-93. [5170]
44. Hagan, John M., III. 1993. Decline of the rufous-sided towhee in the eastern United States. The Auk. 110(4): 863-874. [60751]
45. Heinselman, Miron L. 1970. The natural role of fire in northern conifer forests. In: The role of fire in the Intermountain West: Symposium proceedings; 1970 October 27-29; Missoula, MT. Missoula, MT: Intermountain Fire Research Council: 30-41. In cooperation with: University of Montana, School of Forestry. [15735]
46. Hendrickson, William H. 1972. Perspective on fire and ecosystems in the United States. In: Fire in the environment: Symposium proceedings; 1972 May 1-5; Denver, CO. FS-276. [Washington, DC]: U.S. Department of Agriculture, Forest Service: 29-33. In cooperation with: Fire Services of Canada, Mexico, and the United States; Members of the Fire Management Study Group; North American Forestry Commission; FAO. [17276]
47. Hockman, J. Gregory; Chapman, Joseph A. 1983. Comparative feeding habits of red foxes (Vulpes vulpes) and gray foxes (Urocyon cinereoargenteus) in Maryland. The American Midland Naturalist. 110(2): 276-285. [27679]
48. Huff, Mark H.; Smith, Jane Kapler. 2000. Fire effects on animal communities. In: Smith, Jane Kapler, ed. Wildland fire in ecosystems: Effects of fire on fauna. Gen. Tech. Rep. RMRS-GTR-42-vol. 1. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 35-42. [44446]
49. Keller, J. K.; Richmond, M. E.; Smith, C. R. 2003. An explanation of patterns of breeding bird species richness and density following clearcutting in northeastern USA forests. Forest Ecology and Management. 174: 541-564. [43602]
50. King, T. Gregory; Howell, Mark A.; Chapman, Brian R.; [and others]. 1998. Comparisons of wintering bird communities in mature pine stands managed by prescribed burning. The Wilson Bulletin. 110(4): 570-574. [36037]
51. Klimkiewicz, M. Kathleen; Futcher, Anthony G. 1987. Longevity records of North American birds: Coerebinae through Estrildidae. Journal of Field Ornithology. 58(3): 318-333. [60752]
52. Krementz, David G.; Powell, Larkin A. 2000. Breeding season demography and movements of eastern towhees at the Savannah River Site, South Carolina. The Wilson Bulletin. 112(2): 243-248. [60754]
53. Kroodsma, Roger. 1984. Effect of edge on breeding forest bird species. The Wilson Bulletin. 93(3): 426-436. [60755]
54. Kucera, Clair L. 1981. Grasslands and fire. In: Mooney, H. A.; Bonnicksen, T. M.; Christensen, N. L.; Lotan, J. E.; Reiners, W. A., technical coordinators. Fire regimes and ecosystem properties: Proceedings of the conference; 1978 December 11-15; Honolulu, HI. Gen. Tech. Rep. WO-26. Washington, DC: U.S. Department of Agriculture, Forest Service: 90-111. [4389]
55. Kuchler, A. W. 1964. United States [Potential natural vegetation of the conterminous United States]. Special Publication No. 36. New York: American Geographical Society. 1:3,168,000; colored. [3455]
56. Lanham, Joseph Drew. 1997. Attributes of avian communities in early-successional, clearcut habitats in the mountains and upper piedmont of South Carolina. Clemson, SC: Clemson University. 126 p. Dissertation. [60756]
57. Leck, Charles F.; Murray, Bertram G., Jr.; Swinebroad, Jeff. 1988. Long-term changes in the breeding bird populations of a New Jersey forest. Biological Conservation. 46: 145-157. [60875]
58. Lewis, Amy R.; Yahner, Richard H. 1999. Sex-specific habitat use by eastern towhees in a managed forested landscape. Journal of the Pennsylvania Academy of Science. 72(2): 77-79. [60757]
59. Lohr, Steven M.; Gauthreaux, Sidney A.; Kilgo, John C. 2002. Importance of coarse woody debris to avian communities in loblolly pine forests. Conservation Biology. 16(3): 767-777. [60758]
60. Lyon, L. Jack; Hooper, Robert G.; Telfer, Edmund S.; Schreiner, David Scott. 2000. Fire effects on wildlife foods. In: Smith, Jane Kapler, ed. Wildland fire in ecosystems: Effects of fire on fauna. Gen. Tech. Rep. RMRS-GTR-42-vol. 1. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 51-58. [44448]
61. Lyon, L. Jack; Huff, Mark H.; Telfer, Edmund S.; Schreiner, David Scott; Smith, Jane Kapler. 2000. Fire effects on animal populations. In: Smith, Jane Kapler, ed. Wildland fire in ecosystems: Effects of fire on fauna. Gen. Tech. Rep. RMRS-GTR-42-vol. 1. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 25-34. [44436]
62. Lyon, L. Jack; Telfer, Edmund S.; Schreiner, David Scott. 2000. Direct effects of fire and animal responses. In: Smith, Jane Kapler, ed. Wildland fire in ecosystems: Effects of fire on fauna. Gen. Tech. Rep. RMRS-GTR-42-vol. 1. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 17-23. [44435]
63. Martin, Alexander C.; Zim, Herbert S.; Nelson, Arnold L. 1951. American wildlife and plants. New York: McGraw-Hill Bood Company, Inc. 500 p. [53531]
64. McElveen, J. D. 1977. The edge effect on a forest bird community in north Florida. Proceedings, Annual Conference of Southeastern Associations of Fish and Wildlife Agencies. 31: 212-215. [60759]
65. Miller, Darren A.; Leopold, Bruce D.; Conner, L. Mike. 1999. Effects of pine and hardwood basal areas after uneven-aged silvicultural treatments on wildlife habitat. Southern Journal of Applied Forestry. 23(3): 151-157. [38474]
66. Morimoto, David C.; Wasserman, Fred E. 1991. Intersexual and interspecific differences in the foraging behavior of rufous-sided towhees, common yellowthroats and prairie warblers in the pine barrens of southeastern Massachusetts. Journal of Field Ornithology. 62(4): 436-449. [60760]
67. Mumford, Russell E.; Keller, Charles E. 1984. The birds of Indiana. Bloomington, IN: Indiana University Press. 376 p. [60761]
68. Myers, Ronald L. 2000. Fire in tropical and subtropical ecosystems. In: Brown, James K.; Smith, Jane Kapler, eds. Wildland fire in ecosystems: Effects of fire on flora. Gen. Tech. Rep. RMRS-GTR-42-vol. 2. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 161-173. [36985]
69. National Geographic Society. 1999. Field guide to the birds of North America. 3rd ed. Washington, DC: The National Geographic Society. 480 p. [60563]
70. Ogden, John C. 1974. The short-tailed hawk in Florida. I. Migration, habitat, hunting techniques, and food habits. The Auk. 91: 95-110. [60762]
71. Paysen, Timothy E.; Ansley, R. James; Brown, James K.; [and others]. 2000. Fire in western shrubland, woodland, and grassland ecosystems. In: Brown, James K.; Smith, Jane Kapler, eds. Wildland fire in ecosystems: Effects of fire on flora. Gen. Tech. Rep. RMRS-GTR-42-volume 2. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 121-159. [36978]
72. Peterjohn, Bruce J.; Sauer, John R.; Orsillo, Sandra. 1995. Breeding bird survey: population trends 1966-92. In: LaRoe, Edward T.; Farris, Gaye S.; Puckett, Catherine E.; [and others], eds. Our living resources: a report to the nation on the distribution, abundance, and health of U.S. plants, animals, and ecosystems. Washington, DC: U.S. Department of the Interior, National Biological Survey: 17-21. [27175]
73. Platt, William J. 1999. Southeastern pine savannas. In: Anderson, Roger C.; Fralish, James S.; Baskin, Jerry M., eds. Savannas, barrens, and rock outcrop plant communities of North America. New York: Cambridge University Press: 23-51. [52459]
74. Prather, John W.; Cruz, Alexander. 2002. Distribution, abundance, and breeding biology of potential cowbird hosts on Sanibel Island, Florida. Florida Field Naturalist. 30(2): 21-76. [60768]
75. Provencher, Louis; Gobris, Nancy M.; Brennan, Leonard A.; Gordon, Doria R.; Hardesty, Jeffrey L. 2002. Breeding bird response to midstory hardwood reduction in Florida sandhill longleaf pine forests. Journal of Wildlife Management. 66(3): 641-661. [42243]
76. Quinn, Ronald D. 1994. Animals, fire and vertebrate herbivory in Californian chaparral and other Mediterranean-type ecosystems. In: Moreno, Jose M.; Oechel, Walter C., eds. The role of fire in Mediterranean-type ecosystems. New York: Springer Verlag: 46-78. [26804]
77. Robbins, Louise E.; Myers, Ronald L. 1992. Seasonal effects of prescribed burning in Florida: a review. Misc. Publ. No. 8. Tallahassee, FL: Tall Timbers Research, Inc. 96 p. [21094]
78. Rotenberry, John T.; Cooper, Robert J.; Wunderle, Joseph M.; Smith, Kimberly G. 1995. When and how are populations limited? The roles of insect outbreaks, fire, and other natural perturbations. In: Martin, Thomas E.; Finch, Deborah M., eds. Ecology and management of neotropical migratory birds: a synthesis and review of critical issues. New York: Oxford University Press: 55-84. [27957]
79. Savidge, Irvin R.; Davis, David E. 1974. Survival of some common passerines in a Pennsylvania woodlot. Bird Banding. 45: 152-155. [60770]
80. Shiflet, Thomas N., ed. 1994. Rangeland cover types of the United States. Denver, CO: Society for Range Management. 152 p. [23362]
81. Shugart, Herman Henry, Jr.; James, Douglas. 1973. Ecological succession of breeding bird populations in northwestern Arkansas. Auk. 90: 62-77. [25059]
82. Sibley, Charles G.; West, David A. 1959. Hybridization in the rufous-sided towhees of the Great Plains. The Auk. 76: 326-338. [60772]
83. Sidelinger, John E. 1977. Composition and structure of vegetation and wildlife utilization of a scrub oak forest following a prescribed burn. University Park, PA: Pennsylvania State University. 93 p. Thesis. [60897]
84. Smith, Kimberly G.; Mlodinow, Michael; Self, Janet S.; Haggerty, Thomas M.; Hocut, Tamara R. 2004. Birds of upland oak forests in the Arkansas Ozarks: present community structure and potential impacts of burning, borers, and forestry practices. In: Spetich, Marin A., ed. Upland oak ecology symposium: history, current conditions, and sustainability; 2002 October 7-10; Fayetteville, AR. Gen. Tech. Rep. SRS-73. Asheville, NC: U.S. Department of Agriculture, Forest Service, Southern Research Station: 243-252. [60870]
85. Stauffer, Dean F.; Best, Louis B. 1980. Habitat selection by birds of riparian communities: evaluation effects of habitat alterations. Journal of Wildlife Management. 44(1): 1-15. [8118]
86. Stevenson, Henry M.; Anderson, Bruce H. 1994. The birdlife of Florida. Gainesville, FL: University of Florida Press. 892 p. [60776]
87. Storer, Robert W. 1966. Sexual dimorphism and food habits in three North American accipiters. The Auk. 83: 423-436. [60778]
88. Stupka, Arthur. 1963. Notes on the birds of Great Smoky Mountains National Park. Knoxville, TN: The University of Tennessee Press. 242 p. [60779]
89. Suthers, Hannah B.; Bickal, Jean M.; Rodewald, Paul G. 2000. Use of successional habitat and fruit resources by songbirds during autumn migration in central New Jersey. The Wilson Bulletin. 112(2): 249-260. [41724]
90. Thompson, Frank R., III; Dessecker, Daniel R. 1997. Management of early-successional communities in central hardwood forests. Gen. Tech. Rep. NC-195. St. Paul, MN: U.S. Department of Agriculture, Forest Service, North Central Forest Experiment Station. 33 p. [28318]
91. Thompson, Frank R., III; Fritzell, Erik K. 1980. Bird densities and diversity in clearcut and mature oak-hickory forest. SE Res. Pap. NC-293. St. Paul, MN: U.S. Department of Agriculture, Forest Service, Southeastern Forest Experimental Station. 7 p. [27423]
92. Tucker, James W.; Hill, Geoffrey E.; Holler, Nicholas R. 2003. Longleaf pine restoration: implications for landscape-level effects on bird communities in the lower Gulf Coastal Plain. Southern Journal of Applied Forestry. 27(2): 107-121. [44563]
93. Twedt, Daniel J.; Wilson, R. Randy; Henne-Kerr, Jackie L.; Hamilton, Robert B. 2001. Nest survival of forest birds in the Mississippi Alluvial Valley. Journal of Wildlife Management. 65(3): 450-460. [60780]
94. Urner, Charles A. 1926. Effect of fires on Pine Barren bird life. The Auk. 43: 558-559. [11410]
95. Vogl, Richard J. 1973. Effects of fire on the plants and animals of a Florida wetland. The American Midland Naturalist. 89(2): 334-347. [26118]
96. Wade, Dale D.; Brock, Brent L.; Brose, Patrick H.; [and others]. 2000. Fire in eastern ecosystems. In: Brown, James K.; Smith, Jane Kapler, eds. Wildland fire in ecosystems: Effects of fire on flora. Gen. Tech. Rep. RMRS-GTR-42-vol. 2. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 53-96. [36983]
97. Wasserman, Fred E. 1983. Territories of rufous-sided towhees contain more than food resources. The Wilson Bulletin. 95(4): 664-667. [60873]
98. Whalen, David M.; Watts, Bryan D. 2000. Interspecific variation in extraction of buried seeds within an assemblage of sparrows. Oikos. 88(3): 574-584. [60781]
99. White, Donald H.; Chapman, Brian R.; Brunjes, John H., IV; Raftovich, Robert V., Jr. 1999. Abundance and reproduction of songbirds in burned and unburned pine forests of the Georgia Piedmont. Journal of Field Ornithology. 70(3): 414-424. [60826]
100. Whitehead, Maria A.; Schweitzer, Sara H.; Post, William. 2002. Cowbird/host interaction in a southeastern old-field: a recent contact area? Journal of Field Ornithology. 73(4): 379-386. [60782]
101. Yahner, Richard H. 1986. Structure, seasonal dynamics, and habitat relationships of avian communities in small even-aged forest stands. The Wilson Bulletin. 98(1): 61-82. [60783]
102. Yahner, Richard H. 1987. Use of even-aged stands by winter and spring bird communities. Wilson Bulletin. 99(2): 218-232. [24959]
103. Yahner, Richard H. 1991. Avian nesting ecology in small even-aged aspen stands. Journal of Wildlife Management. 55(1): 155-159. [13835]
104. Yahner, Richard H. 2000. Long-term effects of even-aged management on bird communities in central Pennsylvania. Wildlife Society Bulletin. 28(4): 1102-1110. [60784]
105. Yahner, Richard H.; Ross, Bradley D.; Yahner, Richard T.; Hutnik, Russell J.; Liscinsky, Stephen A. 2004. Long-term effects of rights-of-way maintenance via the wire-border zone method on bird nesting ecology. Journal of Arboriculture. 30(5): 288-293. [60785]
106. Zimmerman, John L. 1992. Density-dependent factors affecting the avian diversity of the tallgrass prairie community. The Wilson Bulletin. 104(1): 85-94. [60823]

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